Planning Comm PKT 02-14-2007
February 14,2007
7:00 p.m.
City of Federal Way
PLANNING COMMISSION
City Hall
Council Chambers
AGENDA
1. CALL TO ORDER
2. ROLL CALL
3. APPROVAL OF MINUTES
4. AUDIENCE COMMENT
5. ADMINISTRATIVE REPORT
6. COMMISSION BUSINESS
. STUDY SESSION
Proposed Amendments to the City's Shoreline Master Program
7. ADDITIONAL BUSINESS
8. AUDIENCE COMMENT
9. ADJOURN
Commissioners
Hope Elder, Chair
Dave Osaki
Merle Pfeifer
Wayne Carlson
Kevin King (Alternate #2)
Dini Duclos, Vice-Chair
William Drake
Lawson Bronson
Richard Agnew (Alternate #1)
Caleb Allen (Alternate #3)
City Staff
Kathy McClung, CDS Director
Margaret Clark, Senior Planner
E. Tina Piety, Administrative Assistant
253-835-2601
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K:\Planning Conunissionl2007\Agenda 02-14-07.doc
CITY OF FEDERAL WAY
PLANNING COMMISSION
December 20,2006
7:00 p.m.
City Hall
Council Chambers
MEETING MINUTES
Commissioners present: Hope Elder, Dave Osaki, Dini Duclos, Merle Pfeifer, Lawson Bronson, and Wayne
Carlson. Commissioners absent: Bill Drake (unexcused). Alternate Commissioners present: Kevin King and Caleb
Allen. Alternate Commissioners absent: Richard Agnew (excused). Staff present: Senior Planner Lori Michaelson,
Assistant City Attorney Amy Jo Pearsall, and Administrative Assistant E. Tina Piety.
Chairperson Elder called the meeting to order at 7:00 p.m.
ApPROV AL OF MINUTES
Commissioner Duclos moved and it was seconded to adopt the November 8, 2006, minutes with the change that
Commissioner Osaki was not present at the November 8, 2006, meeting. The motion was carried.
AUDIENCE COMMENT
None
ADMINISTRATIVE REpORT
None
COMMISSION BUSINESS
STUDY SESSION - Proposed Amendments to Business Park (BP) and Community Business (BC) Zoning
Districts
Ms. Michaelson delivered the staff report. She stated that research still needs to be done. Staff hopes to have the
public hearing on this project in February. The proposal would rename the BP zone to Commercial Enterprise
(CE). The new CE zone would also incorporate BC zoned property located south of South 339th Street (if
extended); except the property located south of South 336th Street and west of SR-99 and the property located at
. the northwest comer of SW Campus Drive and 151 A venue South (Kitts Comer and Winco property).
Commissioner Pfeifer expressed concern over auto body repair shops. Auto body repair shops are different from
automotive mechanical repair. Will they be allowed? Ms. Michaelson responded that automotive mechanical repair
is currently allowed as a principal use in the BC zone, but body repair and painting must be accessory. Staff is
proposing both mechanical and body repair be allowed as a principal use in both the BC and new CE zones.
It is proposed to eliminate senior housing from the CE zone, or require it to be part of a mixed-use development.
Currently, senior housing is allowed in the BP zone (which will become the CE zone). Subject to further research,
the only senior housing that staff is aware of that would be affected by this change is Mitchell Place. Commissioner
Duclos expressed concern that making Mitchell Place nonconforming by eliminating it as a use in the CE zone
could affect the funding for Mitchell Place. She asked what other useslbusinesses would be made nonconforming
by this change. Ms. Michaelson replied that information would be included in the public hearing staff report, but
use nonconformances are expected to be minimal.
Ms. Michaelson stated that staff is still researching the numbers for the proposed height increase for hotels/motels
and mixed use housing. Other text amendments they are researching include (among other things) whether
multifamily density caps are needed and decreasing the amount of open space required for multifamily and
including private space (i.e. decks) as part ofthe open space.
K\Planning Conunission12006\Meeting Summary 12-20-06.doc
Planning Conunission Minutes
Page 2
December 20, 2006
Commissioner Duclos asked what the zoning will be for the Kitts Comer property. Ms. Michaelson responded that
the zoning for this property is governed by a development agreement and the proposed amendments do not affect
this property.
Commissioner Duclos stated that the city should not make any current uses nonconforming because it restricts what
the owner can do with the use. Commissioner Hope agreed with her. The Commission discussed rezoning the
Mitchell Place property and Commissioner Bronson suggested that the property be rezoned as part of these
amendments. Ms. Michaelson and Ms. Pearsall explained that rezoning Mitchell Place would be a site-specific
rezone (which would be part ofthe comprehensive plan update) and a separate request would have to be made to
the city and that request would be part of the next comprehensive plan update. The process could take a year or
more. Commissioners expressed dismay that the city is contemplating a change that would make Mitchell Place
nonconforming and that the process to bring it into conformance could take a year or more.
Commissioner Pfeifer stated that while the proposed amendments may by good for a majority of property owners in
this area, it is not true for all of them. Who came up with this geographic line? Why is the Kitts Comer property not
included? Ms. Michaelson replied that Kitts Comer, Christian Faith Center, and a few smaller properties were not
included because their zoning is governed by concomitant agreements, and/or the current use is not incompatible
with industrial uses. Originally, the City Council considered one zoning district for BP and Be. Staff suggested it
would be better to have two zoning districts, with some changes, and the Council agreed with this approach.
Commissioner Carlson stated that the nonconforming issue aside, he likes the proposed separation of heaver
industrial uses. For light industry/manufacturing, he would like more of an idea of how they will work. He images
they would be manufacturing to sell on site (i.e. making jewelry in the back room to sell in the shop), but would it
include manufacturing of items to be sold elsewhere? The CE zone seems more appropriate for such
manufacturing, even if it is a small business. Ms. Michaelson said the definition will be crafted to ensure very
limited manufacturing and a principal retail use. .
Commissioner Osaki asked for a map of the entire city showing the entire BC zoning. If senior housing is allowed
in the BP zone, why not the CE? He likes the amendment, but is concerned with traffic in regards to industrial
uses. He wants a traffic analysis preformed. Ms. Michaelson replied that the SEP A process will address traffic.
Commissioner Bronson commented that the proposed amendments make the city less attractive for industrial uses.
There has been a downturn the last 20 years for manufacturing (and thereby of business looking for property for
industrial uses), but that ,does not mean the downturn will continue. He has seen some resurgence of heavy industry
and is concerned that Federal Way could lose potential businesses because of the proposed amendments. Ms.
Michaelson noted that heavy industry would continue to be allowed in the CE zone and there will be more total
land available in the proposed CE zone than currently available for such uses in the exiting BC zone.
ADDITIONAL BUSINESS
None
AUDIENCE COMMENT
None
ADJOURN
The meeting was adjourned at 8:01 p.m.
K:\Planning Conunission12006\Meeting Summary 12-20-06.doc
CITY OF FEDERAL WAY
PLANNING COMMISSION MEMO
DATE: February 14,2007
TO: Planning Commission
FROM: Isaac Conlen, Acting Senior Planne~L_
-
SUBJECT: Shoreline Master Program Update
Beginning in early 2006 staff, with the help ofthe consulting firm ESA-Adolfson, has been
working to update the City's Shoreline Master Program (SMP). As required by the Department
of Ecology we have prepared the following draft work items:
Public Participation Plan
Shoreline Inventory, Characterization and Map Folio
Environmental Designation Map
Amended Goals and Policies
Restoration Plan
Amended Shoreline Regulations
Cumulative Impact Analysis
All of the above items are included in your packet. Please see the attached PowerPoint slides for
an overview. It's a lot of information. If you'd like, please focus your review on the
Environment Designations Map, Draft Goals and Policies, Shoreline Regulations and Restoration
Plan. These are the items we will focus our presentation on.
Including the February 14,2007 meeting, we have a total of three Planning Commission
meetings scheduled for this topic. We have tentatively scheduled the public hearing for March 7,
2007 (although this can be rescheduled to the following meeting if necessary). An additional
meeting is scheduled for March 28, 2007 (Special Meeting - if needed).
Attachments: (A)
(B)
(C)
(D)
(E)
(F)
(G)
(H)
(I)
PowerPoint Slides
Draft Public Participation Plan .
Draft Shoreline Inventory, Characterization and Map Folio
Draft Environmental Designation Map
Draft Goals and Policies (amendment to Chapter Two ofComp Plan)
Draft Restoration Plan
Draft Shoreline Regulations (amendment to Chapter 18 of City Code)
Draft Cumulative Impact Analysis
Citizen Advisory Committee Minutes/Meeting Notes
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CITY OF .,. '7
Federal Way
Shoreline Master Program Update -
Public Participation Plan
City of Federal Way, Washington
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March 15, 2006
EXHIBIT 13
P~GE OF
City of Federal Way's SMP Update -Public Participation Plan '
Introduction
Washington State's Shoreline Management Act (SMA) requires jurisdictions that contain
"shorelines of the state" within their boundaries to periodically update their Shoreline
, Master Programs (SMP's). The City of Federal Way is beginning the process of
updating their SMP and must complete the update by July 2007.
Federal Way's updated SMP will be used as a planning document that will set policy
and regulation for the City's shoreline areas, including adjacent upland areas in the
shoreline jurisdiction within 200 feet of designated shorelines. The three primary areas
of focus of SMP updates are to; accommodate reasonable and protective uses of the
shoreline, protect shoreline environmental resources, and protect the public's right to
access and use the shorelines (RCW 90.58.020). These protections are designed to
meet the overarching policy of the Shoreline Management Act which is to ensure that
"the public's opportunity to enjoy the physical and aesthetic qualities of natural
shorelines of the state shall be preserved to the greatest extent feasible consistent with
the overall best interest of the state and the people generally." Since public use and
enjoyment of the shorelines is a principal factor in developing the planning document, it
is imperative that the public has opportunities to participate in the process. The
following details the Public Participation Plan for this project.
Goals of the Public Participation Plan
RCW 90.58.130 and WAC 173-26-090 and 100, require that local governments inform
the people of the state about the planning process and invite and encourage
participation by all who have any interest or responsibility related to shorelines, The
goal of the Public Participation Plan is to provide a guide to proactively encourage
public participation throughout the SMP update process. The City of Federal Way is
committed to encouraging coordinated and effective public involvement.
Overview of City and Shorelines
The City of Federal Way is located in the southwest corner of King County, 25 miles
south of Seattle and 8 miles north of Tacoma. With over 85,800 residents occupying a
land area of 22.5 square miles, it is the eighth largest city in the state of Washington.
The SMP update will also cover the city's Potential Annexation Area (PM) east of
Interstate-5 (the SMP will not be effective in the PM, however, until the area annexes
into the city). The PM is approximately 4,400 acres and is home to approximately
20,000 people.
Federal Way and its PM are located between Puget Sound and the Green River
Valley. Because of its geographic setting, it has some exceptional water resources
including eight miles of Puget Sound shoreline, five major stream systems, seven lakes
(within the city limits) and several unique wetlands. Additionally five major lakes are'
located within the PM. The shorel,i~es alo~tl;'~~~~~~~a~er systems are where
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Enviro Vision Corp.
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March 15, 2006
City of Federal Way's SMP Update -Public Participation Plan
community members live, work, and play and therefore are of great value to the
residents of Federal Way.
Roles and Responsibilities
The City of Federal Way is responsible for all aspects of the SMP update. The City will
be the primary regulator, with Washington State Department of Ecology (Ecology)
acting in a support and review capacity. 'Ecology is also required to approve some
permits and must approve new or amended shoreline master programs.
The primary contact for Federal Way's SMP update is:
Isaac Conlen
City of Federal Way
P.O. Box 9718
Federal Way, WA 980.63-9718
(253) 835-2643
isaac.conlen~citvoffederalway. com
Key Parties
Local governments must consult with interested parties throughout the ,process of
developing a SMP. Federal Way will involve representatives from the following:
, '
o Residents of Federal Way
o Puyallup Tribe
o Muckleshoot Tribe
o Friends of the Hylebos
o Lake Associations ,
o Property/Business owners in the shoreline environment
o Federal Way City Council
o Federal Way Land Use and Transportation Comrriission (LUTC)
o Federal Way Planning Commission '
o City of Des Moines
o City of pacific
o City of Milton
o City of Fife
o City of Algona
o City of Kent
o City of Edgewood
o City of Tacoma
o King County
o Pierce County
o Department of Ecology
o Department of Fish and Wildlife
o Department of Natural Resources
Enviro Vision Corp.
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, March 15, 2006
City of Federal Way's SMP Update -Public Participation Plan
o Department of Community, Trade and Economic Development
o State Office of Archaeology and Historic PreserVation
o NOAA Fisheries
o US Fish and Wildlife Service
o WRIA 9
o WRIA 10
Some of these parties will be involved on committees in a review capacity while others,
will be informed and invited to participate throughout the process. '
Other stakeholders not included as key parties in the list above may also be notified
directly during the public involvement process. These other stakeholders may include
homeowner associations, environmental groups or others. Notification to these
stakeholders may be accomplished via email or other means as the shoreline
management planning process proceeds. '
Public Participation Strategy
The City of Federal Way has developed a strategy to ensure there is effective public
participation throughout the process. The primary methods to be employed are:
~ Formation of a technical advisory committee (T AC)
consisting 9f appropriate technical representatives of
affected Tribes, state and federal agencies and other
affected agencies to provide input and revieW of work
products.
~ Formation of a citizen advisory committee (CAC)
consisting of local residents, businesses and
, stakeholders to proVide input and review work
products.
~ Development of a public outreach program to .inform
community members. '
~ Updating the City Council, Planning Commission, and
LUTC periodically. .
By utilizing all of these methods, the City shall exceed the mandates of Washington
State to involve all interested parties in the update of the SMP.
Further details regarding these primary methods are as follows:
Enviro Vision Corp.
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March 15, 2006
City of Federal Way's SMP Update -Public Participation Plan
Technical Advisory Committee (TAC)1
The T AC will consist of technical representatives of affected Tribes and other agencies
such as D~partment of Natural Resources, Ecology, Department of Fish and Wildlife,
King County, neighboring jurisdictions, etc. These representatives will be asked t6
provide comments and suggestions on work products developed for each task.
Citizen AdVisory Committee (CACl
The CAC will consist of local residents and stakeholders and may include
representatives from groups such as Homeowner Associations, the North lake Steering
Committee, the Steel lake Advisory Committee, lake Geneva Property Owners
Association, Chamber of Commerce, Friends of the Hylebos Wetlands, etc. It will be
important that the CAC-represent a cross section of interest groups and public values.
Meetings will provide a forum to review the technical work, discuss issues and suggest
solutions. Three meetings are tentatively scheduled at this time. By establishing a
committee of citizens, the City is encouraging direct input in 'the process. Based upon
public interest to date, this component of the, public participation plan may need to be
eliminated or delayed. The City will continue to solicit members for the CAC and also
rely on other elements of its public outreach program to encourage citizen participation.
Public Olitreach Program
In addItion to providing the forum of the CAC as a way for community members to be
involved, the City will also set-up a public outreach program to ensure that the broader
population is also informed. Some key elements,of this program include:
.Website3: Adding a page to the City's current website where
community members can access draft documents and maps, view
the schedule, check for meeting notices, obtain contact information
and submit comments. This will create one central location where the
latest information can be obtained. The City calendar could also
contain key dates in the development of the SMP.
· Open house: Hosting an open, house at a convenient location will
allow for the broad dissemination of information (Le. maps, proposals,
etc.) and opportunity for comment. In addition, project staff and City
personnel will be on-hand to answer questions from community
members and address any concerns.
I Federal Way has already sent invitations to participate in this committee.
2 Federal Way has already sent invitatipns to partiCipate in this committee. In addition, the City has
solicited for members through a press release and by posting a hotice on itswebsite.
3 The City has already developed a page on it's website for SMP'related material.
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March 15, 2006
City of Federal Way's SMP Update -Public Participation Plan
. Public meetinqs: Providing opportunity through the Planning
Commission, LUTC and City Council that allow for public input and
participation.
. Public hearinq: Organizing a public hearing for the draft proposal will
provide the community with the forum to include their comments into
the public record.
. Mailinq list: Maintaining a list of interested parties would provide the '
City with another avenue to keep. the public informed throughout the
update process. Notices of comment periods; public hearings or
open houses could be sent to parties on the mailing list.
. Comments: Establishing multiple means for submitting comments wiil
allow for interested people to choose their preferred way to provide
input. Methods can include on..:line comment forms, written comment
forms at the open house, public hearing testimony, and a direct email
address for comments. The City will consider all comments received
and will respond in aggregate or individually.
. Public notices: Notice of the open house and public hearing will be
placed on the City's website, public access channel, posted at City
Hall and local library branches and published in at least one local
newspaper (Le. Federal Way Mirror, Federal Way News, Tacoma
News Tribune or Seattle Times).
Updates to City Council, Planning Commission and LUTC
In order to meet the overallo\;>jective of adopting an updated SMP by July 2007, it is
important to keep interested parties at all levels adequately informed from the beginning
of the process. Through periodic meetings with the planning commission and LUTC,
concerns can be addressed as they surface. These meetings also provide another
opportunity for other interested parties to obtain information on the process. For the
final task of adopting the SMP, workshops have been scheduled to allow for thorough
discussion of the SMP's details.
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City of Federa/Way's SMP Update -Public Participation Plan
Timeline
The City of Federal Way is aware that developing and maintaining a schedule will
contribute to the successful adoption of the SMP. By laying out this tentative schedule
at the start of the process, the public is aware of key dates where input is especially
critical. The following timeline highlights key public involvement opportunities:
February .9;'2006'
March 9, 2006
March 15, 2006
March 27, 2006
April 26, 2006
May 31,2006
May 31 , 20.06
June 7, 2006
June 7,2006
September 13,'2006
October 25, 2006
October 25, 2006
November 1,2006
November 6, 2006
November 29, 2006
February 7,2007
February 21,2007
March 7 , 2001
March 19, 2007
April 2, 2007
April 17, 2007
May 1, 2007
June 29, 2007
'invlts.mOn'~ettt3r~to"(;AC "
Introductory letter to TAC
Public participation plan to Ecology
T AC comments due on inventory
T AC comments on intentory maps
T AC comments due on conditions report
CAC meeting on <;onditions report
Informational update to,Planning Comm.
Open HoLi~e
, ,
CAC meetingbnSMPgoals and policies
TAC comments due on draft SMP and
restoration plan
CAG ,m~~tin9 ,on draft SMP and
'r~stQr:atiorl,pl~1;l
Planni~g Comrn.Meeting
,lUTG meeting
T Ac comments(:fue on cumulative impact
analysis
Planning Comm. workshop
, planning COffirn.,public hearing
Planning Comm. meeting-
recommendation
lUTC workshop
lUTCmeeting ~ recommendation
City Council ordinance - first reading
City Council ordinance - second reading
SMP to Ecology
If there are modifications to the timeline, the schedule on the City's website will be
updated. This plan will meet the requirements for public involvement opportunities in the
SMP update process. Modifications may be made if needed.
Enviro Vision Corp.
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March 15; 2006
EXHIBIT ,.., (./
PAGE OF
WASHINGTON STATE DEPARTMENT
OF ECOLOGY GRANT No.G06001 19
BUDGET BILL ESSB 6090
CITY OF FEDERAL WAY
SHORELINE INVENTORY
Be CHARACTERIZATION
REPORT
DRAFT
PREPARED FOR:
CITY OF FEDERAL WAY
AUGUST 1, 2006
PREPARED By:
Adolfson Associates, Inc.
5309 Shilshole Avenue NW, Ste 200
Seattle, Washington 98107
206.789.9658
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City of Federal Way Draft Shoreline Inventory & Characterization
CONTENTS
I NTR 0 D U CTI 0 N ...............................:................................................................................ 1
Background and Purpose.. ..........;........................................................ .......................... 1
Report Organization.................................................................................... .................. 1
Regulatory Overview....................................,....:............................. .......... ....................2
Shoreline Planning Areas................................................................. ..'...........................4
M ETH 0 DS ...........,............................................................................................................ 5
Data Sources....................................................................:.............. ...............................5
Approach to Characterizing Ecosystem-Wide Processes and Shoreline Functions ..... 7
Approach to Inventory and Characterization of Regulated Shorelines
at the Reach Scale.......... .......... ........ ................................. .......... ....... .......................... 7
3.0 ECOSYSTEM-WIDE PROCESSES & RELATIONSHIP TO SHORELINE FUNCTIONS 8
3.1 Watershed Context....................................................................................................... 8
3.2 Biological Resources............ ....................................................................................... 13
3.3 Major Land Uses and Shoreline Uses......................................................................... 14
3.4 Key Processes Related to Shoreline Functions ...................................................:...... 15
4.0 NEARSHORE/COASTAL pLANNING AREA INVENTORy...................................:...... 24
4.1 Physical Features........ .......... ................................................ ........................... ...........24
4.2 Biological Resources...... ........... .............. ......................................................... ...........32
4.3 Land Use Patterns..........:........................... .................................................................. 41
5.0 FRESHWATER LAKES PLANNING AREA INVENTORy............................................. 46
5.1 Physical Features........................................................................................................ 47
5.2 Biological Resources............................................. ...................... .................................53
5.3 Land Use Patterns..................... .......................................... .........................................60
6.0 RESTORATION AND OPPORTUNITY AREAS............................................................. 66
6.1 Coastal Areas / Nearshore Environment..................................................................... 67
6.2 Freshwater Shoreline Lakes........................................................................................ 70
7 .0 DATA GAPS .......... ................. ...... .......................... ........... ...... ........................................73
8.0 CON C L U S ION S .............................................................................................................. 73
8.1 Coastal Puget Sound................................................................................ ............ .......73
8.2 Freshwater Lakes........................................................ ............:...................................74
REF E R EN C ES ........................................................................................................................... 76
1.0
1.1
1.2
1.3
1.4
2.0
2.1
2.2
2.3'
LIST OF APPENDICES
Appendix A - Map Folio
LIST OF TABLES
Table 1. City of Federal Way Shoreline Planning Area ............................................................................... 5
Table 2. 303(d) Water Quality Exceedances in Federal Way and its PAA..............................................., 13
Table 3. Shoretypes, Modifications and Landslides, and Toe Erosion...................................................... 25
Table 4. Net Shore-drift Direction, Sediment Size, Beach Width............................................................... 25
Table 5. Ecology Slope Stability Map Designations .................................................................................. 30
August 2006
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City of Federal Way Draft Shoreline Inventory & Characterization
Table 6. Shellfish Population Densities in Southern WRIA 9....................................................:................. 37
Table 7. Forage Fish Species .........................,.......,.................................................................................. 39
Table 8. Land Use, Zoning, and Shoreline Environments ......................................................................... 43
Table 9. Federal and State, Listed Threatened and Endangered Species in Federal Way. ...................... 55
Table 10. Existing Land Use ................................,......................................................:..............................61
Table 11. Land Use, Zoning, arid Shoreline Designations ........................................................................62
August 2006
pageii
City of Federal Way Draft Shoreline Inventory & Characterization
1 ~O INTRODUCTION
1.1 Background and Purpose
The purpose of this study is to conduct ,a baseline inventory and characterization of conditions
relevant to the shoreline resources ofthe City of Federal Way (City), Washington. According to
Substitute Senate Bill (SSB)60l2, passed by the 2003 Washington State Legislature, cities and
counties are required to amend their local shoreline master programs (SMPs) consistent with the
Shoreline Management Act (SMA), Revised Code of Washington (RCW) 90.58 and its
implementing guidelines, Washington Administrative Code (WAC) 173-26. The City is
updating its SMP with the assistance ofa grant from the Washington Department of Ecology
(Ecology) (Grant Agreement No. 00600119). A first step in the comprehensive update process
is development of a shoreline inventory and characterization. The inventory and characterization
documents current shoreline conditions and provides a basis for updating the City's SMP goals,
policies, and regulations. This characterization will help the City identify existing conditions,
evaluate existing functions and values of its shoreline resources, and explore opportunities for
conservation and restoration of ecological functions. This study characterizes ecosystem-wide
processes and how these processes relate to shoreline functions. Processes and functions are
evaluated at two different scales: a watershed or landscape scale, and a shoreline reach scale. The
purpose of the watershed or landscape scale characterization is to identify ecosystem processes
that shape shoreline conditions and to determine which processes have been altered or impaired.
The intent of the shoreline reach scale inventory and characterization is to: 1) identify how
existing conditions in or near the shoreline have responded to process alterations; and 2)
determine the effects of the alteration on shoreline ecological functions. These findings will help
provide a framework for updates to the City's shoreline management policies and regulations,
which will occur later this year.
This shoreline inventory and characterization report was prepared by Adolfson Associates, Inc.
with technical assistance from Enviro Vision Corporation, Coastal Geologic Services, and
Shannon & Wilson, Inc. '
1.2 Report Organization
The information in this report is divided into seven main sections. The introduction discusses the
purpose of this report and describes the regulatory context for shoreline planning. The second
section describes the methods, approach, and primary'data sources ~sed for this inventory and
characterization. The third section provides an overview of ecosystem-wide processes and how
they affect shoreline ecological functions in the City of Federal Way. The fourth section
discusses physical features and biological conditions in or immediately adjacent to the Puget
Sound shoreline in Federal Way. The fifth section addresses these conditions for the freshwater
lakes in the City and its Potential Annexation Area (P AA). The sixth section describes
opportunities for conservation and restoration of shoreline areas in the City. The seventh section
identifies data gaps and provides recommendations for addressing those gaps. Finally, the last
section provides the overall conclusions of the shoreline inventory and characterization report.
August-2006
page 1
City of Federal Way Draft Shoreline Inventory & Characterization
Appendix A of this report is a map folio that includes several figures that identify the City's
approximate shoreline planning area and document various biological, land use, and physical
elements at a variety of scales. '
1.3 Regulatory Overview
'1.3.1 Shoreline Management Act and Shoreline Guidelines
Washington's Shoreline Management Act (SMA) was passed by the State Legislature in 1971
and adopted by the public in a referendum. The SMA was created in response to a growing
, ,
concern among residents of the state that serious and perman~nt damage was being done to
shorelines by unplanned and uncoordinated development. The goal of the SMA was "to pr~vent
the inherent harm in an uncoordinated and piecemeal development of the state's shorelines."
While protecting shoreline resources by regulating development, the SMA is also intended to
provide for appropriate shoreline use by encouraging land uses that enhance and conserve
shoreline functions and values.
The primary responsibility for administering the SMA is assigned to local governments through
the mechanism oflocal SMPs. The Washington Department of Ecology is responsible for
reviewing and approving local master programs, approving some permit decisions under the
SMA, and developing guidelines for the development and amendment of local master programs.
The state guidelines (WAC 173-26) establish an overarching framework of goals and policies
thatare implemented through local master programs, which contain goals, policies, and use
regulations for each city and county. Local SMPs are based on state guidelines but tailored to
the specific conditions and needs of individual communities. Local SMPs are also meant to be a
comprehensive vision of how the shoreline area will be managed over time.
1.3.2 Shoreline Jurisdiction
Under the SMA, the shoreline jurisdiction includes areas that are 2.00 feet landward ofthe
ordinary high watermark (OHWM) of Waters that have been designated as "shorelines of
statewide significance" or "shorelines ofthe state." These designations were established in '1972
and are described in WAC 173-18. Generally, "shorelines of statewide significance" include
portions oIPuget Sound and other marine waterbodies, rivers west of the Cascade Range that
have a mean annual flow of 1,000 cubic feet per second (cfs) or greater, rivers east of the
Cascade Range that have a mean annual flow of200 cfs or greater, and freshwater lakes with a
surface area of 1,000 acres or more. "Shorelines ofthe state" are generally described as all
marine shorelines and shorelines of all other streams or rivers having a mean annual flow of 20
cfs or greater and lakes with a surface area 2.0 acres or greater.
Under the SMA, the shoreline area to be regulated under the City's SMP must include all
shorelines of statewide significance, shorelines of the state, and their adjacent shore lands,
defined as the upland area within 200 feet ofthe OHWM, as well as any associated wetlands
(RCW 90.58.030). "Associated wetlands" means those wetlands that are in proximity to and
either influence or are influenced by tidal waters or a lake or stream subject to the SMA (WAC
173-22-.030 (1)). These are typically identified as wetlands that physically extend into the
shoreline jurisdiction, or wetlands that are functionally related to the shoreline jurisdiction
August 2006
page 2
City of Federal Way Draft Shoreline Inventory & Characterization
through surface water connection and/or other factors. The specific language from the RCW
describes the limits of shoreline jurisdiction as follows:
Those lands extending landward for two hundred feet in all directions as
measured on a horizontal plane from the ordinary high water mark; jloodways
and contiguous jloodplain areas landward two hundred feet from such jloodways;
and all associated wetlands and river deltas (RCW 90.58.030(2)(f)).
Local jurisdictions can choose to regulate development under their SMPs for all areas within the
I OO-year floodplain ora smaller area as defined above (RCW 90.58.030(2)(f)(i)).
1.3.3 City of Federal Way Shoreline Master Program
The City has two main types of water bodies that are regulated under the SMA and the City's
SMP (Figure 1). The City is bound on the west by the lower Puget Sound marine coastal
shoreline, which is designated a "shoreline of statewide significance." There are also several
freshwater lakes under SMA regulation within the City limits. These include Steel Lake, the
northwestern shore of Lake Killarney, and North Lake.
The City of Federal Way in conjunction with the county and other local municipalities has
identified an area largely to the east ofthe City and the Interstate 5 corridor for future
annexation. This area is in the King County designated Urban Growth Area (UGA) and is
referred to as the City's Potential Annexation Area (PAA). Lakes subject to SMA regulation
located within the City's PAA include Star Lake, Lake Dolloff, Five Mile Lake, Lake Geneva,
and the remaining portions ofLilke Killarney. The freshwater lakes are all designated as
"shorelines of the state." Lakes or portions thereof in the PAA (as well as the eastern shore of
North Lake) are currently regulated under the King County SMP.
State Master Program Guidelines (WAC 173-26-150 and 176-26-160) give local jurisdictions the
option to plan for shorelines in designated Urban Growth Areas and P AAs. The Ecology grant
for the City of Federal Way requires that the City plan for shorelines of the state, which lie
within the PAA. However, regulated shorelines in the PAA would continue to be regulated
under the provisions of the King County SMP until the City annexes those areas. King County is
required to update its SMP for shorelines throughout unincorporated portions of the County,
including designated UGAs, by the end of2009. '
There are no rivers or streams in Federal Way regulated Ullder the SMA. However, the
headwaters ofHylebos Creek lie within the City. Downstream portions of Hylebos Creek, where
the East and West Forks converge, are regulated shorelines ofthe state within the Cities of
Milton, Fife and Tacoma.
At the time of incorporation in 1990, the City of Federal Way adopted the King County SMP. In
1998 and 1999, the City developed and adopted its own local SMP. Shoreline management
goals and policies are contained in the land use element ofthe Federal Way Comprehensive Plan'
(FWCP, Section 2.8.5). Shoreline development regulations and permitting procedures are
codified in Chapter 18, Article III, ofthe Federal Way City Code (FWCC g18-161 through g18-
176).
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City of Federal W(1Y Draft Shoreline Inventory & Characterization
Local SMPs establish a system to classifY shoreline areas into specific "environme~t
designations." The purpose of shoreline environment designations is to provide a uniform basis
for applying policies and use regulations within distinctly different shoreline areas. In a
regulatory context, shoreline environment designations function similarly to zoning overlay
districts. That is, they do not change the underlying zoning or other applicable land use
regulations, but provide an additional layer of policy and regulations that apply to land within the
SMP jurisdiction. Generally, environment designations should be based on biological and
physical capabilities and limitations of the shoreline, existing and planned development patterns,
and a community's vision or objectives for its future development. During development of its
current SMP, the City evaluated the natural and built characteristics of its shoreline jurisdiction
and developed four. shoreline environment designations: Natural, Conservancy Residential,
Rural, and Urban.
A variety of other regulatory programs, plans, and policies work in concert with the City's SMP
to manage shoreline resources and regulate development near the shoreline. The City's
Comprehensive Plan establishes the general land use pattern and vision of growth the City has
adopted for areas both inside and outside the shoreline jurisdiction. Various sections of the
City's municipal code are relevant to shoreline management, such as zoning and stormwater
management. The City's development standards and use regulations for environmentally critical
areas are particularly relevant to the City's SMP. Designated environmentally critical areas are
found throughout the City's shoreline jurisdiction, including streams, wetlands, frequently
flooded areas, aquifer recharge areas, geologic hazard areas, and fish and wildlife habitat
conservation areas. .
1.4 Shoreline Planning Areas
The approximate extent of shoreline jurisdiction within the City of Federal Way and in its P AA
is shown on Figure 1, and referred to as the "shoreline planning area." In general, this extent
represents:
· 200 feet from the mapped waterline edge (to approximate OHWM) ofthe Puget
Sound coastal shoreline;
· 200 feet from the mapped waterline edge of seven freshwater lakes - Steel Lake, Lake
Killarney, North Lake, Five Mile Lake, Star Lake, Lake Dolloff, and Lake Geneva;
· All special flood hazard areas currently mapped by FEMA that are associated with
Puget Sound, streams discharging to Puget Sound, and the freshwater lakes; and
· All mapped wetlands that lie adjacent and contiguous to the areas above.
This approximate extent of shoreline jurisdiction should be considered useful for planning
purposes only since its resolution is based on relatively coarse mapping. Site-specific
delineation of floodplains, wetlands, and/or OHWM could result in modifications to the actual
regulatory extent of shoreline areas. '
For purposes ofthe shoreline inventory and characterization, the shoreline planning area was
divided into reach units. The coastal Puget Sound shoreline was divided into three reaches while
each lake is designated its own reach. The extent and general description of the individual
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City of Federal Way Draft Shoreline Inventory & Characterization
shoreline reaches that comprise the City's shoreline planning area are summarized in Table 1.
The rationale for delineating reach breaks is described in Section 2, Methods.
Table 1. City of Federal Way Shoreline Planning Area
General DescriR!i()n
Coastal Puget Sound lA
- East
Coastal Puget Sound lB
- Dumas Bay
CO,astal Puget Sound lC
- West
Steel Lake 2
Star Lake 3
Lake Dolloff 4
Lake Geneva 5
North Lake 6
7
Lake Killarney
8
Five Mile Lake
Total
1.67 From the City limits boundary with Des Moines on
Puget Sound, near 151 A venue South, extending west
to Dumas Bay
1.43 Dumas Bay
1.74 From Dumas Bay extending west to the City limits
along the King/Pierce County line, including Dash
Point State Park
1.69 Inside the City limits, west ofI-5.
1.33 Inside the northeast portion of the City's PAA, near
the bound with Ci of Kent
1.81 Inside the northeast portion of the City's PAA, near
1-5 and Milit Road.
1.12 In the southeast portion of the City's PAA, southeast
ofSR 18.
2.16 Inside the City limits, between 1-5, SR 18, and
Milit Road
2.12 Partially in the City limits, partially in the southeast
portion of the City's PAA, east ofI-5 and SR 18.
1.87 In the southeast portion of the City's PAA, near
Military Road.
Approximately 4.84 miles ofPuget Sound shoreline
16.93 and approximately 12.09 miles oflake shoreline.
2.0 METHODS
The following data sources and methodologies were used to complete this inventory and
characterization report.
2.1 Data Sources
A number of City of Federal Way, King County, state agency, and federal agency data sources
and technical reports were reviewed to compile this inventory and characterization, including but
not limited to the following:
· City of Federal Way Comprehensive Plan (2002);
· City of Federal Way Surface Water Facilities Plan (1994);
· City of Federal Way Potential Annexation Area Inventory (2002);
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City of Federal Way Draft Shoreline Inventory & Characterization
· Washington State ShoreZone Inventory (2001);
· Coastal Zone Atlas of Washington, King County (1979);
· The Catalog of Washington Streams and Salmon Utilization, Volume 1, Puget Sound
Region (1975);
· Washington State Department ofFish and Wildlife Priority Habitats and Species,
Washington Lakes and Rivers Information System Database and Marine Resource
Species information (2006);
· Marine Shoreline Inventory Report - WRIA 9. Prepared for Seattle Public Utilities and'
WRIA 9. (Anchor Environmental, 2004); and
· Inventory and Assessment of Current and Historic Beach Feeding SourceslErosion and
Accretion Areas for the Marine Shorelines of Water Resource Inventory Areas 8 & 9.,
Prepared by Coastal Geologic Services for King County Department of Natural
,Resources and Parks (Johannessen et at., 2005).
· Final Report, Prioritization of Marine Shorelines ofWRIA 9 for Juvenile Salmonid
Habitat Protection and Restoration. Prepared for WRIA 9 Technical Group. (Anchor
Environmental, 2006). .
A number of sources were also reviewed to characterize overall watershed and Puget Sound
nearshore conditions and to assess the ecological function of the Federal Way shorelines in an
ecosystem-wide context. Watershed- and Puget Sound-level condition sources reviewed for this
report include:
· Reconnaissance Assessment of the State of the Nearshore Report: Including Vashon and
. Maury Islands (WRIAs 8 and 9) (2001);
· Occurrence and Quality of Ground Water in Southwestern King County, Washington (1995);
· Geology and Ground-Water Resources of Southwestern King County, Washington (1969);
· Soil Survey of King County Area, Washington (1979);
· Washington Trout Water Type Survey Results, South King County (2004);
· Habitat Limiting Factors and Rec'onnaissance Assessment Report., Green/Duwamish and
Central Puget Sound Watersheds (WRIA 9 and Vashon Island) (2000); and
· Coastal Bluffs and Sea Cliffs on Puget Sound, Washington (2004).
Historic and current mapping and aerial photographs of the study area were consulted, and staff
biologists, geologists, and planners conducted a reconnaissance field survey of the City's
shoreline jurisdiction at existing public access locations. Sources of information on cultural and
historic resources included the Federal Way Historical Society website and consultation with the
King County Historic Preservation Program and the Washington Office of Archaeology and
Historic Preservation. '
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City of Federal Way Draft Shoreline Inventory & Characterization
2.2 Approach to Characterizing Ecosystem-Wide Processes and
Shoreline Functions '
SMA guidelines require local governments to evaluate ecosystem-wide processes during SMP
updates. Ecosystem-wide processes that create, maintain, or affect the City's shoreline resources
were characterized using an adapted version of the five-step approach to understanding and
analyzing watershed processes described in Protecting Aquatic Ecosystems: A Guide for Puget
Sound Planners to Understand Watershed Processes (Stanley et aI., 2005). This approach
defines watershed processes as the delivery, movement, and loss of water, sediment, nutrients;
toxins, pathogens, and large woody debris. The processes are qualitatively described using
available reports and spatial information related to topography, geology, soils, land cover, and
other themes. This approach is most appropriate at the watershed scale. However, conditions
arid processes at the watershed scale inform local planning by providing a broader understanding
of processes that influence shoreline conditions and functions. .
Natural processes, and alterations to those processes, are described at a variety of geographic
scales based on existing reports and readily available mapping information. No new quantitative
analyses were performed to develop' the summaries and characterization included in this
document.
For marine shorelines, processes are described in the context of coastal processes in Puget Sound
generally, and how those processes are affected by conditions in the Federal Way shoreline. For
upland areas, processes'and conditions in areas outside of the shoreline jurisdiction; but which
may influence shoreline conditions and functions, are described. Surface water drainage basins
delineated by King County Surface Water Management were used to delineate areas that
contribute flow to regulated waterbodies (i.e., Puget Sounrland freshwater lakes) in the City and
its P AA.
2.3 Approach to Inventory and Characterization of Regulated
Shorelines at the Reach Scale
The inventory of Puget Sound and lakes at the shoreline reach scale is intended to characterize
conditions in and adjacent to the. regulated waterbody. The shoreline planning area roughly
approximates the regulatory limits of the City's SMP, and lakeswithin the City's PAA, as
described in section 1.4. GIS data were used to quantify certain conditions in this area (e.g.,
spatial extent of zoning or l~md uses). Aerial photography, review of existing reports, and brief
field reconnaissance were used to qualitatively describe conditions in the shoreline~
Reach boundaries are shown on Figure 1. Puget Sound was inventoried in three reaches,
described above. Reaches were delineated based on significant changes in the physical and
biological resource composition of the Puget Sound shoreline in the City. Reach lA, Puget
Sound East, is characterized by variable topography (i.e., bluffs transitioning into lower gradient
topography) and variable densities of development. Reach lB, Dumas Bay, is distinct as a
marine bay and estuarine delta with several freshwater stream inputs. Reach 1 C, Puget Sound
West, is characterized by variable topography, low-density development, and significant
recreational open space at Dash Point State Park. Each freshwater lake was inventoried as one
reach, due to the size and relatively consistent level of development of the lakes.
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City of Federal Way Draft Shoreline Inventory & Characterization
3.0 ECOSYSTEM-WIDE PROCESSES & RELATIONSHIP TO
SHORELINE FUNCTIONS
The ecosystem-wide processes that form and maintain Federal Way's coastal/nearshore
shorelines and freshwater lakes are focused on hydrology (i.e., the quantity and timing of surface
flow and groundwater flow characteristics). These processes occur at a landscape or watershed
scale and serve to form, maintain, or influence shoreline ecological functions. Examples of
shoreline functions include habitat structure, nutrient filtering, and vegetation (which provides
temperature control and organic inputs).
Changes in land use patterns and development across the landscape, not solely at the water's
edge, may change these processes and alter shoreline functions. Geographic areas that are
important in maintaining these processes are discussed at the watershed scale generally, and
more specifically in the vicinity of Federal Way and itsPAA. This section discusses the
watershed context of Federal Way and its PAA and the key processes affecting shoreline
functions for both the coastal Puget Sound and the freshwater lake shorelines.
3.1 Watershed Context
Water flow drives many ecological processes; therefore a useful characterization study area is
the watershed. Surface and groundwater flow in the watershed is controlled by climate,
topography, vegetation, soils, and geologic conditions. In Washington State, watersheds at a
large scale are organized into Water Resource Inventory Areas (WRIAs). The City of Federal
Way is located within the Duwamish-Green River WRlA 9 and the Puyallup-White River WRIA
10 (Figure 2). An Inventory of Federal Way's marine or coastal shoreline was conducted in
January of2004 as part ofa report prepared for Seattle Public Utilities and WRIA 9
(Johannessen et aI., 2005). This 2004/2005 inventory describes the coastal process in action
along Puget Sound within the City. The freshwater shoreline lakes in the City are located at the
headwaters of several drainage basins flowing to the two main watersheds.
The Duwamish-Green River (WRIA 9) watershed encompasses lands within the City and P AA
that drain to coastal areas, Mill Creek and the lower Green River, including Mullen Slough. The
Mill Creek Sub-basin drains the PAA area to the east of the City, including the area around Lake
Dolloff (Reach 2). The sub-basin stretches east and north of the City, eventually entering the
Duwamish-Green Basin to the north of Auburn. The Lower Green River Basin drains the
northwest corner of the City and the PAA to the northwest of the City, including the area around
Star Lake (Reach 7). Water flow from this area of the City and PAA enters into Mullen Slough
prior to draining to the Green River. The Lower Puget Sound Basin and its nearshore areas are
included into the WRIA 9 area.
The White River Basin (WRIA 10) drains the southwest areas of the City and the PAA,
including the area around Five Mile Lake (Reach 1). The White River Basin joins with the
Puyallup River Basin before entering Puget Sound at Commencement Bay. A large portion of
the City and PAA lies within the Hylebos Creek Basin, including North Lake (Reach 5) and
Lake Killarney (Reach 4) to the east. Hylebos Creek flows to the south beyond the City limits of
Federal Way until the creek enters the Hylebos Waterway, a working seaport waterway in the
City of Tacoma at Commencement Bay.
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City of Federal Way Draft Shoreline Inventory & Characterization'
3.1.1 Climate
Federal Way is located in the greaterPuget Lowlands of western Washington. This area,
surrounding Puget Sound, has a maritime climate with cool winters, dry summers, and a distinct
rainy season through fall and spring. The Federal Way area has recorded average January low
temperatures of approximately 350 F and average July high temperatures of approximately 76 of.
Precipit~tion in the Puget Lowlands varies considerably because of the effects of mountains.
The Federal Way area receives between 35 and 40 inches of rain per year on average, with
approximately 75 percent ofthe precipitation falling between October and March (Woodward et
ai., 1995). Winds are generally from the southwest during the rainy season and from the
northwest during the dry summer months.
3.1.2 Topography
The Federal Way area watershed is located on a broad northerly-trending upland area (the Des
Moines Plain) located between the Duwamish Valley and Puget Sound. The upland plateau
largely lies between 200 to 400 feet above sea level. The area is bounded to the west by steep
coastal bluffs and to the south and east by steep valley walls that lead down to the relatively flat,
broad valley floors of the Puyallup and Duwamish Rivers (Figure 3).
Topography on the surface of the plateau is characterized by elongate, north-trending hills with
relatively low relief in the range of 40 to 100 feet. The surface has local closed depressions
occupied by lakes and poorly drained areas occupied by wetlands and peat bogs. Streams
draining the watershed are relatively short arid flow directly to Puget Sound or to the adjacent
river valleys. Some of these streams have incised deep ravines into the coastal bluffs and valley
walls.
3.1.3 Geology and Soils.
The geology ofthe Federal Way vicinity is summarized by Waldron (1961) and Booth and
others (2004 and in review). The geology along the marine shoreline is also documented in the
Coastal Zone Atlas of King County (Washington State Department of Ecology [Ecology], 1979).
Surficial geologic units are shown in Figure 4; soils classes are shown in Figure 5.
The upland plain at Federal Way is underlain by a sequence of glacial and nonglacial deposits
that overlie Tertiary bedrock. The depth to bedrock in the vicinity of the Federal Way is
approximately 1,000 to 1,500 feet (Jones, 1996). The area has been glaciated six or more times
in the past 2 million years. Each glacial advance likely left a sequence of deposits that consisted
, of fine-grained lacustrine (lake) deposits, outwash sand and gravel, and till. Many ofthese
deposits have been partially to completely eroded by subsequent glaciations or erosion during
interglacial periods. The many lakes in the Federal Way area are formed within these glacially
derived deposits.
The most recent incursion of glacial ice into the central portion of the Lowland is called the
Vashon Stade ofthe Fraser glaciation, which receded from the area about 13,500 years ago.
That glaciation is responsible for the majority of deposits that make up the s~rface ofthe upland
plain. North-trending elongate hills, or drumlins, that form the surface ofthe upland plain were
shaped by the moving ice sheet.
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City of Federal Way Draft Shoreline Inventory & Characterization
The steep-walled troughs that define the Duwamish and Puyallup Valley to the east and south of
Federal Way were probably constructed as glacial ice or subglacial streams cut into deposits of
previous glacial advances (Mullineaux, 1974; Booth, 1994). FofIowing recession ofthe ice
sheet, the troughs existed as historic embayments ofPuget Sound. The troughs were filled
principally by estuarine deposits, lahars and lahar derived sediment from Mount Rainier, and
alluvium ofthe White and Green Rivers (Dragovich and others, 1994). Glacial and non-glacial
deposits that predate the Vashon Stade are exposed in the steep walls of the troughs.
Steep coastal bluffs that define the western City limits of Federal Way were probably formed by
coastal erosion following retreat ofthe ice sheet and regional drop in relative sea level (Shipman,
2004). Wave erosion at the base of the coastal bluffs, along with landsliding and mass wasting,
have caused episodic but continual retreat ofthe shoreline. Landslide and mass-wasting deposits
are exposed along these cliffs, along with older glacial and non-glacial sediments.
Most soils, exposed at the ground surface within the study area are glacial deposits left during the
most recent ice-sheet advance (Waldron, 1961; Booth and others, 2004). Lodgment till mantles
much of the upland area in the vicinity of Federal Way (Figure 4). The till is a poorly sorted
mixture of gravel, sand, silt, and clay deposited at the base of a glacier. Till is typically very
dense due to compaction by the overriding ice. Such deposits have very low permeability and
often act as aquitards, restricting the downward flow of groundwater.
. Recessional outwash and recessional lacustrine deposits overlie the till in places on the upland
plain. These sediments were deposited in topographic lows in the till surface where meltwater
streams drained from the receding glacier, such as along the headwater areas of Mill Creek
(Figure 4). The recessional outwash deposits typically consist of well-sorted sand and gravel.
Recessional lacustrine deposits generally comprise silt and clay. Peat deposits are found on the
surface of the plain on top of poorly drained lacustrine deposits or on top of outwash deposits
that are underlain by till at shallow depths. The peat deposits are commonly associated with
larger wetland areas within the watershed (Figures 4 and 5).
Underlying the till are thick deposits of sand and gravel separated by finer grained layers of clay
and silt or tight, well-graded soils, such as till from previous glaciations. These layers comprise
several aquifers and aquitards within the subsurface and control subsurface water movement to
the shorelines and adjacent valleys.
3.1.4 Surface and Groundwater
There are five major stream systems in Federal Way, including West Hylebos Creek, Cold
Creek, Joe's Creek, Lakota Creek and Redondo Creek (Figure 6). The City's surface water
bodies also include several lakes, only two of which (Steel and North Lakes) are considered
shorelines of the state; these are: Steel, Panther, Easter, Mirror, Lorene, Jeanne, and North. In
addition, many unique, rare and useful wetlands and bogs are spread throughout the city,
including West Hylebos Wetlands State Park and Fisher's bog.
The Federal Way watershed lies within the South King County Groundwater Management Area.
Information concerning groundwater recharge, monitoring, contamination, and management
specific to the Federal Way area is readily available on the King County Groundwater
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City of Federal Way Draft Shoreline Inventory & Characterization
Management website (http://dnr.metrokc.gov/wlr/wq/groundwater-data.htm). Groundwater and
hydrology of the watershed is described by Luzier (1969) and Woodward et al. (1995).
Additional analysis and groundwater protection planning are being conducted under King
County's Groundwater Management Program.
The upland surface has several small lakes and numerous streams that flow short distances from
the upland area to the shoreline and adjacent valleys (Figure 6). Precipitation falling within the
watershed is conveyed directly to lakes and streams by surface runoff or travels in the subsurface
as groundwater flow. Water from precipitation generally soaks into the ground, but during heavy
rainfall the ground quickly becomes saturated, inhibiting further infiltration. Water that is unable
to infiltrate travels down slope across the ground surface as stormwater runoff. Surface runoff
may erode soil, which is conveyed to streams and eventually to the shoreline ofPuget Sound.
Impermeable surfaces such as pavement, rooftops, or compacted ground increase stormwater
runoff. Conversely, vegetation promotes infiltration by intercepting rainfall, effectively
spreading precipitation events over longer periods oftime and reducing peak flows and
associated sediment transport. Vegetation also reduces erosion by holding soil in place and
reducing splash erosion.
Poorly drained areas of the upland plateau are the sites of former or existing wetlands. Wetlands
regulate the flow of water within a watershed by storing water during precipitation events,
slowing the conveyance of water from the upland to the shoreline, and increasing infiltration.
Development has reduced the number and area ofwetIands in the upland plateau, causing higher
volumes and peak rates of storm water runoff.
Water that infiltrates into the grouQd generally flows downward until impeded by less permeable
soils and then flows laterally to a body of water or to a slope face where it may emerge as springs
, or seeps on the hillside. A portion of the groundwater, however, will percolate downward
through lower-permeability soils to underlying more permeable soils or aquifers. Because of the
complex stratigraphy of soils in the Puget Lowland, several aquifers exist within the subsurface.
For the uppermost aquifer beneath the till, groundwater flow is radially outward from a
groundwater high that lies beneath Star Lake (Woodward et aI., 1995). Several deeper aquifers
'exist within outwash deposits in older glacial drift. Groundwater highs for the uppermost of
these aquifers are situated to the south of Star Lake and just south of DumaS Bay.
3.1.5 General Coastal Processes
The shores of Federal Way encompass 4.8 linear miles from the intersection of Redondo Beach
Drive South and 1st A venue in Des Moines southwest to the King-Pierce County line (DNR
2001). The major factors influencing the beaches of Federal Way include the local geology,
fluvial systems, and variable degrees of wave exposure and development. The beaches of Federal
Way are generally of two different characters, eroding bluffs or estuarine shores, with varying
degrees of development and related shore modifications (Figure 7).
The coastal zone is a dynamic environment, and human actions can easily alter the natural
system. Therefore, it is important for communities to understand potential impacts of land use.
General coastal processes are well summarized in the Coast of Puget Sound by Downing (1983)
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City of Federal Way Draft Shoreline Inventory & Characterization
and by Shipman (2004). Steep, gradually receding bluffs back much of the shoreline in Federal
Way. Over time, the bluffs erode and recede landward, providing sediment to the shore. Prior to
construction of bulkheads and other structures that were intended to protect property from wave
and tidal action, intermittent landslides occurred along bluff shores, although natural bluff
recession rates were generally quite slow in most ofPuget Sound. Sediment that accumulates at
the base of the bluff helps to protect the bluff from further erosion and reduces the recession rate.
Sediment from eroded bluffs may enter the intertidal zone within the nearshore, where it is
subject to transport by waves and water currents (Figure 7).
Prevailing winds and waves cause littoral drift, which is the movement of loose sediment along
the shore, primarily within the intertidal zone. Sediment that is sufficiently small, typically sand,
is suspended for short durations by wave action and is transported along the shore parallel to the
beach. Gravel is tran~ported by rolling (saltation) as a result of storm waves, and plays an
important role in beach stability. The direction of drift transport is generally in the direction of
prevailing winds, which may differ in the summer and winter. The predominant, or net-shore
drift direction is the most important consideration for coastal processes (Figure 7). Where
natural net-shore drift is blocked, beach processes are altered. Transported sand and gravel
accumulates on the updrift side of shore obstructions (the side opposite the net-shore drift
direction) and is depleted on the downdrift side of obstructions by blocking the transport of drift
material. Such obstructions include human-built structures such as bulkheads, breakwaters,
groins, docks, and boat ramps. In areas where the beach is depleted, erosion accelerates.
Shoreline armoring using bulkheads and other hardened structures eliminates the transport of
sediment to the beach from natural upland sources. The elimination of sediment supplied to the
shore also results in an increase in erosion processes along the beach.
Owners of property adjacent to the shore commonly construct rock or concrete bulkheads to
protect the bank or bluff from erosion. Such measures can increase beach depletion as wave
energy is reflected rather than absorbed. The shoreline processes and conditions along the
Federal Way coastline ~re summarized in the Net-shore Drift of King County (Chrzastowski,
1982), whiCh updated the coastal drift section of the Coastal Zone Atlas of King County
(Ecology, 1979). These processes and conditions have been re-evaluated by Johannessen and
others (personal communications) in work completed in 2005 for WRIA 9.
3.1.6 Water Quality
The Washington Department of Ecology maintains a 303(d) list of water bodies where tested
pollutants exceed thresholds established by the state surface water quality standards (WAC 173-
201A). Section 303(d) of the Federal Clean Water Act requires Washington State to periodically
prepare a list of all surface waters in the State for which beneficial uses of the water, such as
drinking, recreation, aquatic habitat, and industrial use, are impaired by pollutants. Lakes and
streams that do not appear on the 303(d) list may fall short of that pollutant threshold, but may
not be free of pollutants. In addition, not all streams, or all stream reaches are tested as part of
this process. Therefore, absence from the 303(d) list does not necessarily indicate that the
waterbody is not impaired. The 1998 303(d) list was the last one submitted to and approved by
the federal Environmental Protection Agency (EPA). A preliminary draft of Washington State's
2004 303(d) list is currently available for public review. Although not yet approved by EPA, the
listings are included below.
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City of Federal Way Draft Shoreline Inventory & Characterization
Table 2 shows the waterbodies within the City and its P AA that were listed in both the 1998
, approved 303(d) list and the proposed 2004 list, as well as the water quality parameters that
exceeded standards for the class of water tested. Several ofthe freshwater lakes and the Hylebos
Creek are included on Washington State's 1998 303(d) list and 2004 proposed list.
Table 2. 303(d) Water Quality Exceedances in Federal Way and its PAA
W'ith:ill :::~. .
CitylPAA "
"
Puget Sound Dioxins ./ Water
Central
Furans ./ Water
Total PCBs ./ Water
Steel Lake Fecal Coliform ./ Water
Star Lake Fecal Coliform ./' Water
Lake Dolloff Fecal Coliform ./ Water
Lake Geneva Fecal Coliform ./ Water
Lake Killarne Fecal Coliform ./ Water
Five Mile Lake Fecal Coliform ./ Water
Joe's Creek Fecal Coliform ./ ./ Water
H Jebos Creek Fecal Coliform ./ Water
Source: Washington State Department of Ecology. 2005
./
./
./
./
./
./
./
./
./
./
./
The City ofPederal Way monitors the quality of streams within the city limits. Surface Water
Management maintains and operates water quality instruments throughout the city that
continuously detect and record pollutant levels of concern. In addition, biological monitoring is
performed annually in selected streams to help us gauge the condition ofthe aquatic habitat,
water quality, and overall ecosystem productivity.
3.2 Biological Resources
Biological components ofthe watershed are important factors in maintaining ecosystem-wide
processes along with hydrologic and geologic components. The presence of vegetation serves to
intercept rainfall and increase infiltration of surface water runoff. Trees and native plants
provide habitat for fish and wildlife and contribute large woody debris as habitat components in
the shoreline. Wetlands also provide functions in a watershed context to protect the ecosystem-
wide processes that protect shoreline functions.
3.2.1 Vegetation
Historically, vegetation within the watershed was coniferous forest, deciduous riparian forest and
wetland or other native habitat types. Vegetation existing today within the watershed is largely a
function of the type and degree of residential and commercial development within the Federal
Way area. Little natural vegetation remains within the urbanized City as it has developed in
commercial, industrial, and low- to high-density residential land uses. Native vegetation is
restricted to undeveloped areas, and includes land along existing wetlands and streams. In
, addition, the areas preserving the greatest amount of native vegetation are the steeper slopes
between the upland and lowland areas, and open s'pace areas, such as parks.
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City of Federal Way Draft Shoreline Inventory & Characterization
Native vegetation in undeveloped or less developed areas ofthe City comprises trees, such as
Douglas fir, western red cedar, western hemlock, big-leaf maple, and red alder. Western red
cedar, once dominant in wetter areas, is less common. Common upland understory plants
include salal, ferns, Indian plum, Oregon grape, elderberry, oceanspray, salmonberry, and
snowberry. Non-native plant species, such as Himalayan blackberry, cut-leaf blackberry, Scot's
, broom and reed canarygrass, are also present within the forested habitats. Vegetation present in
developed areas may include native plant species, but ornamentals or landscaping varieties are
more prevalent.
A reduction in native vegetation and primarily forested cover occurs as land is developed in
urban uses. This conversion to impervious surfaces results in an overall increase in surface water
runoff velocity, higher peak flows during storm events, lower stream baseflows, and an increase
in erosion, sediment transport and turbidity in natural surface waters.
3.2.2 Wetlands
Wetlands are an important component of a healthy watershed, providing functions such as
floodwater storage, stormwater detention, water quality improvement, shoreline protection and
habitat for fish and wildlife. In Federal Way, a wetland inventory was completed in 1999 that
identified a total of232 wetlands, 170 of which were within the City limits and 55 of which were
in the 'unincorporated P AA (Figure 6). Of all wetlands surveyed, more than half were less than 1
acre in size and more than 80 percent were less than 5 acres in size. Wetlands were rated using
the City's three-tiered rating system that incorporates wildlife and plant species identified,
ecological functions and other wetland characteristics (FWMC 18-28, Sheldon and Associates,
1999). The higher value Category I wetlands make up large portions of the total wetland acreage
both within the City (50 percent) and the PAA (75 percent). Wetland inventoried in the City and
its P AA are largely associated with existing lakes and streams.
Within the City, wetlands were identified most frequently in association with West Hylebos
Creek, Lakota Creek, and Joe's Creek. Within the PAA, wetlands were identified most
frequently in association with Mill Creek and East Hylebos Creek. Several important wetlands
and bogs occur throughout the city, including West Hylebos Wetlands State Park and Fisher's
bog.
3.3 Major Land Uses and Shoreline Uses
Historically, land use within the Federal Way area was predominantly timber-oriented. The U.S.
Geological Survey created a Land Classification map ofth6 Federal Way area in 1897. Within
0.5 to 1.5 miles of the marine shoreline, forests had been harvested for timber and restocked for
subsequent harvest. Further inland from the marine shoreline, the majority of lands, including
those surrounding the freshwater lake shoreline areas, were classified as "uncut merchantable
forests." Throughout the City area the map shows small, interspersed areas of clearing and
human development both along the marine shoreline and inland areas. (USGS, 1897)
By 1940, the development pattern in Federal Way was predominantly single-family homes
located around lakes and along major roads (Figure 8). Vegetation had grown in some areas near
the Puget Sound shoreline that had been previously harvested for timber. More significant
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City of Federal Way Draft Shoreline Inventory & Characterization
development in the vicinity has occurred since 1940, with subdivision development throughout
the City and commercial development along and between the SR 99 and Interstate-5 corridors
(Figure 8).
Today, single-family residential development is the dominant land use, occupying approximately
42 percent of the land area in the City of Federal Way. Multi-family development occupies 11
percent of the total land area. Commercial developments (including office, retail, and industrial)
occupy approximately 12 perceht ofthe City's land area and are located primarily in the
downtown area, and along major transportation corridors including Pacific Highway South and
Interstate 5. One percent ofthe land area is made up of religious services. Parks and public
beaches occupy 6 percent of the City's land area. Vacant lands occupy approximately 12 percent
ofthe City (City of Federal Way, 2002). '
3.4 Key Processes Related to Shoreline Functions
Ecosystem-wide processes that create, maintain, or affect the City's shoreline resources were
characterized using an adapted version ofthe five-step approach to understanding and analyzing
watershed processes developed by Ecology (Stanley et aI., 2005). This approach defines
watershed processes as the delivery, movement, and loss of water, sediment, nutrients, toxins,
, pathogens, and large woody debris.
The key processes affecting shorelines in Federal Way and the factors and mechanisms that
control them are discussed in this section.
3.4.1 Processes Affecting Marine Coastal Shorelines
Federal Way beaches represent a commonly occurring beach character found in Puget Sound,
having two distinct foreshore components: a high-tide beach and a low-tide terrace (Johannessen
1993). The high-tide beach consists of a relatively steep beachface with coarse sediment and an
abrupt break in slope at its waterward extent. Sand in a mixed sand and gravel beach is typically
winnowed from the high-tide beach by waves (Chu 1985) and deposited on the low-tide terrace.
Extending seaward from the break in slope, the low-tide terrace typically consists of a gently
sloping accumulation of poorly sorted fine-grained sediment (Komar 1976, Keuler 1979,
Johannessen 1993). Lag deposits derived from bluff recession are also found in the low-tide
terrace. These deposits are typically comprised of larger materials, ranging from cobbles to
boulders.
3.4.1.1 Beach Composition and Sediment Sources
Puget Sound beach composition is dependent upon three main influences: 1) wave energy, 2)
sediment sources, and 3) relative position of the beach within a littoral cell. Wave energy is
controlled by fetch; the open water over which winds blow without any iilterference from land.
Within the Federal Way study area fetch is limited to 28 miles from the north (Adelaide to
Indianola on the Kitsap Peninsula), and 5.5 miles to the northwest (Dash Point State Park to
inner shores of Quartermaster Harbor). Segment exposure was classified by DNR's Shorezone
inventory as "semi-protected" (DNR 2001). Eastern Federal Way marine shores have greater
fetch than western shores that are protected by Vashon and Maury Islands to the north. The
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City of Federal Way Draft Shoreline Inventory & Characterization
northern orientation ofthe shore precludes the region's predominant and prevailing southerly
winds from exerting high wave energy on the shore.
Wind-generated waves gradually erode beaches and the toe of coastal bluffs, usually leading to
landslides (Hampton and others 2004). These coastal bluffs are the primary source of sediment
for most Puget Sound beaches, including the Federal Way study area (Keuler 1988, Downing
1983). Currently, 37 percent of the Federal Way's marine shores are comprised of eroding
coastal bluffs (feeder bluffs; Johannessen et aI., 2005).
Bluff composition arid wave energy influence the composition of beach sediment. Waves sort
coarse and fine sediment and large waves can transport cobbles that small waves cannot. This
results in relatively fine~grained beaches where wave energy is lowest, as these waves cannot
transport coarse gravel. Additionally beaches supplied by the erosion of coarse gravel bluffs will
differ in composition from those fed by the erosion of sandy sediment. The exposed strata ofthe
eroding bluffs in the northeastern 'portion ofthe study area are of a different character than those
of the southwestern shores, resulting in spatial variability in beach materials. Northeastern
beaches are typically made up of coarse material, typically comprised of coarse sands with
moderate pebble, due to the poorly-sorted, coarse grained strata that makes up the bluffs (Qmw;
W A DNR 2001) (Figure 4). The bluffs ofthe southwestern portion ofthe study area are.
composed ofVashon advance outwash deposits, which are predominantly composed of medium
to fine-grained sand. As a result, beach material in the southwestern portion of the study area is
finer grained and considerably sandier than the northeastern beaches of Federal Way (DNR
2001).
In addition to the previously mentioned influences (wave energy and sediment sources), tidal
range also affects beaches over time. Rosen (1977) demonstrated that the coastal erosion rate
increases with decreasing tidal range. This is due to the focusing of wave energy at a narrow
vertical band with small tidal range in comparison to the dissipation of wave energy over a large
vertical band with a greater tidal range. The mean tidal range in the study area is roughly 10.5 to
11.9 feet or meso-tidal (2 - to 4 m range). This tidal range is lower than southern Puget Sound,
which means that erosion will be primarily focused withi~ the 10.5 to 11.9 feet ofthe beach'
profile exposed to tidal waters (excluding storm conditions). However, the majority of coastal
ero~ion in the region occurs when high wind events coincide with high tides and act directly on
the backshore and bluffs (Downing 1983). The majority of coastallandsliding occurs during and
following prolonged high precipitation periods in the winter (Tubbs 1974, Gerstel et al. 1997,
Shipman 2004).
3.4.1.2 Net Shore-drift
Wind-generated waves typically approach the shore at an angle, creating beach drift and
longshore currents t4at result in sediment transport through a process called littoral drift. Net
shore-drift refers to the long-term, net result of littoral drift. Net shore-drift cells represent a
sediment transport sector from sediment source to sediment sink (deposition area) along a
portion of coast. Each drift cell acts as a system consisting ofthree components: 1) a sediment
source and origin of a drift cell (typically an eroding bluff area); 2) a transport zone where
materials are moved alongshore by wave action with minimal sediment input; and 3) an area of
deposition that acts as the drift cell terminus. Deposition of sediment occurs where wave energy
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City of Federal Way Draft Shoreline Inventory & Characterization
is no longer sufficient to transport the sediment in the drift cell. Drift cells in the Puget Sound
region usually range in length from 5 or more miles to just hundreds of feet.
The Federal Way study area contains one entire drift cell and two partial drift cells. The general
patterns of net shore-drift will be briefly described with more detailed descriptions of sediment
sources and depositional areas presented in the reach scale inventory. The northeastern portion of
the study area falls within drift cell KI-9-2 (also referred to as KI-10-1), which exhibits
southwestward drift. The drift cell originates approximately 2.4 miles northeast ofthe City
boundary (approximately 1,050 feet north of Saltwater State Park)., The drift cell terminates at a
convergence with cell KI-1O-2 in the southwest comer of Dumas Bay. Cell KI-lO-2 originates
east of a divergent zone at the southwestern headland that marks the western entrance to Dumas
Bay. Divergent zones are the areas between drift cells where the net shore-drift direction
changes. Cell KI-IO-2measures only 864 feet and exhibits southward drift. The western shore of
the City, west of the divergence zone located west of Dumas Bay, marks the origin of cell KI-10-
3 (also referred to as cell PI -1-1). This cell exhibits southwestward drift and terminates outside
the study area, at the cuspate foreland at Dash Point.
3.4.1.3 Coastal Bluff Landslides
Coastal landslides typically occur during periods of high precipitation on bluffs with a
combination of characteristics making the bluff more vulnerable to slope failure (Tubbs 1974,
Gerstel et al. 1997). These characteristics include the underlying geology of a bluff or bank, its
level of exposure (fetch), and the local hydrology (groundwater and surface water). As a result
the exposed high-gradient bluffs and banks ofthe eastern and western portion of Federal Way
are more susceptible to coastal landslides, relative to the central study area shore.
. Landslides are more likely to occur in areas where there is a history of landslides or where the
lower bluff strata is comprised of a consolidated impermeable layer (such as dense silt or clay)
that is overlain by an unconsolidated permeable layer (typically sands; Gerstel et al. 1997). As
water seeps through the permeable layer and collects above the imperm~able layer, a zone of
weakness or "slip-plane" is created. This stratigraphic sequence is a common setting for mass
wasting (landslides) in central Puget Sound. Recent mapping (Johannessen et al. 2005)
documented recent landslides across 18 percent of the Federal Way study area.
Undercutting of the toe ofthe bluff is the long-term "driver" of bluff recession (Shipman 2004,
Keuler 1988). Bluffs that are exposed to greater fetch are subject to higher wave energy during
storms, resulting in greater toe erosion and bluff undercutting, thus more frequent landslides
(Shipman 2004). Recent bluff toe erosion was documented along 28.1 percent of the Federal
Way shores (Johannessen et aI., 2005). Bulkheads reduce wave attack to blufftoes but can
accelerate erosion of the beach (see Shore Modifications section, below).
Storms that coincide with elevated water levels, such as a storm surge or extraordinary high-high
tide, often initiate landslides in the Puget Sound region (Johannessen and Chase 2003). The wave
attack caused by a storm that occurs in conjunction with heightened water level can produce
dramatic toe erosion, which then undermines and destabilizes a larger portion of the bluff that
may not fail (slide) until subsequent wet-weather months.
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City of Federal Way Draft Shoreline Inventory & Characterization
Two springs were mapped along the eastern bluffs of Federal Way, between Adelaide and the
northeastern limit of the study area.,It is common to observe groundwater seeping from the bluff
face following prolonged heavy precipitation. Periods of high rainfall intensity and duration
(especially during saturated soil conditions) are the most common trigger of coastal landslides
(Tubbs 1974, Thorsen 1987), such as those observed at New Years 1996-97 (Gerstel et al. 1997,
Shipman 2001).
Surface water volumes often increase and become more concentrated as a result of development
of housing and roads. This is due to decreased infiltration and interception of water.
Concentrated surface water can locally erode bluff crests while also saturating soils, which
exacerbates "natural" slope stability problems along coastal bluffs and can trigger landslides
(Shipman 2004). Runoffflowing down a driveway and rapidly across a lawn (which can absorb
little water when wet) as sheet flow to the bluff face is an example of this process. Failed
tightlines (constructed out of inexpensive and low-strength corrugated pipe) on a bluff face have
often contributed to initiating coastal landslides in King County.
Removal of bluff vegetation that results in a loss of root density and strength typically increases
the likelihood offuture landslides (Schmidtet al. 2001, Zeimer and Swanson 1977, Bishop and
Stevens 1964). Bluffs with significant modifications to both the natural drainage regime and
vegetation pattern are particularly susceptible to landsliding. Reestablishment and maintenance
of native vegetation cover or installation of a fibrous-rooted vegetation cover along with some
type, of drainage control can reduce the likelihood of the bank failures (Gray and Sotir 1996,
Menashe 2001, Roering et al. 2003).
The slope stability mapping in the Coastal Zone Atlas was recently digitized by the Washington
State Department of Ecology (1979). The mapping was originally performed in the 1970s using
aerial photograph analyses and field reconnaissance. Seven "recent landslides" were mapped in
the Federal Way shoreline planning area, predominantly located in the western portion ofthe
county. Five historic landslides were identified, three of which were located along the eastern
shores. The remaining slides were located in the western portion of the study area.
3.4.1.4 Fluvial Influences on the Nearshore
Fluvial sources contribute to nearshore character and can act as an agent of change on the marine
landscape. The quantity of fluvial sediment delivered to the nearshore depends up the nature of
the hinterland: its elevation, the types of rocks and soil found there, the density of vegetation,
and the climate (Komar 1976). The greater the volume of sediment, the greater influence on
nearshore processes. In a regional, ecosystem-wide context, , the fluviai influence on the Federal
Way nearshore is negligible since none of the streams in Federal Way discharge significant
volumes of sediment to Puget Sound.
3.4.1.5 Shore Modifications
A substantial portion of the Federal Way shoreline has been modified from its original state.
Shoreline modifications observed within the study area include: riprap and revetments,
bulkheads, fill, boat ramps and their associated footings. Approximately 38.4 percent of the
linear shoreline has undergone such modifications, excluding filling which is not easily observed
or formally inventoried (Johannessen et al. 2005). Modified shoreline segments vary in the
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City of Federal Way Draft Shoreline Inventory & Characierization
degree that they are modified. Each form of shore modification alters nearshore ecosystem
function or processes in some way.
, Riprap, Revetments, and 13ulkheads - Shore armoring or modifications that include covering the
beach and/or backshore with riprap, a rockery, revetment or a bulkhead directly impact the
nearshore. The effects of shore armoring on physical and biological processes have been the
subject of much concern in the Puget Sound region (for example, Rice 2006). Macdonald, ,et al.
(1994) completed a series of studies documenting the impacts to the beach and nearshore system
caused by shore armoring at a number of sites. Additional studies on impacts from shoreline
armoring have shown that in front of a bulkhead the suspended sediment volume and littoral drift
rate all increased substantially compared to an adjacent unarmored shore (Miles 2001).
A bulkhead-constructed near the ordinary high water mark (OHWM) in a moderate energy
environment increases the reflectivity of the upper beach to waves substantially, causing
backwash (outgoing water after a wave strikes shore) to be more pronounced. Increased
backwash velocity removes beach sediment from the intertidal beach, thereby lowering the beach
profile (Macdonald et al. 1994). A bulkhead constructed lower on the beach causes more impact.
Construction of a bulkhead at or below OHWM results in coarsening of beach sediment in front
of the bulkhead (Macdonald et al. 1994, Kraus 1988). Relatively fine-grain size sediment is
mobilized by increased turbulence caused by the bulkhead (Miles 2001), and is preferentially
transported away, leaving only the coarse material on the beach. This process also leads to the
removal of large woody debris (L WD) from the upper beachface. Both of these impacts lead to
changes in habitat along the armored portion of shore.
A number of local hydraulic impacts often occur in response to a bulkhead. These include the
formation of a scour trough (a linear depression) directly in front ofthe wall, probably as a result
of increased reflectivity ofthe wave energy from the wall to the upper beach. Another hydraulic
response is the formation of end erosion ("end effects"). This occurs at unprotected shores
adjacent to the end of a bulkhead and is caused by wave refraction at the end of the bulkhead
, ,
(Tait and Griggs 1991). "During storm" impacts, where seabed fluidization and scour occur at
enhanced levels, may be pronounced in front of a bulkhead, but this process is not well
understood.
The groundwater regime is often modified by the construction of a seawall along the base of a
bluff (Macdonald et al. 1994). An impermeable bulkhead that extends vertically above OHWM
raises the groundwater table. This can cause increased pore pressure in beach sediment, leading
to mobilization of beach sediment under lower energy waves, relative to unbulkheaded
conditions. This effect is most pronounced at locations with fine-grained beach sediment.
Of all the impacts of shore armoring in the Puget Sound area, sediment impoundment is probably
the most significant negative impact (PSAT 2003, Pilkey 1988). Structures such as bulkheads, if
functioning correctly, "lock up" bluff material that would otherwise be supplied to the shore drift
system. This results in a decrease in the quantity of drift sediment available for maintenance of
down-drift beaches. The negative impact of sediment impoundment is most pronounced when
armoring occurs along a feeder bluff with a high sediment yield such as the bluffs approximately
one-half mile east of Adelaide and in the western portion of the study area, just east of Dash
PointState Park (Johannessen et a12005, Macdonald et al. 1994). Additionally, the extent of
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City of Federal Way Draft Shoreline Inventory & Characterization
cumulative impacts from several long runs of bulkheads is a subject of great debate in the coastal
research and management communities.
A comparison of current and historical bluff conditions in King County documented that prior to
modifications 49.5 percent of Federal Way shores were comprised of feeder bluffs (sediment
sources). When compared with current conditions (37 percent), this represents a 25.2 percent loss
ofthe total historic sediment sources in the Federal Way nearshore (Johannessen et aI., 2005).
As the bluffs in the study area continue to gradually recede, there will likely be an increasing
desire for homeowners to build bulkheads. This would lead to further sediment impoundment
and, further reductions in the natural sediment supplied to drift cells and nearshore habitats, and
would therefore constitute a significant negative impact. Without this sediment, the beaches
would become "starved," resulting in a reduction of the beach width and habitat degradation
(Macdonald et al. 1994, Rice 2006). Beaches would also become more coarse-grained
(Macdonald et al. 1994) as sand was winnowed out leaving a higher percentage of gravel. This
would likely negatively impact forage fish spawning and other habitat values of county beaches
(Rice 2006). This could also lead to an increase in coastal flooding and wave-induced, erosion of
existing low-shore armoring structures and homes.
Filling -Fill areas along the shores of Federal Way are not always obvious today; however, they
quickly become apparent when comparing current and historic maps. For this purpose the U.S.
Coast and Geodetic Surveys' Topographic maps (T-sheets) were compared with USGS 7.5 '
minute topographic maps.
It appears that filling has taken place at several locations in Federal Way. The most obvious are
at the estuaries in Dumas Bay and Dash Point State Park. The marsh in western Dumas Bay was
historically considerably larger, but appears to have been reduced in size for residential
development. The estuary in Dash Point State Park also appears to have been filled and
channelized, possibly to reduce flooding and facilitate parking and recreational areas. Backfilling
ofbulkheaded shores appears to have occurred near Adelaide, where a historic accretion
shoreform previously occurred, and at the base of bluffs east of Dash Point State Park.
3.4.2 Processes Affecting Freshwater lake Shorelines
Ecosystem-wide,processes that affect lake shorelines include specific actions related to
hydrologic processes, sediment delivery, water quality and large woody debris. However,
unlike large river systems where water flow is affected by factors across a greater watershed,
lakes in Federal Way are located in the headwaters of drainage baSIns and are influenced by a'
limited ar~a draining to these waterbodies. Lake processes are more easily altered by nearby
land use modifications since they are directly tied to conditions in a smaller basin area.
3.4.2.1 Hydrology
Water naturally enters a watershed through rain, snow, or movement of groundwater. Water
moves within a watershed by surface water flow in rivers and streams, infiltrates and becomes
groundwater, or is stored in wetlands, lakes, and floodplains. In a natural system, the movement
and storage of water is generally controlled by physical conditions such as climate, topography,
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City of Federal Way Draft Shoreline Inventory & Characterization
land cover, and the permeability or infiltration capacity of soils and the underlying surficial
geology (Stanley, et aI., 2005).
Lakes in Federal Way have formed in shallow depressions remaining from glaciation on an
upland plateau. These areas are in the headwaters of the drainage basin and are not affected by ,
larger-scale ecosystem-wide processes occurring within the rivers in WRIA 9 and 10. The lakes
in Federal Way are important for maintaining stream baseflow for down gradient streams and
rivers.
Important areas for hydrologic processes affecting freshwater lakes in Federal Way include:
. Saturated areas or areas, which with low permeability provide overland or shallow
subsurface flow;
. Lakes, low-gradient floodplains, and depressional wetlands, which provide surface
water storage; and
. Topographic slope breaks or contact areas between geologic deposits of differing
permeability, which provide gr,oundwater discharge (i.e., retUrn to surface flow)
(Stanley, et aI., 2005).
Hydrologic processes influence the following shoreline functions:
. Quantity and timing of flow affects hydrologic functions such as channel incision and
flood storage; ,
. Quantity and timing of flow affects in-stream habitat functions such as channel
complexity and habitat availability; and
. Groundwater flow affects hydrologic and hyporheic functions such as baseflow and
temperature, as well as habitat and vegetation functions related to species diversity.
Groundwater flow affects these functions in both riverine and wetland ecosystems.
3.4.2.2 Sediment Delivery
Sediment is naturally delivered to streams and river systems through surface erosion, mass
wasting, and in-channel erosion. The delivery, movement, and storage of sediment is largely
driven by hydrologic factors and generally controlled by physical conditions such as topography
(gradient), land cover (vegetation), soil characteristics (erodibility), and the transport capacity or
velocity of moving water (Stanley, et aI., 2005).
Lakes in Federal Way do not naturally deliver sediment to downstream waterbodies, but rather
serve as "sinks" for sediment from urbanized areas. As such these areas are more sensitive to
urban development and inputs of sediment in surface water runoff.
Important areas for sediment delivery and movement in Federal Way include:
. Lakes, depresssional wetlands, floodplains, and depositional channels, which provide
sediment storage (Stanley, et aI., 2005).
Sediment processes influence the following shoreline functions:
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City of Federal Way Draft Shoreline Inventory & Characterization
. Sediment storage can protect downstream habitats from delivery of too much
sediment input, which can adversely affect habitat.
. Increases in sediment delivery to lakes can surpass the lake's capacity to assimilate
sediment and adversely affect habitat and water quality.,
3.4.2.3 Water Quality
There are many processes at work that maintain or affect water quality in a watershed. This
report focuses on the movement of phosphorus, toxins, nitrogen, and pathogens. Key processes
include biotic uptake and decomposition, adsorption, and denitrification. The movement of
water and sediment largely drives these processes, and they are generally controlled by physical
characteristics such as biotic cover and composition, soil characteristics, and bacterial activity
(Stanley, et aI., 2005).
Lakes in Federal Way are important areas for uptake and adsorption of nutrients to purify waters
to outlet streams ,and rivers. Wetlands associated with the lakes or those that drain to the lakes in
Federal Way serve to protect lake water quality th~ough several mechanisms.
Important areas for water quality related processes in freshwater lakes include:
'. Depressional wetlands with organic, mineral, or clay soils, which provide adsorption
of phosphorus, toxins, and pathogens (fecal matter);
. High-permeability geologic deposits, which allow subsurface transport of pathogens
while low-permeability deposits allow movement of pathogens via recharge;
. Depressional wetlands, which can both provide nitrogen (nitrification) and remove
nitrogen (denitrification);
. Riparian areas with a consistent supply of shallow groundwater, which provide
denitrification; and
. Headwater streams, which can provide biotic uptake and decomposition, and/or
adsorption of nitrogen (Stanley, et aI., 2005).
Water quality processes influence the following shoreline functions:
. Delivery and storage of nitrogen, phosphorus and toxins, and pathogens affect,
functions such as denitrification and nutrient cycling. Habitat functions such as'
invertebrate abundance and diversity, and food sources for fish, are also affected; and
. Delivery of nitrogen, phosphorus, and pathogens affects these functions in both
riverine and wetland aquatic ecosystems.
3.4.2.4 Large Woody Debris
Large woody debris (L WD) consists of logs or trees that have fallen into a river or stream. In a
natural system, L WD provides organic material to aquatic ecosystems and is considered a
principal factor in forming stream structure and fish habitat characteristics. Riparian vegetation
is the key source ofL WD. Large woody debris is primarily delivered to rivers, streams, or
wetlands by mass wasting, wind throw, or bank erosion (Stanley, et aI., 2005).
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City of Federal Way Draft Shoreline Inventory & Characterization
Lakes in Federal Way are largely developed in residential uses and will not likely provide
delivery ofL WD as a key function. Lakes may deliver woody debris to stream outlets, but this is
not an important function of the lakes in an urban setting. Delivery of L WD provides habitat
function within the lakes themselves along the lakeshore supporting both inwater and riparian
habitats.
Important areas for LWD delivery and movement in the lake of Federal Way include:
. Forested areas adjacent to aquatic resources, which can provide L WD via windthrow;
and
. Low-gradient channels, which provide storage ofLWD and organic material, subject
to the transport capacity of water (Stanley, et aI., 2005).
The presence, movement, storage, and decomposition ofLWD influence the following shoreline
functions:
. Delivery of wood and organics affects vegetation and habitat functions such as
lakeshoie habitat structure and species diversity; and '
. Riparian vegetation, especially L WD, provides habitat in the form of nesting,
perching, and roosting as well as thermal protection, nutrients, and sources of food
terrestrial insects) to a variety of wildlife species.
3.4.2,5 Shoreline Modifications
Lakes in Federal Way are most commonly influenced by surrounding development, which
affects ecosystem processes. Some ofthe most common alterations that impact lakes include:
. Removing native shoreline vegetation;
. Removing mature trees in upland and nearshore areas;
. Armoring the shoreline using bulkheads;
. Increasing impervious surface area in the watershed;
. Increasing stormwater runoff into the lake;
. Increasing fertilizer/pesticide runoff; and
. Increasing docks or other in-water structures.
These alterations affect shoreline processes through:
. Loss of habitat, shade, and insects which are important for fish;
. Increased sediment delivery, disturbing fish habitat and carrying pollutants;
. Increased wave action that can increase beach erosion rates;
. Loss of large woody debris for aquatic habitat;
. Decreased water quality from stormwater ruQoff;
. Increased rates of weed growth and algae blooms from increased nutrients; and
. Increased water temperature leading to more algae blooms.
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City of Federal Way Draft Shoreline Inventory & Characterization
4.0 NEARSHORE/COASTAL PLANNING AREA INVENTORY
The purpose of this section of the report is to inventory and characterize conditions within the
approximate boundaries ofthe City's nearshore/coastal shoreline planning area in greater detail
and in the context of the larger watershed, or landscape scale characterization of ecosystem wide
processes. The intent is to identify how existing conditions in the shoreline planning area
, influence or contribute to alterations of processes that maintain aquatic ecosystems. The study
area is shown on Figure 1 and subsequent figures as the City's shoreline planning area.
4.1 Physical Features
4.1.1 Coastal/Nearshore Processes and Modifications
The physical condition of the Federal Way coastal shores is the dynamic result of numerous
influences including geology, shoreline orientation, bathymetry, fetch, and geomorphology. Each
, segment of shore within the study area falls within a distinct littoral drift cell, which is composed
of a sedIment source, transport zone and depositional area (Figure 7). Sediment sources in the
study area are predominantly eroding bluffs, commonly referred to as "feeder bluffs".
Landslides and toe erosion commonly occur along these shores, where sediment is delivered to
the nearshore and transported along shore by littoral drift. Smaller quantities of sediment are
delivered to the nearshore by fluvial sources, though due to the small size of the streams and
relatively low-flow, fluvial sediment sources in the area have only local effects on the nearshore.
Transport zones are shores that are neither eroding nor accreting. Depositional areas, also
referred to as accretion shoreforms, are typically located near the drift cell's terminus (Jacobsen
and Schwartz 1981) and are associated with valuable habitats such as salt marshes, spits and
pocket estuaries.
The width of the beach, and more specifically the backshore, influences bluff erosion rates. Wide
beaches often typically have a storm berm in the uppermost beach, or backshoie, which functions
to absorb wave energy and protect the base ofthe bluff from wave attack. Wave attack leads to
toe erosion and bluff undercutting that destabilizes slopes. Where beaches are broad, due to
littoral drift deposition, a recent influx of sediment, or proximity to a groin or other drift
obstruction, bluff erosion and mass wasting may be locally reduced. Conversely, where beaches
are narrow and sediment "starved" due to either natural or artificial circumstances, the erosion
rate of associated bluffs may accelerate (Shipman 2004). '
Beach substrate is influenced by the geology of local sediment sources, wave energy and the
position ofthe beach within the netshore-drift cell. Bluffs in the eastern study area are composed
of larger sediment than bluffs located in the western area. As a result, beach material is finer at
western beaches, relative to those in the eastern portion ofthe study area. Additionally, sediment
size commonly becomes increasingly fine with increasing distance from the drift cell origin.
Erosion control or shore protection structures are common in the study area. Residential or
industrial bulkheading (also called seawalls) are typically designed to limit the erosion ofthe
backshore area or bluff, but have numerous direct and indirect impacts on nearshore systems.
Studies of the impacts of shoreline armoring have documented increased suspended sediment
and littoral drift rates along armored shores, relative to unarmored shores (Miles et al. 2001).
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City of Federal Way Draft Shoreline Inventory & Characterization
Bulkheads constructed lower on the beach (below the OHWM) result in coarsening of beach
sediment in front of the bulkhead (Macdonald et al. 1994). Relatively fine-grained sediment is
mobilized by the increased turbulence caused by the bulkhead (Miles et at 2001), and is
preferentially transported away, leaving the coarser material on the beach.
Of all the impacts of shore armoring in the Puget Sound area, sediment impoundment is probably
the lJlostsignificant negative impact (PSA T 2003). Bulkheads, and similar structures, essentially
"lock up" bluff material that would otherwise be supplied to the net shore-drift system. This
results in a decrease in the quantity of sediment available for maintenance of down-drift beaches.
The negative impact of sediment impoundment is most pronounced when armoring occurs along
actively eroding bluffs (Johannessen et al. 2005, Griggs 2005). Over the long term, the
construction of bulkheads on an erosional coast leads to the loss of beach area and complexity.
A recent study by Johannessen et al. (2005) mapped feeder bluffs, transport zones, accretion
shoreforms and modifications along the reaches of the Federal Way study area. Landslides and
toe erosion were also mapped throughout the study area. These data are summarized in Table 4.
Mapping by Schwartz et al. (1991) mapped littoral drift direction throughout the study area.
Table 5 displays net shore-drift direction, intertidal beach width, and sediment size.
Table 3. Shoretypes, Modifications and Landslides, and Toe Erosion
'_."';;"
.;;;~: ;
,t,.
. ;>1,,_.
, Shorieline
R,each
5.9%
8.4%
Modified LandSlides
21.8% 67.6% 5.9% 25.5%
18.2% 67.6% 0.6% 4.8%
7.3% 25.3% 44.6% 49.7%
Puget Sound
East
Dumas Bay
Puget Sound
West
38.0%
12.0%
60.9%
6.4%
Source: Johannessen, MacLennan and McBride 2005.
Table 4. Net Shore-drift Direction, Sediment Size, Beach Width
. N~t shol'e-dr-iftdirec,tion
Sediment size
Beach width
Puget Sound East
West
Pebble with moderate
sand
25-33 ft
Dumas Bay
Drift cell convergence.
Southwest and Northeast
Sand with pebble
80-255 ft
Sand with minor
pebble
Source: Schwartz et al. 1991, Johannessen, MacLennan and McBride 2005, and Washington State DNR 200 i.
Puget Sound West
West
75-100 ft
The following section characterizes the physical conditions within each ofthe Federal Way shore
reaches.
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City of Federal Way Draft Shoreline Inventory & Characterization
puget Sound East
Sediment transport in the Puget Sound East reach is southwestward from the eastern boundary of
the City limits and terminates at the southwestern corner of Dumas Bay. The northern orientation
of the shoreline precludes exposure to predominant southerly wind and wave conditions and
results in larger northerly wind waves driving net littoral sediment transport (net shore-drift;
Schwartz et al. 1991). This shore is exposed to the greatest amount of fetch and/or wave energy
throughout the study area.
This reach is characterized by high banks with varying levels of residential development (west of
Redondo Beach), which lower to low bank south of Poverty Bay Park. Twenty-eIght percent of
the Puget Sound East shore is modified. Modified shores diminish in abundance in the
southwestern portion of the reach. Modifications observed in the reach include bulkheads,
riprap, and overwater structures.
Feeder bluffs account for approximately 38 percent ofPuget Sound East shore length
(Johannessen et il. 2005). These sediment sources are predominantly found in the central portion
of the reach, likely due to th~ less modified state ofthe shoreline, enabling natural geomorphic
processes to persist. Recent landslides were mapped along 5.9 percent, and recent toe erosion
was active along 25.5 percent of the reach.
Geomorphic processes in this reach have been substantially altered by shoreline modifications. A
recent study by Johannessen et al. (2005) shows that shoreline modifications have reduced the
sediment sources in this shore reach by 23 percent oftheir historic prevalence.
Accretion shoreforms account for 21.8 percent of Puget Sound East. Each of these accretionary
landforms is associated with a stream mouth or freshwater source (culverts). However, each has
modifications that precluded the formation of subestuarine conditions. Beach sediment at these
sites is sand with moderate pebble. The remaining shores within this reach are mapped as
transport zones, neither substantially accreting nor eroding.
A typical beach profile in the Puget Sound East marine reach is composed of a mixed conifer and
deciduous riparian buffer atop 80- to 100- foot-high, steep coastal bluffs. These bluffs are
composed ofVashon advance outwash deposits and have a history of sliding. As a result, the
base of the bluff is commonly armored with riprap. Upper beach sediment is predominantly sand
with pebble, but at lower elevations clast size increases to pebble dominant. The beach is narrow,
indicative ofthe erosive nature of these shores. Waterward of the beachface is a sandy low-tide
terrace.
Dumas Bay
Drift cells KI-9-2 and KI-lO-l converge in the southwest corner of Dumas Bay. The eastern
portion of this marine reach encompasses the last mile (approximately) ofKI-9-2, which
originates just south of Saltwater State Park near the City of Des Moines. The western portion of
the reach includes the entire drift cell KI -10-1. This O.3-mile cell exhibits southeastward drift and
terminates at a recurved spit just northwest of the prograded beach in Dumas Bay. .
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City of Federal Way Draft Shoreline Inventory & Characterization
The Dumas Bay reach is characterized by low to moderately high bank shores, with dense
residential development, and abundant modifications. Higher bluffs are found in the western
portion of the reach in cell KI-lO-2. The beaches are wider and generally of more accretionary
character relative to the other reaches, due to the drift cell convergence, multiple stream deltas
and the protection afforded by the rounded headland on the west shore of the bay and by Maury
Island to the north. Over two-thirds ofthe reach is modified with bulkheads or riprap. The
eastern portion of the reach is near contiguously modified with several relict boat ramps and
boathouse footings in the intertidal. Several ofthe beaches mapped as accretionary were also
modified in the upper beach or backshore.
Feeder bluffs account for only 5.9 percent of this shore reach (Johannessen et al. 2005). These
remaining sediment sources are exclusively found northeast of Joe's Creek (stream delta in the
southeast comer of Dumas Bay), as, well as on the southwest side of Lakota and Joe's Creeks.
Toe erosion is mapped along4.8 percent of the reach. Toe erosion is also mapped on the
southwest side of both creeks. Only one landslide is mapped in Dumas Bay, which accounted for
0.6 percent of the reach.
Accretion shoreforms currently account for 18.2 percent of Dumas Bay, several of which are
associated with a stream mouth. Fluvial-derived sediment contributes to accretionary condition
of the beach. Broad sand flats and extensive backshores with driftwood and dune vegetation
characterize these areas.
A typical beach profile in this reach consists of a 3- to 5-foot-high bank, residentiai dwelling
with a bulkheaded backshore. An absence of back shore (storm berm and dune) habitats and
marine riparian is a direct result of the density of residential development and a bulkheaded
shore. Beach material is a mix of sand with moderate pebble. A broad sand flat extends below
the high-tide beach.
puget Sound West
This reach originates at a drift zone divergence between cells KI-l 0-2 and KI-l 0-3 located at the
headland on the west shore of Dumas Bay. KI-I0-3 exhibits westWard drift from the divergence
zone to the drift cell terminus at Dash Point in Pierce County.
Puget Sound West is characterized by 80- to 200-foot-high, slowly receding (apparently through
slumping) high bluffs with abundant large woody debris recruitment. Much of the Puget Sound
West shoreline is encompassed within Dumas Bay City Park and Dash Point State Park. Areas
, not within the parks are easily identifiable due to residential development on top or at the base of
the bluffs. Modifications are typically residential bulkheads constructed at the base of bluffs
between the two parks. This is the only contiguously bulkheaded area in the reach and represents
25.3 percent of its length. Another very short shore modification is located at the western end of
the study area.
Feeder bluffs are mapped throughout much ofthis shore reach, representing 60.9 percent of the
segment (Johannessen et al. 2005). Thirteen recent landslide areas are mapped, most of which
are located along the high bluffs ofthe headland west of Dumas Bay and surrounding Dash Point
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City of Federal Way Draft Shoreline Inventory & Characterization
State Park. In total, landslides are mapped along 44.6 percent ofthis reach. Recent toe erosion is
also frequently observed, accounting for 49.7 percent of the reach. '
Few transport zones are mapped in this reach, accounting for only 6.4 percent of the reach.
Accretion shoreforms are, also relatively infrequent. These are exclusively found in the western
portion of the reach, adjacent to the mini-estuary in Dash Point State Park. Most of this accretion
shoreform is unmodified; however, the stream channel is heavily riprapped.
Geomorphic processes in this reach have been substantially altered by shoreline modifications. A
recent study by Johannessen et aJ. (2005) shows that prior to modifications sediment sources
accounted for 84.6 percent ofthe reach. This indicates that shoreline modifications has resulted
in a 2~.7 percent (2,066 feet) loss of the available sediment sources in the reach.
A typical cross section of the Puget Sound West reach includes a mixed conifer and deciduous
forested bluff with slumps and jack strawed trees hanging over the intertidal area. Toe erosion
has scoured beneath some trees, leaving them growing over the intertidal area while still attached
to the toe ofthe bluff. Drift logs are caught and accumulate in these trees. Beach material is
almost exclusively sand with minor amounts of pebble. The low-tide beach includes a broad sand
fl& .
4.1.2 Geological Hazards and Shoreline Slope Stability
4.1.2.1 Seismic Hazard Areas
Seismic hazard areas are defined in Chapter 18-28 of the Federal Way Municipal Code (FWMC)
as those areas subject to earthquake damage as a result of seismically-induced ground shaking,
slope failure, settlement or soil liquefaction, or surface faulting. These conditions commonly
occur in areas underlain by cohesion less soils oflow density, usually in association with a
shallow groundwater table. No seismic hazard areas are identified within the shoreline
jurisdiction in the King County Sensitive Areas Map Folio (King County, 1990) or on the
county's interactive map site (iMAP) (accessed on 5/16/06 at
http://www.metrokc.gov/gis/mapportalliMAP_main.htm). However, maps produced by the
Washington Department of Natural Resources indicate areas of low to moderate liquefaction
susceptibility in all shoreline segments (Palmer et aI., 2003).
4.1.2.2 Landslide Hazard Areas
Landslide hazard areas are defined in Chapter 18-28 ofFWMC as those areas potentially subject
to episodic downslope movement of a mass of soil or rock. They are defined as: (1) any area
having a combination of slopes greater than 15 percent, permeable soils overlying impermeable
soils, and springs or groundwater seepage, (2) any area showing movement during the last
10,000 years, (3) any potentially unstable area as a result ofstrearri incision or wave erosion, (4)
any area located in a ravine or on an alluvial fan that may be inundated by flooding or debris
flows, (5) any area identified by the Natural Resources Conservation Service as having a severe
limitation for building site development, (6) any area mapped as unstable by the Department of
Ecology, or (7) slopes having gradients greater than 80 percent.
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City of Federal Way Draft Shoreline Inventory & Characterization
Landslide hazard area information for the City's shorelirte jurisdiction is shown on Figures 9-A
through 9-e. Designated landslide hazard areas include the majority of the shore bluffs in all of
the shoreline segments. As much as 77 percent ofthe shoreline Reach 1 C is considered to be a
landslide area, while 47 and 38 percent of Reaches lA and 1B, respectively, are considered to be
landslide hazard areas. The extent of designated landslide hazard areas may not correspond
exactly with the mapped extent of mass wasting deposits, as shown on Figure 4, or with the slope
stability and landslide area designations indicated in the Coastal Zone Atlas.
4.1.2.3 Erosion Hazard Areas
Erosion hazard areas are defined in Chapter 18-28 ofFWMC as those areas having severe to
very severe erosion hazard because of natural agents such as wind, rain, splash, frost action or
, stream flow. Such areas designated on City GIS maps and King County GIS maps (accessed on
5/16/06 at http://www.metrokc.gov/gis/mapportal/iMAP_main.htm) include all coastal bluffs and
steep slopes within th~ jurisdiction, which includes all shoreline segments. Approximately 65 to
70 percent of the shoreline segments are considered erosion hazard areas. These areas are shown
on Figures 9-A through 9-C.
4.1.2.4 Steep Slopes
Steep slope hazard areas are defined in Chapter 18-28 ofFWMC as those areas with a slope of
40 percent or greater and with a vertical relief of 10 or more feet, a vertical rise of 10 feet or
more for every 25 feet of horizontal distance. According to City GIS maps King County GIS
maps (accessed on 5/16/06 at http://www.metrokc.gov/gis/mapportal/iMAP_main.htm). the
shoreline bluffs in all segments ofthe jurisdiction qualify as steep slopes, as shown on Figures 9-
A through 9-C. '
4.1.2.5 Shoreline Slope Stability
The Department of Ecology Coastal Zone Atlas (Ecology, 1979) characterizes the slope stability
ofthe entire shoreline along Puget Sound. Although the City does not regulate shoreline
development based on slope stability characterization, the maps provide an additional
characterization of slope stability and a source of documented landslides. This mapping should
not be considered comprehensive and does not include landslides that have occurred, since the
late 1970s. '
In the Coastal Zone Atlas, slope stability is defined in terms of six separate categories: stable,
intermediate, unstable, unstable recent landslide, unstable old landslide, and modified. Table 5
describes these slope stability categories.
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City of Federal Way Draft Shoreline Inventory & Characterization
Definition
Stable
Generally rise less than 15 percent in grade, except in areas oflow groundwater
concentration or competent bedrock. Include rolling uplands and lowlands
underlain by stable material (Le., unweathered till and/or peat deposits) with no
significant slope.
Generally steeper than 15 percent except in areas where weaker material and/or
abundant material exist. These areas include slopes of sand and gravel, till, or
thin soils over bedrock with no known failures.
Slopes that are considered unstable due to geology, groundwater, slope, and/or
erosional factors which include areas of landslide and talus too small or obscure
to be mapped.
Recent or historically active landslide areas (based on surveys conducted in the
late 1970s). '
Post-glacial but prehistoric landslide areas.
Slopes that are highly modified by human activity and include areas of
significant excavation or filling. Response ofthe slope to a combination of
human activity and natural processes may be unpredictable.
Intermediate
Unstable
Unstable Recent Landslide
Unstable Old Landslide
Modified
Slopes classified as unstable are present in all segments of the shoreline jurisdiction according to
the Department of Ecology Coastal Zone Atlas (Ecology, 1979). Slopes within Reach lA are
generally designated in the Coastal Zone Atlas as unstable, unstable recent landslide, unstable
old landslide, and intermediate. Along the shoreline of Dumas Bay, Reach lB, slopes are
designated unstable, unstable 'old landslide, and intermediate. Shorelines within Reach 1 Care
characterized by unstable old landslide, intermediate, and stable.
4.1.3 Aquifer Recharge Areas
Critical aquifer recharge areas are defined in WAC 365-190-030 as "areas in which water
reaches the zone of saturation by surface infiltration. These areas are hydrogeologically
susceptible to contamination and contamination loading potential including but not limited to
such areas as sole water source aquifer recharge areas, special protection groundwater
management areas, wellhead protection areas, and other areas with a critical recharging effect on
aquifers used for potable water." Chapter 22, Article XIV, Division 9 of the Federal Way City
Code, "Critical Aquifer Recharge Areas and Wellhead Protection Areas," apply to any
development activity, or division of land which requires review under FWCC Chapter 18,
"Environmental Protection." The Lakehaven Utility District has mapped generalized aquifer
recharge areas. There are three major aquifers in the City and its P AA, but only one intersects
any shoreline planning areas. The RedondolMilton Channel Aquifer overlaps portions of reach
lA, lB, and 1 C. This area is managed as A Critical Aquifer Recharge Area. The City has
mapped wellhead protection zones within the city limits and the P AA. The majority of the
wellhead protection areas do not coincide with the shoreline reaches. Wellhead protection areas
are mapped adjacent to the east side of North Lake and adjacent to the east side of Lake
Killarney, extending to Lake Geneva. These areas are managed as Wellhead Protection Areas
(Federal Way City Code (FWCC), Chapter 22).
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City of Federal Way Draft Shoreline Inventory & Characterization
4.1.4 Flood Hazard Areas
Flood hazard areas are typically identified on the Federal Emergency Management Agency
(FEMA) flood insurance rate maps as the 100-year floodplain. All coastal beaches within the
City's jurisdiction are included within the 100-year floodplain (King County, 2002, from FEMA
FIRM mapping). Coastal floodplain hazard areas are typically associated with storm waves.
4.1.5 Streams
Streams are defined in the FWCC Chapter 22 Article I Section 22-1 and are classified as "Major"
or "Minor" streams. Major streams include any stream or tributary that contains or supports, or
which under normal circumstances contains or supports resident or migratory fish. Minor
streams are those typically smaller streams that do no meet t~e definition of a "major" stream.
Streams within. the City of Federal Way have been evaluated and classified in a citywide
inventory conducted in 2001 (URS). Streams provide valuabie wildlife corridors, a source of
fluvial sediments to the marine shoreline (moved along the shoreline by currents), and support a
range offish species. The City of Federal Way is located in Water Resource Inventory Area
(WRIA) 9, the Duwamish-Green River and Central Puget Sound Watershed. Information on
stream conditions was drawn in particular from the following documents: Habitat Limiting
Factors and ReconnaissanceAssessment Report, Green/Duwamish and Central Puget Sound
, Watersheds (WRIA 9 and Vashon Island) (Ker:win and Nelson, 2000), and A Catalog of
Washington Streams and Salmon Utilization - Volume I, Puget Sound Region (Williams et al."
1975). ' '
Several streams have been identified in Federal Way that flow directly into Puget Sound and are
part of the Lower Puget Sound basin. The streams discussed below are shown in Figure 6.
puget Sound East
Four short unnamed streams enter the coastal shoreline in Reach lA. These streams have steep
gradients and are associated with landslide and erosion hazard zones. The city stream inventory
considers these streams as Major streams.
Dumas Bay
Three streams drain to the shoreline within the Dumas Bay area, or Reach IB; these include
Joe's Creek, Lakota Creek and an unnamed tributary to the Sound (Dumas Bay Creek). Joe's
Creek and Lakota Creek are Major streams and Dumas Bay Creek is considered a Minor stream.
Joe's Creek originates in the uplands of Federal Way, flowing through Olympic View Park and
the Twin Lakes Golf Course, then drops into a high-gradient stream channel that falls through a
wooded ravine, eventually flattening immediately prior to entering Puget Sound on the east side
of Dumas' Bay. The substrate within the creek consists of pebbles and cobble-sized particles
with localized sand depositions. Gravel deposits are very local and spawning opportunities are
typically few. These features are typical of flow alterations caused by undetained stormwater
(King County, 2000). Joe's Creek appears on the 2004 Department of Ecology 303(d) list for
fecal coliform.
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City of Federal Way Draft Shoreline Inventory & Characterization
Lakota Creek flows in a northwesterly direction, passing thorough the Lakehaven Sewage and
Wastewater Treatment Plant before entering Puget Sound at Dumas Bay (Reach IB). The lower
reach of the stream was relocated as part of an upgrade to the sewage treatment plant in 1987.
The creek generally flows through residential areas and alongside roads. The riparian habitat in
the lower reaches consists of small deciduous trees with a shrub understory. The lower mile of
creek supports dense stands of conifers within a moderate..; to high-gradient ravine. Substrate
within Lakota Creek is generally the same as that in Joe's Creek. It was on the 1998 303(d) list
for fecal coliform (King County, 2000), but is not Iisted,on the 2004 303(d) list.
Puget Sound West
One unnamed creek (referred to in the WRIA as No.. 0391)flows through a steep ravine into
Puget Sound at Dash Point State Park in Reach 1 C. Clay bluffs border the beach in many places.
Mud slides have become more frequent in the stream with increasing development (KCDNR,
1998). From aerial photography (2002), riparian buffer vegetation appears to be largely intact in
the upper reaches within Dash Point State Park, but less so from the parking lot down to the
creek mouth. The creek banks are armored from the mouth up to the road bridge, 200 feet
upstream (WRIA 9, 2005).
4.2 Biological Resources
Biological resources described in the coastal shorelines encompass wetlands, critical wildlife
habitat and species, marine riparian habitats, marine intertidal habitats, and priority species.
4.2.1 Wetlands
Wetlands near the Puget Sound shoreline typically include tidal marshes and tidally influenced
estuaries. Tidal marshes include salt and freshwater habitats that experience tidal inundation,
(KCDNR, 2001). Several wetlands have been mapped by various sources in the City's'coastal
shoreline jurisdiction. According to the 1987 National Wetlands Inventory (NWI), the entire area
of the City's shoreline jurisdiction in the City limits is designated as Estuarine Intertidal
Unconsolidated Shore wetland or Estuarine Intertidal Aquatic Bed and Unconsolidated Shore
wetland (USDI, 1987a and 1987b). In addition, one larger freshwater wetland is mapped at
Dumas Bay as a Palustrine Emergent Scrub/Shrub wetland. The King County Sensitive Areas
Map Folio (King County, 1990) does not identify any wetlands within the City's marine
shoreline jurisdiction. '
The City Wetland Inventory (City of Federal Way, 1998) identifies the freshwater wetland at
Dumas Bay as a Class I wetland (FWMC 18-28). However, it does not include the estuarine
wetlands identified in the NWI within the City's marine shoreline jurisdiction. Although
, mapp~d as wetlands at the national level on the NWI maps, the intertidal areas are likely not
sufficiently vegetated to meet the ,definition of wetland at the state or local level. Additional
marine shoreline jurisdiction wetlands are identified in the City's Wetland Inventory northeast of
Dumas Bay near the intersection of Southwest 300th Place and 30th A venue Southwest and two
within the conservancy area north of Southwest 295th Street between 9th and 1 Oth Avenues
Southwest. All of these wetlands are less than 1 acre in size and are identified as Class III
(FWMC 18-28).
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ply of Federal Way Draft Shoreline Inventory & Characterization
Parks and open spaces including Dash Point State Park, Poverty Bay Park, and Dumas Bay Park
create significant breaks in residential development along the City's marine shoreline. Of the
roughly 25,000 feet of marine shoreline within the City's jurisdiction, approximately 40 percent
is armored. The majority ofthe unarmored shoreline is within the park and open space
conservation areas, with some of the developed private shoreline also without armoring.
Development and armoring along marine shoreline reaches within the City's jurisdiction have
eliminated historical wetlands and prevent connections between interior wetlands and the
nearshore area.
4.2.2 Critical Wildlife Habitat and Species
Critical fish and wildlife habitat areas are those areas identified as being of critical importance in
the maintenance and preservation of fish, wildlife and natural vegetation. Critical fish and
wildlife habitat areas are defined in Chapter 18.28 (FWMC) as follows:
Fish and wildlife habitat conservation area shall mean the management of land'
for maintaining spe'Cies in suitable habitats within their natural geographic'
distribution so that isolated subpopulations are not created. Habitat
conservation areas include but are not limited to such areas as: areas with
which endangered, threatened, and sensitive species have a primary
,association; habitats and species of local importance; commercial and
recreational shellfish areas; kelp and eelgrass beds; herring and smelt
spawning areas; naturally occurring ponds under 20 acres andtheir
submerged aquatic beds that provide fish or wildlife habitat; waters of the
state; lakes, ponds and streams planted with game fish by a governmental or
tribal entity; state natural area preserves and natural resource conservation
areas; and streams.
Mapped critical fish and wildlife habitats are shown on Figure 10. Critical fish and wildlife
habitats in the City's marine shoreline planning area are characterized throughout the following
sections describing the shoreline and nearshore biological areas.
4.2.3 Marine Riparian Habitats
Riparian areas are transitional zones between terrestrial and aquatic ecosystems. Riparian
habitats include those portions of terrestrial ecosystems that significantly influence exchanges of
energy and matter with aquatic ecosystems (Brennan and Culverwell, 2004). Marine riparian
vegetation is defined as vegetation overhanging the intertidal zone (KCDNR, 2001). Marine
riparian zones function by protecting water quality; providing wildlife habitat; regulating
microclimate; providing shade, nutrient and sources of food; stabilizing banks; and providing
large woody debris (Anchor Environmental and People for Puget Sound, 2002).
Marine riparian zones were examined through limited field reconnaissance and review of 200 1
oblique aerial photos (Ecology, 2002). Marine riparian vegetation within the City's shoreline
planning area was mapped in the WRIA 9 Marine Shoreline Inventory Report (Anchor, 2004).
August 2006
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City of Federal Way Draft Shoreline Inventory & Characterization
Puget Sound East
Riparian vegetation in Reach lA is mixed trees and grasses. Much of Reach lA is armored with
concrete and wooden bulkheads, and riprap seawalls. L WD or drift log accumulations have been
mapped along unarmored portions of Reach lA.
Dumas Bay
Riparian vegetation within the Dumas Bay reach, Reach IB, is dominated by grasses, although
trees are found along the high bluffs to the west of Dumas Bay, as well as in the reach between
Joe's Creek and Lakota Creek. The shoreline is armored for approximately 600 feet east of
Dumas Bay Park, as well as east of Lakota Creek to Poverty Bay Park for the protection of
homes along the toe of the bluff. L WD is lacking along most of this shoreline segment, though
drift log accumulations have been mapped along the beach at Dumas Bay Park.
Puget Sound West
Trees dominate the riparian vegetation in Reach 1 C, particularly along Dash Point State Park and
the high, steep bluffs along this segment. Shoreline armoring is limited to the center ofthis
reach, along the rural segment. This armored section is generally lacking in L WD and drift logs,
although L WD is available along much of the rest of the shoreline segment.
Shoreline activities that may negatively affect marine riparian areas (Brennan and Culverwell,
2004) include: '
· Fecal and chemical contamination from failing septic systems, lawn chemicals, and
stormwater;
· Loss of vegetation from shoreline armoring, clearing and grading activities, or tree
removal for view corridors; and
· Wildlife habitat infringement due to increased ambient light levels at night, fragmentation
from road crossings, noise from human activity, and domestic pets.
4.2.4 Marine Intertidal Habitats
Marine intertidal habitats include flats, subestuaries, eelgrass beds, and, kelp forests. These areas
are considered "special aquatic sites, "which are special habitats in the intertidal zone that
generally do not meet the definition of wetland. Flats generally include gently sloping (less than
50 slope) sandy or muddy intertidal or shallow subtidal areas (KCDNR, 2001), and are used by
juvenile salmonids, shorebirds, and shellfish, among other species. Flats are generally located at
the mouths of streams where sediment transported downstream is deposited, and in areas of low
wave and current energy where longshore waves and currents deposit sediment (KCDNR, 2001).
All of the flats in WRIA 9 were mapped around Vashon and Maury Island; however, there are
tidal flats in WRIA 9 that were not captured during the WDNR mapping effort. Sand and gravel
flats are located near the mouth of Unnamed Creek (#0391) that enters Puget Sound through
Dash Point State Park (Reach Ie), and Dumas Bay (Reach lB).
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City of Federal Way Draft Shoreline Inventory & Characterization
Shoreline activities that may impact tidal flats (KCDNR, 2001) include:
. Unnatural erosion or deposition of sediment;
. Harvesting of shellfish and other marine life;
. Fecal and chemical contamination from on-site septic systems, lawn chemicals, and
stormwater;
. Physical disturbances from shoreline armoring, marina construction, and upland
development practices;
. Shading from ()verwater structures; and
. Loss of emergent and riparian vegetation.
Subestuaries are those areas of river and stream mouths that experience tidal inundation,
including their deltas and any associated marshes (KCDNR, 2001). Subestuaries form where the
stream or river broadens and fresh and saltwater mix. Subestuaries function to attenuate flooding,
provide juvenile salmonid feeding and rearing habitat, act as a transition area for migrating adult
salmonids, support eelgrass beds (depending on salinity), and provide refuge, feeding, and
production areas to a wide variety of birds, fish, mammals, and invertebrates (KCDNR, 2001).
Subestuaries, especially those rich in organic matter, can support numerous and diverse marine
and estuarine invertebrates such as polychaete worms and amphipods. These organisms near the
base of the food web can be key to overall ecosystem productivity and habitat value for fish,
birds, and mammals. Subestuaries occur in marine shoreline Reaches IB and lC, and are
associated with the stream mouths of Unnamed Creek (#0391), Joe's Creek, and Lakota Creek.
Deltas are formed by downstream sediment transport. The growth of deltas and quality of habitat
provided by thesubestuaries is influenced by annual rainfall and the rate at which sediment is
transported and deposited at the mouths of streams. High peak flows that occur as a result of
increased impervious surface within the stream basin likely transport sediment further out into
Puget Sound where depths are greater, resulting in sediment accumulation beyond the stream
mouth.
Shoreline activities that may affect subestuaries include:
. Physical disturbances from shoreline armoring;
. Physical disturbances from dredging and filling;
. Changes in hydrology due to increased impervious surface within stream basins; and
. Nonpoint pollutant runoff from impervious surfaces and residential lawns near the
shoreline.
The importance of eelgrass has been described in various sources, including the Reconnaissance
Assessment of the State of the Nearshore Environment (KCDNR, 2001). Eelgrass beds are found
,in shallow subtidal areas and provide feeding and rearing habitat for a large number of marine
organisms. Eelgrass beds have been documented within the City's shoreline jurisdiction in all
marine shoreline segments. Continuous eelgrass distribution can be found along the north end of
Dash Point State Park and Palisades Park, as well as from the north end of Dumas Bay to 3rd
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City of Federal Way Draft Shoreline Inventory & Characterization
Avenue Southwest; eelgrass distribution along the remainder of the City's marine shoreline is
classified as patchy (WDNR, 2001). Shoreline activities that may impact eelgrass (KCDNR,
2001) include:
· Clam harvesting;
· Propeller scour and wash;
· Physical disturbances from shoreline armoring;
· Shading from overwater structures; and
· Physical disturbances from dredging and filling.
The function of kelp has been described in Reconnaissance Assessment of the State of the
Nearshore Environment (KCDNR, 2001). Kelp provides habitat for many fish species, including
rockfish and salmon ids, potential spawning substrate for herring, and buffers to shoreline from
waves and currents, among other functions. Kelp distribution is largely dependent upon the type
of substrate, generally attaching to rocky substrates. In areas where there is a coarsening of
substrate.in- the low intertidal and shallow sl.lbtidal zones, there is a more likely occurrence of
kelp. A change in kelp distribution may indicate the coarsening of shallow subtidal sediments
(such as that caused by erosion related to a seawall) or an increase in nutrient loading (such as
from sewage effluent). Kelp forests are not currently mapped within the City of Federal Way
shoreline planning area. Kelp was previously reported as occurring within all reaches of WRIA
9, which would include the Federal Way shoreline (KCDNR, 2001). KCDNR also noted data
gaps in general knowledge of kelp and its biology, its role in nearshore ecological processes, lack
of historical or recent studies, and lack of distribution data.
Shoreline activities that may impact kelp densities (KCDNR, 2001) include:
· Physical disturbances from shoreline armoring, marina construction, and harvesting;
· Shading from overwater structures;
· Beach nourishment; and
· Nutrient loading.
4.2.5 Priority Habitat and Species
The Washington Department ofFish and Wildlife (WDFW) maintains priority habitat and
species information for Washington State, including the status of species as threatened or
endangered. The City of Federal Way occurs within the WDFW Region 4. Priority habitats
within Region 4 include consolidated marine/estuarine shorelines, cliffs, caves, snags, riparian
areas, old-growth/mature forests~ and urban open spaces. The following sections discuss some of
the priority species and species of local importance that occur within the City's shoreline
planning area.
4.2..5.1 Shellfish
Geoduck clams (Panopea gene rosa) are documented in subtidal areas adjacent to shoreline in a
, small portion of Reach lA, as well as all ofReacheslB and lC, southwest of Poverty Bay Park
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City of Federal Way Draft Shoreline Inventory & Characterization
and extending beyond the City limits (Figure 10). The tract was last surveyed in 1971, as
reported in Sizemore and Ulrich (2000). At the time ofthe 1971 survey, densities within the
tract and other geoduck tracts along the WRIA 9 mainland area were shown to be amongst the
highest in Puget Sound (approximately 4 to 7 per square meter). The tracts, however, were also
reported as "polluted or possibly polluted" (Sizemore and Ulrich, 2000).
In general, shellfish populations are relatively low in all shoreline reaches. Population data from
a series of shoreline surveys along the southern extent ofWRlA 9 (south ofMee Kwa Mooks
Park of Seattle to Dash Point State Park) were analyzed by KCDNR (2001), and are presented in
Table 6. It should be noted that there is a: data gap concerning the collection of population data,
and this relates primarily to the differences in sampling methodology and lack of recent'
quantitative population studies within WRlA 9.
Table 6. ShelIfish Population Densities in Southern WRIA 9
€ommon Name Scientific Nam,e ROPIJ'1lti.9P density, (IJPm~eJt J>~r,
S.q)jil,re meter)
Butter clam Saxidomus giganteus <10
Native littleneck clam Protothaca staminea 6-17
Manila clam Tapes philippinarum :::;10
Geoduck Panopea generosa 1-2
Dungeness crab Cancer magister N/A; decreases as you move south from
Seattle
Olympic oyster Ostrea lurida 0
Northern abalone Ha/iotis kamtschatkana 0
No portion of the City's shoreline is currently used for commercial shellfish harvest. In July
2004 the Washington State Department of Health closed all of the Puget Sound shoreline in King
County, including Dash Point State Park, Dumas Bay Park and Poverty Bay Park, to recreational
shellfish harvesting for all species due to pollution advisory and the presence ofbiotoxins in
particular shellfish species. The Department of Health conducts an ongoing assessment of
pollution and conditions related to shellfish harvesting. The latest update was in March 2006,
which maintained the closure of mainland King County beaches to recreational shellfish
harvesting (Washington Department of Health, 2006).
4.2.5.2 Salmonids
The WDFW SalmonScape database (WDFW, 2006), PHS Data, as well as A Catalog of
Washington Streams and Salmon Utilization - Volume I, Puget Sound Region (Williams et aI., ,
1975), identify the known presence of salmon in local streams. Two creeks in ReachlB have
documented presence of PHS fish, Joe's Creek and Lakota Creek. Joe's Creek contains.
documented coho salmon and Chum. Lakota Creek has documented use by coho and chum
salmon.
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City of Federal Way Draft Shoreline Inventory & Characterization
Nearshore habitat is an important environment for juvenile salmon ids, where the shallow water
depth obstructs the presence of larger predator species (Kerwin and Nelson, 2000). All shoreline
segments within the City's shoreline jurisdiction are known or expected to contain juvenile
salmonids including bull trout, cutthroat, Chinook, chum, coho, pink, and sockeye salmon based
in the knowledge of species life histories (KCDNR, 2001).
Critical Habitat, as defined by the Endangered Species Act,. "is the specific areas within the
geographical area occupied by a species.. .on which are found those physical or biological
features essential to the conservation of the species and that may require special Jllanagement
considerations or protection"; and "specific areas outside the geographical area occupied by a
species at the time it is listed... that are essential for the conservation of the species." Critical
Habitat has been designated for Pacific salmon and steelhead in Washington, Oregon, and Idaho,
including the Puget Sound Evolutionarily Significant Unit (ESU) Chinook salmon. Areas within
Federal Way that are included as Chinook Critical Habitat include West Hylebos Creek, and
estuarine, and nearshore marine areas to a depth of 30 meters relative to Mean Lower Low Water
(MLL W) (Federal Register, 2005a). Critical Habitat has also been designated for bull trout,
which may be present in the nearshore areas of Federal Way. Designated Critical Habitat for
, bull trout includes marine waters to a depth of 33 feet (10 meters) relative to MLL W (Federal
Register,2005b).
, Nearshore modifications affect salmoI)id habitat (Redman et aI., 2005) in the following ways:
. Loss and/or simplification of deltas and delta wetlands, which provide forage and rearing
habitat for salmonids;
. Alteration of flows through major rivers;
. Modification of shorelines by armoring, overwater structures and loss of riparian
vegetation;
. Contamination of nearshore and marine resources;
. Alteration of biological populations and communities;
. Transformation of land cover and hydrologic function of small marine surface water
discharges via urbanization; and
. Transformation of habitat types and features via colonization by invasive plants.
These nearshore modifications can adversely affect salmonid habitat by reducing forage and
rearing habitat for young fish, changing flow dynamics in rivers and altering in-stream habitat,
reducing water quality, creating blockages for fish passage, and altering the food supply upon
which salmon ids depend.
4.2.5.3 Forage Fish
Forage fish include species that as adults breed prolifically and are small enough to be prey for
larger species. They are often nnn-game fish. The three forage fish species most likely to occur
in the City's' shoreline jurisdiction include surf smelt, sand lance, and Pacific herring (Figure 10).
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City of Federal Way Draft Shoreline Inventory & Characterization
Different species utilize different parts of the intertidal and subtidal zones, with sand lance and
surf smelt spawning primarily in the substrate of the upper intertidal zone, and Pacific herring
spawning primarily on intertidal or subtidal vegetation (Lemberg et aI., 1997). Information on
the five potential forage fish species within the City marine shoreline is summarized in Table 7.
Table 7. Forage Fish Species
Pacific
herring
None (nearest is
Quartermaster
Harbor on Vashon
1.)
Sand lance
Yes, WDFW PHS
Eulachon
None
Longfin
smelt
None
Surf smelt
Yes, WDFWPHS
Quartermaster Harbor
stock spawn January
through mid-April
November 1 to February
15 '
, Late winter/early spring
Winter
South Puget Sound stocks
are fall-winter spawners
(September to March)
Sources: (O'Toole, 1995; KCDNR, 2001; Lemberg et aI., 1997)
"', ,.;,"':..":T;':'- :~.::: "".,,, ..',". ' ~,"~;
: .~,ret~n:~d' :',' ; ,
; Sp'a~~j~g ,
, Sub~,trat~. ; ,
Eelgrass
Fine sand, mixed
sand and gravel, or
gravel up to 3cm
Unknown
Sand with aquatic
vegetation
Mix of coarse sand
, and fine gravel (1-
7mm)
Spawning Location
Upper high tide limits to
depths of 40 feet
(typically between 0 and -
10 tidal elevation)
From + 5 tidal elevation
to higher high water line
(from bays and inlets to
current-swept beaches)
Freshwater streams
Freshwater streams
Upper intertidal
Information on documented forage fish spawning activity was available from the WDFW PHS
data, (2004). No Pacific herring, eulachon, or longfin smelt spawning areas are currently
documented in the shoreline inventory area (WDFW, 2004). However, it is fair to assume that
they all utilize the nearshore areas for feeding and migration. WDFW (2004) and Kerwin and
Nelson (2000) document surf smelt spawning areas in a small stretch of Reach lA, adjacent to
Southwest 296th Street between 9th and 12th Avenues Southwest and in a segment of Reach 1 C
and from the western edge of Dash Point State Park to beyond the City's western shoreline
boundary. A sand lance spawning area is mapped from just inside the eastern boundary of the
City (Reach lA) and continuing northeast across the mouth of Redondo Creek (Kerwin and
Nelson, 2000; WDFW, 2004).
Nearshore modifications affect forage fish habitat in the following ways:
. Development impacts the shoreline, particularly marinas and boat ramps, which bury
spawning habitat, introduce the potential for repeated disturbance, and potentially alter
nearshore hydrology; ,
. Sewer outfalls introduce pollutants and nutrients to the nearshore;
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City of Federal Way Draft Shoreline Inventory & Characterization
. Overwater structures shade intertidal vegetation and may alter nearshore hydrology;
. Riprap revetments and bulkheads impound sediment in bluffs such that fine-grained
spawning beach sediment is not replenished (ongoing net-shore drift decreases spawning
habitat); and
'. Riprap revetments and vertical bulkheads alter nearshore hydrology and may increase
wave energy on intertidal areas.
Sand lance and surf smelt spawn in the upper intertidal zone of protected sand-gravel beaches
throughout the increasingly populated Puget Sound basin, making these species vulnerable to the
cumulative effects of various types of shoreline development. "No net loss" regulations for
protection of known spawning sites offorage fish species are included in the Washington
Administrative Code Hydraulic Code Rules (WAC 220-110), which are applied during
permitting of in-water construction activities.
4.2.5.4 Marine Mammals
Seals, sea lions, whales, and dolphins may all be observed off the shores of Federal Way. Seals
and sea lions use specific shoreline areas, known as haul-outs, to haul-out ofthe water and rest,
dry out, interact and regulate body their temperature. In addition to resting, harbor seals give
birth to and nurse their pups at certain haul-out locations, and undergo an annual molt of their
, pelage or fur. Haul-outs can include beaches, rocky areas, log booms and floats. Some haul-outs
are used regularly, while others may be used seasonally or occasionally. No seal or sea lion haul- '
outs have been documented in Federal Way, although they have been documented on buoys,
floats, and logbooms in Commencement Bay and southeast of Maury Island (Jeffries et aI.,
2000).
Whales and dolphins known to regularly visit central Puget Sound include southern resident
killer whales, common dolphin, harbor porpoise, and Dall's porpoise. They do not typically use
the nearshore areas within City of Federal Way shoreline jurisdiction. Critical Habitat has been'
proposed for killer whales, including Puget Sound marine waters deeper than 20 feet (6.1 meters)
(Federal Register, 2006).
4.2.5.5 Shorebirds and Upland Birds
Adjacent to the open waters ofPuget Sound, the upland terrestrial environment provides habitat
for birds, amphibians, reptiles, and insects. A variety of shorebirds utilize the nearshore
environment for wintering and breeding. Seventy-five species of birds are associated with marine
nearshore environments in Washington (O'Neil et aI., 2001).
Great blue heron (Ardea herodias) and green heron (Butorides striatus) nesting colonies have
been identified in Reach IB (WDFW, 2006). Documented observation dates ofthese nesting
colonies range from 1980 to 2003 (WDFW, 2006). Bald eagle (Haliaeetus leucocephalus) nests
have also been documented in Reaches lA and lC (WOFW, 2004). A seabird colony outside of
the City's jurisdiction, associated with the northeast shore of Commencement Bay and the
Hylebos Waterway, as well as breeding purple martins (Progne subis) south ofthe City, may
utilize nearshore resources within Federal Way.
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City of Federal Way Draft Shoreline Inventory & Characterization
4.3 Land Use Patterns
The City of Federal Way is located in the southwestern comer of King County. Federal Way is
highly developed and has a well-established pattern of land use. Approximately 4.5 miles of
Puget Sound shoreline bound the City to the west, South 272nd Street to the north, the
King/Pierce County line to the south, and Interstate-5 (1-5) to the east. The Cities of Kent and
Des Moines borders Federal Way on the north, the Cities of Auburn, Algona, and Pacific to the
east, and the Cities of Milton and Tacoma to the south as well as portions of unincorporated
Pierce County. The City's nearshore shoreline jurisdiction is composed ofa variety of natural
and human-modified landscape features that include natural and modified beaches, concrete,
wood and rock bulkheads, and roads. These features are illustrated by the air photo depicting
current conditions on Figures ll-A through II-C.
4.3.1 Existing Land Use
The nearshore shoreline of Federal Way is predominantly developed as single-family residential,
interspersed with parks, open space, and multi-family developments. The City has a diversity of
housing types. The nearshore shorelirie areas are comprised of approximately 55 percent single-
family development, 18 percent parks, 14 percent open space, 1 0 percent vacant land, and 2
percent multi-family development. Existing land use categories per marine shoreline reach are
shown in Table 8. Existing land use categories are derived from King County Assessor codes,
compiled by parcel. Road right-of-way areas in the reaches are not included.
4.3.2 Comprehensive Plan
According to the City of Federal Way Comprehensive Plan Map (2002), the City's shoreIlne
jurisdiction is largely comprised of properties designated as low- to medium-density residential
(1 to 4.5 dwelling units per acre). Parks, Open Space and Public FacilitieslUtilities designations
comprise the second largest portion of the shoreline. Small areas designated as commercial,
office and multi-family comprise the remainder.
General goals and policies established in the City ofFeqeral Way Comprehensive Plan (2002)
relate to the preservation of existing residential neighborhood character, protection of
environmental resources, and the promotion of economic development. The Comprehensive
Plan seeks to balance these social, environmental, and economic goals through land use and
zoning regulations, criti<:al areas regulations using best available science, and development
regulations. In relation to shorelines, the Comprehensive Plan seeks to preserve or develop
shorelines and adjacent areas in a manner that assures a balance of shoreline uses with minimal
adverse effect on the quality oflife, water, and environment (City of Federal Way, 2002).
The City's existing Shoreline Master Program goals and policies are included as an element in
the land use chapter ofthe City's current Comprehensive Plan. These goals and policies
encourage water-oriented uses and existing residential uses in balance with protection of the
Puget Sound shoreline's natural resources (City of Federal Way, 2002). This document also
establishes shoreline environment designations as Natural, Conservancy, Rural, or Urban
Environments, depending on the land use and intensity of development. In the coastal shoreline,
the existing shoreline environment designations are shown on Figures l2-A through l2-e.
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City of Federal Way Draft Shoreline Inventory & Characterization
4.3.3 Zoning Designations
Zoning designations in the City of Federal Way generally follow land use designations as
discussed above under Comprehensive Plan Designation. Within the City's nearshore shoreline
jurisdiction, zoning is exclusively residential single-family (Figures l2-A through l2-C). These
include residential 1 unit! 7,200 square feet (RS 7.2), residential 1 unit!9,600 square feet (RS
9.6), residentiall unit!15,000 square feet (RS 15.0), residentiall unit!35,000 square feet (RS
35.0), anQ residential 1 unit!
5 acres (SE).
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City of Federal Way Draft Shoreline Inventory & Characterization
Table 8. Land Use, Zonrng, and Shoreline Environments
Existing
Shoreline Shoreline
Reach Existing Land Use Zoning Designations
Multi Fam 0.70% Single Family 34.24% Urban
Single Family 63.37%
Open Space 34.20% Low Density Conservancy
Park 7.16% Rural
Right of Way 1.92%
Single Family Residential 62.51 %
lA Vacant 15.79%
Open Space 27.78% Single Family 26.21% Conservancy
Single Family 71.10%
ParI< 8.02% Low Density Rural
Right of Way 96.00% Natural
Single Family Residential 55.82%
Utilities 0.44%
1B Vacant 4.94%
Single Family
Multi Fam 6.04% Low Density 98.70% Conservancy
Open Space 1. 79% Rural
Park 38.18%
Right of Way 1.29%
Single Family Residential 44.65%
IC Vacant 8.04
4.3.4 Roads and Bridges
As described above the majority ofthe City's shoreline is occupied by low- to medium-density
single-family development. Public shoreline access is available at Dash Point State Park, Dumas
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City of Federal Way Draft Shoreline Inventory & Characterization
Bay Park, Dumas Bay Center, and Poverty Bay Park. Limited shoreline access and uniformity in
shoreline land use (single family) created a land use pattern with relatively few roads in the
City's shoreline. Most of the roads that provide access to the shoreline are located outside the
City's shoreline jurisdiction. The exceptions are a small portion of Southwest 300th Place in
shoreline environmental Reach 1 B, and Southwest 292nd Street, 2nd A venue Southwest, and
Southwest 291 st Street, in Reach 1 C. All streets in the City's shoreline are local streets.
However, one larger roadway influences the shoreline area by providing access, but is outside of
the City's,shoreline. Leading to Dumas,Bay Center, Dumas Bay Park, and Dash Point State
Park, is Southwest Dash Point Road, State Route 509 (located in Reach lB, Ie). King County
Metro, Sound Transit, and Pierce Transit provide transit services in the City of Federal Way.
The only transit route in the Federal Way nearshore shoreline vicinity is Metro's Route 175 that
provides service along Southwest Dash Point Road.
4.3.5 Wastewater and Stormwater Utilities
Lakehaven Utility District (District) provides sanitary sewer service within the City's boundaries
and to unincorporated areas to the east and north of the City (including all P AA regions except a
small area at the northeastern portion of the PAA area). The District operates and maintains 2
wastewater treatment facilities and a collection system consisting of 27 sewage pump stations,
approximately 275 miles of sanitary sewer pipe, and 6,400 manholes. The District's area is
divided into seven basins, the two largest of which (Redondo and Lakota) serve the majority of
the City. Wastewater from the Redondo and Lakota Basins is treated by the District's two
secondary wastewater treatment facilities, one of which is located near the Dumas Bay shoreline
planning area. The five remaining basins are relatively small, serving areas around the
perimeter of the two large basins on the south, north, and east. Wastewater from these basins is
conveyed to other utilities for treatment.
The City of Federal Way's Comprehensive Plan was last updated in 2002. At the time of
update, an estimated 7,500 on-site disposal systems were still in operation within the Lakehaven
Utility District's corporate boundaries. The plan indicates that the District will integrate the
remaining on-site disposal systems over time as they became unfeasible to maintain and/or
require sewer connection for redevelopment. Recommendations within the plan include the
expansion and upgrade of existing treatment and conveyance facilities, and installation of new
conveyance facilities to provide service to areas in the City and P AA that are currently using on-
site septic systems.
The City of Federal Way operates a stormwater management system. According to the City's
Comprehensive Plan (2002), the City has completed projects to create regional detention and
treatment facilities serving the City over the last decade. Localized storm water treatment is also
required for new developments. The 1994 Surface Water Facilities Plan (City of Federal Way,
1994) indicates that regional facilities have been designed with a 100-year flood storage
capacity. All other stormwater system elements have been designed to a 25-year flood storage
capacity. ' Chapter 16 of the Federal Way Municipal Code and the King County Surface Water
Design Manual establishe stormwater standards for new development.
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City of Federal Way Draft Shoreline Inventory & Characterization
Undetained and untreated stormwater runoff can deliver pollutants to waterbodies, 'including
heavy metals and other pollutants associated with automobiles and roadways. Water quality
impairments described in previous sections include the presence of mercury and other metals in
local streams, wetlands, and lakes. Untreated stormwater discharging to surface water bodies is
likely a contributing factor.
4.3.6 Other Utilities
According the City's Comprehensive Plan (2002) and the Lakehaven Utility District's
Comprehensive Water System Plan (1994), the District maintains decentralized water supply
production facilities that serve the majority of the City. The District operates 27 wells with the
water system connected by interties to the water supply of other utility districts. The system
allows the District to buy and sell water according to intra-District supply demands. Water
systems attached to the District through interties include the Highline Water District, Tacoma
Public Utilities, and the City of Milton's water supply system. These surrounding water supply
systems and other neighboring water suppliers provide portions ofthe City's water supply. The
City's PAA is partially within the District's water supply area and those of neighboring water
suppliers. In addition, the City of Tacoma, Fruitland Water District, and several private
landowners own production wells.
, , A variety of gas, telephone, electri~, and related utilities serves the existing residential and
commercial developments within the nearshore shoreline planning areas. '
4.3.7 Existing and Potential Public Access Sites
Approximately 31 per~ent of the City's shoreline is dedicated as parks or open space and is
available for public access and use. Figure 13 shows the locations of all the shoreline public
parks and open space within the City's shoreline. Existing parks; open space, and public
facilities in the City's shoreline planning area include the following:
. Dash Point State Park - This 398-acre state park is located on the westernmost point
of the Federal Way marine shoreline. The park provides access to 3,302 feet ofPuget
Sound marine shoreline. The park also contains two covered picnic shelters, 11 miles
of hiking and biking trails, amphitheater, and 138 camping sites, with a mix of
primitive tent sites and a serviced campground.
. Dumas Bay Park - This 19.3-acre neighborhood park is located along the City's
western Puget Sound shoreline, north of Dash Point State Park, off Dash Point Road.
The park offers,12 parking stalls and unpaved trails which lead to the beach front.
The park also contains interpretive signs.
. Dumas Bay Centre - Located on the north side of Dumas Bay, opposite Dumas Bay
Park, the Dumas Bay Center features the Knutzen Family Theater, ,a retreat and
meeting center, as well as a park and Puget Sound beach front.
. Poverty Bay Park - Located north of Dumas Bay Center, this park is a 48-acre site
of undeveloped open space, with approximately 500 feet of beach shoreline.
Opportunities for new access to the shoreline in Federal Way are limited. The City and state
park resources and the public open space offer access to the shoreline and Puget Sound
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City of Federal Way Draft Shoreline Inventory & Characterization
throughout the City. Most other areas are developed residentially. The City could explore
developing additional street-end overlooks or beach access points. Undeveloped rights-of-way
totall.7 acres in the nearshore shoreline environments; these could be potential beach access or
overlooks.
4.3.8 Historical/Cultural Resources
The existing Federal Way Comprehensive Plan provides a general goal to identify, protect, and
restore those areas and facilities within the City that are of historical or archeological
significance (City of Federal Way, 2002). The plan establishes a goal to ensure that historic
properties and archeological sites are protected as "important elements in the overall design of
the City." Policies in the Comprehensive Plan define characteristics that enable the identification
of historic and archeological sites, and direct the City to preserve and protect these sites from
incompatible land uses. '
Native American use of water bodies throughout western Washington has been well documented.
Native peoples undoubtedly used tributaries ofthe Green River, the Hylebos Creek, and Puget
Sound Marine shoreline for fisheries resources. Historic GLO survey maps from the 1860s do
not identify any native American village sites or any other Native American sites within the
City's marine shoreline planning area. The Historical Society of Federal Way includes an article
review of Native American use within the vicinity of the City. The article does not indicate that
village sites are known to exist within the vicinity. However, the article notes the presence of
Native American artifacts and,.in one instance, human remains along the marine shoreline
(Historical Society of Federal Way, 2005). Shell middens have been documented within the
City's marine shorelines. The City requires review of archeological and historical resources on a
parcel-by-parcel basis during development review as warranted.
The Historical Society of Federal Way works to restore and preserve structures and artifacts of
historical significance within and around Federal Way. The society owns and maintains two
historical cabins, both of which have been relocated to Historic Cabins Park near 348th Street and
4th Avenue South. The park area is not within the City's Shoreline Planning Area (Historical
Society of Federal Way, 2003).
The Washington State Department of Archeology and Historic Preservation maintains a database
of sites listed on Washington's Historic register and the mitional register. A search of the
database, for sites within the City's shoreline planning area revealed no listed sites of historical
significance (DAHP).Additionally, no sites are listed on King County's Local Landmarks List
(King County, 2006). '
5.0 FRESHWATER LAKES PLANNING AREA INVENTORY
The purpose of this section of the report is to inventory and characterize freshwater lake
conditions within the Shoreline Planning Areas in greater detail and in the context ofthe larger
watershed. The intent is to identify how existing conditions in the freshwater lake shoreline
influence or contribute to alterations of processes that maintain aquatic ecosystems. The study
area is shown on Figure 1 and subsequent figures as the City's shoreline planning area.
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City of Federal Way Draft Shoreline Inventory & Characterization
5.1 Physical Features
5.1.1 Drainage Basins and Surface Water
Drainage in the Federal Way area is divided into five basins: Lower Puget Sound, Lower Green
River, Mill Creek, Hybelos Creek, and White River Basins. Surface water that does not feed the
freshwater lakes is directed either west to Puget Sound, east into the Duwamish-Green River
Valley, or south to Commencement Bay. Freshwater lakes that are part of the shoreline
jurisdiction are located in all the drainage basins and are discussed below.
Steel lake
Steel Lake (Reach 2) is located in the Lower Puget Sound basin in the western part of Federal
Way. Streams within the basin generally flow north and west into Puget Sound and have incised
ravines into the steep coastal bluffs. Steel Lake is situated on top of low-permeability till, which
suggests that it likely receives most of its water from surface runoff from the adjacent hills rather
than from groundwater seepage. Although there is not any visible inflow, surface water in the
watershed is conveyed to the lake and discharged through 14 stormwater outfalls. Outflow
passes through a Category 1 wetland on the western shoreline and then flows through a culvert to ,
another wetland and then becomes Redondo Creek, flowing through the City of Des Moines to
the Puget Sound.
The City established the Steel Lake Management District (LMD) in 2003 to provide integrated
, aquatic vegetation management and community education. The LMD is now in its third year and
the program has seen considerable success in the reduction of aquatic weeds and the maintenance
of beneficial uses (Le. swimming, fishing, boating).
Star lake
Star Lake (Reach 3) is located in the Lower Green River basin in the Federal Way P AA.
Topography in the basin directs surface water, including the outlet stream of Star Lake, eastward
into the Duwamish-Green River Valley. Star Lake lies on till and recessional outwash deposits
that overlie till at a shallow depth. Star Lake-is likely a kettle lake formed by the melting of
large blocks of glacial ice buried in the glacial drift of outwash plains left behind as continental
glaciers receded. Consequently, the lake is probably supplied by a combination of surface runoff
and groundwater seepage. Very small streams, runoff and groundwater are the primary
contributing water sources to the lake. the outfall is via a pipe and culvert to Bingham Creek and
then to the Green River.
lake Dolloff and lake Geneva
Lake Dolloff (Reach 4) and Lake Geneva (Reach 5) are located in the Mill Creek basin in the
Federal Way PAA. Surface drainage in the basin flows eastward into the Duwamish-Green
River Valley through the Mill Creek valley of Auburn. Mill Creek, which drains the south end
of Lake Dolloff, has incised a deep ravirie that is also fed by small tributary streams, which drain
the surrounding hillsides. Lake Dolloff is formed on recessional outwash deposits and thus is'
probably fed principally by groundwater infiltration. Although there are no major inflows to the
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,City of Federal Way Draft Shoreline Inventory & Characterization
lake, wetland areas, runoff and groundwater are contributing water sources. An outflow through
a wetland exists at the sOHthern end of Lake Dolloff.
Lake Geneva likely receives most of its water supply from surface drainage overtop of till.
Inflows to the lake come from a small stream on the southern end ofthe Jake, adjacent wetland
areas, runoff and groundwater. Outflow exits at the northeast comer of Lake Geneva through a
wetland, which forms a small tributary to Mill Creek.
North lake and lake Killarney
North Lake and Lake Killarney (Reaches 6 and 7) are located in the Hylebos Creek Basin in the
south-central part of Federal Way. Both lakes are drained by Hylebos Creek, which flows
southward into Commencement Bay. Other small streams in the basin also drain to the south
and either join with Hylebos Creek or terminate in wetland areas. Both lakes lie on top of till,
and therefore likely receive surface runoff from the surrounding area.
North Lake is located in the Hylebos Creek basin within the City limits for Federal Way. Inflow
occurs via a smaIl tributary through a wetland on the north shore. Groundwater, runoff and
precipitation are additional water sources. Outflow occurs via a tributary through a wetland in
the southwestern comer ofthe lake. North Lake drains to a pond ,on the Weyerhaueser campus
then through a pipe to a wetland, which drains to the west fork of the Hylebos.
The northwestern section of Lake Killarney is located within Federal Way City limits, with the
remainder of the lake within the P AA. There are no stream inflow sources. A wetland along the
northern boundary likely serves as a water source during certain periods of the year, with
groundwater, precipitation and runoff acting as the primary sources of incoming water. Outflow
exits the lake to the southwest through a small, concrete culvert into a tributary. Lake Killarney
drains to the east fork of the Hylebos. ,
Five Mile lake
Five Mile Lake (Reach 8) is situated in the White River drainage basin in the Federal Way PAA.
The lake is fed by wetlands to the north as well as springs, runoff and groundwater. Five Mile
Lake is likely a kettle lake formed by the melting of large blocks of glacial ice buried in the
glacial drift of outwash plains left behind as continental glaciers receded. ' Five Mile lake drains
to Trout Lake to the southeast, which then flows to the White river.
5.1.2 Geologic Hazard Areas
5.1.2.1 Seismic Hazard Areas
King County GIS maps (accessed on 5/18/06 at http://www.metrokc.gov/gis/
mapportal/iMAP _ main.htm) do not indicate seismic hazards associated with the freshwater lake
areas (Reaches 2 through 8). Areas of low to moderate liquefaction susceptibility are designated
on maps produced by the Washington Department of Natural Resources (Palmer et aI., 2003);
however, map coverage is limited to the western part of Federal Way, and does not include the
freshwater lakes planning area.
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City of Federal Way Draft Shoreline Inventory & Characterization
Correlations between soil conditions and liquefaction susceptibility in the western part of Federal
Way permit s9me inferences regarding the hazard in the unmapped areas of the freshwater lake
planning area. Regions in the western part of Federal Way that are mapped as having low to
moderate liquefaction susceptibility include, the areas around Lorene and Jeane Lakes as well as
several smaller lakes which are unnamed on existing maps. Typically, those areas considered to
be susceptible to liquefaction are mapped as recessional outwash or consist stratigraphically of
fine-grained wetland deposits overlying granular recessional outwash deposits. Those areas
underlain by till are generally considered to have very low liquefaction susceptibility. The
shorelines of Star, Dolloff, and Five Mile Lakes (Reaches 3, 4, and 8) are underlain largely by
recessional outwash and/or wetland deposits, and thus most likely have low to moderate
liquefaction susceptibility. The shorelines of Steel and North Lakes and Lakes Geneva and
Killarney (Reaches 2,6,5 and 7) are underlain primarily by till, with small areas of wetland and
outwash deposits. Most of the areas within these segments would likely have very low
liquefaction susceptibility.
5:1.2.2 Erosion Hazard Areas
Erosion hazard areas are not present within the majority ofthe freshwater lakes shoreline
segments (Reaches 2 through 8) according to City GIS maps and King County GIS maps
(Figures 9D through 9H). An exception is the outlet located on the western shoreline of Steel
Lake (Reach 2), which is mapped as an erosion hazard area. That outlet feeds a small stream,
which flows westward to Puget Sound. Approximately 11 percent of the Steel Lake Reach is
designated an erosion hazard area.
, The drainage basins for six ofthe seven freshwater lakes in the shoreline planning area contain
erosion hazard areas: Steel, Star, Dolloff, North Lakes and Lakes Geneva and Killarney. Those
areas with erosion hazards are primarily concentrated in narrow corridors along streams or on
hillsides, and make up a very small proportion of the drainage basin analysis area.
5.1.2.3 Landslide Hazard Areas and Steep Slopes
Landslide hazard areas and steep slopes do not occur within the fresh water lakes shoreline
Reaches (Reaches 2 through 8) according to City GIS maps and King County GIS maps (Figures
9D through 9H). However, landslide hazards are in factpresent in the far eastern portions of the
shoreline analysis areas for Five Mile Lake, Lake Geneva, and Star Lake. Those areas include
the relatively steep valley walls of the Duwamish-Green River Valleys and the ravines of several
small streams, including Mill Creek.
5.1.3 Aquifer Recharge Areas
Critical aquifer recharge areas in Federal Way, as defined above in section 4.1.3, are commonly
associated with regions that are underlain by recessional outwash deposits. Such deposits
generally have high infiltration rates because they tend to be relatively permeable and allow for
rapid movement of water. Alternatively, infiltration rates in till are typically low because of
limited pore space arising from a variety of grain sizes and a high degree of compaction.
Critical aquifer recharge areas in the freshwater lakes planning area include the areas around
Star, Dolloff, and Five Mile Lakes (Reaches 3, 4, and 8) according to City GIS maps and King
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City of Federal Way Draft Shoreline Inventory & Characterization
County GIS maps (accessed on 5/22/06 at http://www.metrokc.gov/gis/mapportal/
iMAP _main.htm).
5.1.4 Flood Hazard Areas
Frequently flooded areas are defined in Chapter 18-28 of the FWMC as those areas in the
floodplain subject to a one percent or greater chance of flooding in any given year including but
not limited to such areas as streams, lakes, coastal areas and wetlands. According to King
Courity GIS maps (Figure 6), the shoreline of Lake Dolloff (Reach 4) is located within a 100-
year floodplain, and thus may be considered a flood hazard area. The remaining areas located
within the freshwater lakes shoreline jurisdiction (Reaches 2, 3, 5, 6, 7, and 8) are not currently
considered to be within 100-year floodplains.
5.1.5 Streams
The upper plateau lies within 5 drainage basins that have been identified in Federal Way: the
Lower Green River, Mill Creek, Hylebos Creek, White River and Lower Puget Sound. Of these,
the Hylebos Creek and White River are within Watershed Resource Inventory Area (WRIA) 10-
Puyallup/White; the other drainage basins, including the portion of the Lower Puget Sound
basin, which covers the Redondo Subarea, are within WRlA 9 - Duwamish/Gre,en. The
freshwater shoreline lakes form the headwaters for several streams including Redondo Creek,
tributaries to Mill Creek, and the East and West forks ofHyh~bos Creek
The Hylebos Creek is the largest drainage basin for the upper plateau of Federal Way. The
Hylebos Creek basin is approximately 18,361 acres in size, and contains 25 miles of stream, 11
named lakes, and 250 acres of wetlands (Kerwin, 1999). There are two major tributaries to
Hylebos Creek, the West and East Forks. The headwaters ofthe West Fork ofthe Hylebos are
located in Federal Way near South 320th Street (Pierce County, 2006). The East Fork originates
in King County near North Lake and Lake Killarney in the City's P AA. The two forks join east
ofInterstate-5 in the City of Milton. From the confluence of these forks in Milton downstream,
the Hylebos Creek itself is considered a shoreline ofthe state. Hylebos Creek enters the Hylebos
Waterway in Tacoma and drains to Puget Sound's Commencement Bay.
The majority of the Hylebos basin is urbanized, and covered by commercial development and
single and multifamily residential dwellings. Approximately two-thirds ofthe basin is located in
the city of Federal Way, which experienced large population growth in the 1980's (Friends ofthe
Hylebos Wetlands, 2006). As of 1999, the City of Federal Way was 96 percent built out, with
more than half the land area covered with impervious surfaces (Kerwin, 1999). Due to
deforestation, the increase in impervious surfaces, and the loss of adjacent wetlands in the
Hylebos Creek basin, the damaging peak flows in the creek have, increased dramatically, as
compared to pre-development conditions. .
There has not been a comprehensive water quality study performed on the Hylebos basin.
However, it is generally accepted that non point and point source pollution problems affect water
quality throughout the basin (Kerwin, 1999).
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City of Federal Way Draft Shoreline Inventory & Characterization
5.1.6 Shoreline Modifications
Land use and development surrounding the freshwater lakes in Federal Way have resulted in
shoreline modifications including the placement of bulkheads, removal of forested vegetation
and other alterations as described below. Shoreline modifications provided here are based upon
a one-day field reconnaissance of the lakes as part of this inventory and analysis.
Steel Lake
The basin around Steel Lake was already significantly developed in 1976 when only 15 percent
ofthe land in the drainage basin was classified as forested or unproductive (USGS, 1976).
According to King County, in 2002 less than 10 percent was classified as forested or timber
,harvest areas (King County, 2002) indicating rapid urbanization.
It appeared that most residential parcels on the lake has been developed. The exceptions are the
park, and wetlands and the remaining undeveloped lots. Of the developed parcels, at least 50
percent have bulkheads and the featureless shoreline habitat associated with them. Extensive'
shoreline armoring and overwater structures have significantly reduced the riparian vegetation on
Steel Lake, although abundant riparian vegetation has been observed near the creek inlet at the
west side ofthe lake. Low-growing vegetation and shrubs in the nearshore are lacking, however
numerous mature trees still are present in most of the developed parcels. The wetland to the west
coveres approximately 10 percent of the shoreline and provides good riparian conditions and
habitat.
Star Lake
Land use surrounding Star Lake has changed since 1976 when 46 percent ofthe land in the
drainage basin was still classified as forested or unproductive (USGS, 1976). According to King
County, in 2002 less than 10 percent was classified as forested or cleared (King County, 2002).
The shoreline of Star Lake is entirely developed with multiple layers or tiers of houses as one
moves up the slope away from the lake.
It appears that nearly every available parcel on the lake has been developed. Of the developed
parcels, approximately 10 to 20 percent have bulkheads and the featureless shoreline habitat that
is assoGiated with them. Even though Star Lake has minimal shoreline armoring, significant
riparian and upland vegetation are still lacking. There are relatively few large trees within 25 feet
ofthe shoreline although there are occasionally over hanging willows and other shrubs near the
shore.
Lake Dolloff
Land use surrounding Lake Dolloff has changed since 1976 when 65 percent of the land in the
drainage basin was still classified as forested or \loproductive (USGS, 1976). According to King
County, in 2002 only 25 percent of the land in the drainage basin was still classified as forested
or cleared (King County, 2002).
About two-thirds of the available parcels on the lake have been developed; however most houses
have small footprints and are placed further away from the lake shore. Very few bulkheads are
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City of Federal Way Draft Shoreline Inventory & Characterization
visible, allowing for intact riparian buffer zones near the waters edge along most of the shoreline.
Multiple layers of vegetation are present, consisting of over-hanging trees, shrubs, and large
evergreens in many cases within 25 feet of the shoreline. This provides excellent coverage and
habitat. Large wetland areas exist in the north and south ends of the lake as well as a small
section on the eastern shore. Combined, these wetlands cover approximately 30 percent of the
lake shore and provide good riparian conditions and habitat.
lake Geneva
Approximately 28, percent of the land in the drainage basin surrounding Lake Geneva was still
classified as forested or unpr09uctive in 1976 (USGS, 1976). According to King County, in
2002 approximately 8 percent was still classified as forested or cleared (King County, 2002).
It appeared that a majority of the available parcels on the lake have been developed. However,
the use of bulkheads seemed to be minimal. Compared to most urban lakes, nearshore vegetation
was relatively intact throughout most of the lake shoreline and consisted of over hanging trees
and shrubs. The eastern shoreline had an approximately 1,000 foot-long section of steep
shoreline containing a mature stand of trees. A wetland area in the northern section of the lake
provides additional shoreline protection and habitat for a variety of species. This wetland
comprises approximately 5 percent of the lake shore.
North lake
In 1976, approximately 73 percent of the land in the drainage basin was still ,classified as
forested or unproductive (USGS, 1976). According to King County, in 2002 approximately 48 ,
percent was still classified as forested or cleared (King County, 2002).
Only a little over half of the lake appeared to be developed. Weyerhaeuser owns a 52-acre parcel
of land that protects most of the western shoreline. Of the developed area, bulkheads comprised
approximately 25 percent of the shoreline. Some overhanging trees and shrubs were present
along segments of the developed shoreline, but most mature trees were absent within 25 feet of
the lake. The second-growth forest along the western shoreline does provide a diverse, complex,
and near natural riparian zone. In addition, the smaller wetlands at the inflow/outflow provide
additional habitat.
lake Killarney
Approximately 59 percent of the land in the Lake KilIarney drainage basin was still classified as
forested or unproductive in 1976 (USGS, 1976). According to King County, in 2002
approximately 17 percent was still classified as forested or cleared (King County, 2002).
The use of bulkheads seemed to be minimal especially in the North arm where nearshore
vegetation was predominately intact providing in-water structure. The eastern shoreline was
moderately steep, however development was not tiered; thus many mature trees were still
present. In the southern arm, more of the developed parcels exhibit featureless shorelines with
little habitat. A wetland area in the northern section of the lake comprising approximately 10
percent of the lake shore provides additional protection and habitat. In addition, a 10.8-acre
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City of Federal Way Draft Shoreline Inventory & Characterization
parcel of land used as a park on the western shoreline contains diverse vegetation and natural
shoreline.
Five Mile Lake
Land use has changed since 1976 when 75 percent of the land in the drainage basin was still
classified as forested or unproductive (USGS, 1976). According to King County, in 2002
approximately 42 percent was still classified as forested or cleared (King County, 2002).
Only about half ofthe available parcels on the lake have been developed. However, of these,
approximately 50 percent have bulkheads and the featureless shoreline habitat that is associated
with them. In-water, nearshore vegetation consists of periodic stands of cattail. There are
relatively few large trees within 25 feet of the shoreline although there are occasionally over-
hanging willows and other shrubs near the shore. An exception is at Five'Mile Park, where a 600
foot section of shoreline contains a stand of mature trees. The large wetland areas in the north
and northeastern sections of the lake that have protected shorelines provide good riparian
conditions and habitat. These wetlands comprise approximately 35 percent of the lake shore.
, ,
5.2 Biological Resources
5.2.1 Lacustrine Habitats
Lacustrine habitats are those habitats found along shores of freshwater lakes to water depths
where aquatic plants still receive light. The shallow shoreline of several of the lakes in Federal
Way offer excellent habitat for aquatic plants. However, non-native aquatic species also take
advantage of the shallow shoreline. Eurasian watermilfoil (Myriophyllum spicatum), purple
loosestrife (Lythrum salicaria), fragrant water lily (Nymphaea odorata), and yellow flag iris (Iris
pseudacorus) have all been identified within the lakes of Federal Way. Several of the lakes
undergo treatment in an attempt to eradicate Eurasian watermilfoil, including Star Lake, Lake
Dolloff, Lake Geneva, North Lake, Killarney and Five Mile Lake.
5.2.2 Wetlands
Lacustrine and palustrine wetlands are identified by the NWI immediately adjacent to and
associated with lakes within the City's shoreline planning area. In addition, the City's Wetland
Inventory (Sheldon and Associates, 1999) identifies and maps wetlands throughout the City,
along with classification pursuant to FWMC 18-28. These inventories are used as primary
sources in the discussion of wetlands within the planning area of seven freshwater lakes included
in the City's shoreline jurisdiction (Figures 6 and ll-D through II-H).
Most ofthe freshwater lakes within the City, except for Steel Lake (Shoreline Reach 2) are
considered wetlands by the City's Wetland Inventory. However, in many cases the lakes
constitute deepwater habitats (water depths greater than 6.6 feet) that are not wetland according
to the state definition. The Category I (FWCC 18-28) wetland identification of these lakes
(Shoreline Reaches 3 - 8) includes open water areas and shoreline edges, as well as (with the
exception of Star Lake, Reach 3) portions of the land immediately adjacenttothe lakes. At Steel
Lake, a large, Category I wetland was identified beginning at the western-most portion of the
lake and continuing northwest across South 304th Street through the undeveloped area. Three
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City of Federal Way Draft Shoreline Inventory & Characterization
other small, Category III wetlands were identified along the north (2 wetlands) and south (1
wetland) shores of Steel Lake (Figure II-E).
The NWI maps identified all of the seven freshwater lakes (Reaches 2 - 8) as permanent
lacustrine wetlands, with a pattern of similar ecological system classification at all lakes except
Star Lake. The entire area of Star Lake was classified as a lacustrine open water wetland with no
other wetlands identified in the adjacent areas. AquatiC bed wetlands are mapped at or near each
lake's shoreline.
Palustrine, or freshwater, wetlands were identified by the NWI map as adjacent and associated
with all lake reaches except for Star Lake and Lake Geneva (Reaches 3 and 5). At Steel Lake
(Reach 2), a scrub-shrub and forested wetland stretches from the west end of the lake to the
northwest at the outlet stream. This wetland is considered an "associated wetland" and part of
the shoreline jurisdiction. At Lake Dolloff (Reach 4), a palustrine forested wetland and open
water/aquatic bed are mapped at the northwest end ofthe lake (Figure II-E). This is considered
"associated wetland" as is wetland areas to the northeast of Lake Dolloff and south of South
303rd Street. A wetland also extends along the outlet stream to the southeast.
At North Lake (Reach 6), a palustrine scrub/shrub and emergent wetland is identified as
extending to the north from the northeast corner ofthe lake (Figure II-F). At Lake Killarney
(Reach 7), a palustrine emergent and scrub-shrub wetlands are mapped as adjoining to the north
of the lake (Figure II-G). At Five Mile Lake (Reach 8), forested, scrub-shrub, and open water
wetlands are identified extending the north from the north end of the lake and spreading out to
the north and east from the northeast corner ofthe lake (Figure II-H).
5.2.3 Critical Wildlife Habitat and Species
Critical fish and wildlife habitat areas are those areas identified as being of critical importance in
the maintenance and preservation of fish, wildlife, and natural vegetation. Critical habitat, or
fish a~d wildlife habitat conservation areas, means habitat areas with which endangered,
threatened, or sensitive species of plants or wildlife have a primary association (e.g., feeding,
breeding, rearing of young, migrating) (Chapter 18-28 FWCC). Fish and wildlife habitat
conservation areas in the fresh waters of Federal Way include streams; ponds under 20 acres;
lakes, ponds and streams planted with game fish by a governmental or tribal entity; and State
natural area preserves and natural resource conservation areas.
Several state and federally listed species are known to occur or could potentially occur within the
City's freshwater shoreline planning area, as well as within waters downstream of Federal Way
(Table 9; Figure 10). Federally listed species that have been documented in the City include bald
eagle (Haliaeetus leucocephalus), commoilloon (Gavia immer), and Puget Sound/Strait of
Georgia coho salmon (Oncorhynchus kisutch), a federal species of concern. In general, coho and
other anadromou,s salmonids are not found within the freshwater lakes of Federal Way and its
PAA; however, salmonids do inhabit streams down gradient ofthese lakes.
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City of Federal Way Draft Shoreline Inventory & Characterization
Table 9; Federal and State Listed Threatened and Endangered Species in Federal Way.
Common name Scientific name Status Within Federal Way Downstream from
or P AA? Federal Way?
Bald eagle Haliaeetus Threatened ,Yes Yes
leucocephalus
Common loon Gavia immer State Sensitive Yes No
Pileated woodpecker Dryocopus pileatus State Candidate No Yes
Puget Sound/ Strait of Oncorhynchus kisutch Federal species of Yes Yes
Georgia coho salmon concern
Puget Sound Chinook Oncorhynchus Threatened No Yes
salmon tshawytscha
Puget Sound Oncorhynchus mykiss Proposed threatened No Yes
steelhead
CQastaVPuget Sound Salvelinus confluentus Threatened No Yes
bull trout
Steel lake
Steel Lake is within the Lower Puget Sound drainage basin, drains to the Puget Sound through
Redondo Creek. The lake has a mean depth of 13 feet, and supports stocked trout and bass (King
County, 2005). Streams within this basin are known to provide habitat for coho and fall chum
salmon. '
Star lake
Star Lake is within the Lower Green River Drainage Basin. Mean depth of the lake is 25 feet,
and supports stocked trout, bass, and other fish (King County, 2005). The Lower Green River
basin has rearing habitat for fall chinook, fall chum, and summer steelhead; spawning and
rearing habitat for coho; and documented presence of pink and sockeye salmon, bull trout/dolly
varden, and winter steelhead (WDFW, 2006). A pileated woodpecker nest has been identified
approximately 0.6 miles away, and bald eagle nest has been identified slightly over one mile
from Star Lake (WDFW, 2004). '
lake Dolloff and lake Geneva
Lake Dolloff and Lake Geneva are within the Mill Creek drainage basin. Lake Geneva has an
average depth of 19 feet, and supports populations of stocked trout and bass (King County,
2005). An adult common loon has also been documented at Lake Geneva (WDFW, 2004). Lake
Dolloff also supports populations of stocked trout and bass, as well as other fish species (King
County, 2002). Mill Creek is known to provide habitat to fall chinook and winter steelhead, as
well as spawning and rearing habitat for coho salmon (WDFW, 2006). Coho, chum and winter
steelhead have been observed spawning in Mill Creek (Kerwin and Nelson, 2000). Juvenile
coho, chum, winter steelhead, cutthroat and chinook have been captured in the creek.
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City of Federal Way Draft Shoreline Inventory & Characterization
North Lake and Lake Killarney
North Lake and Lake Killarney are within the Hylebos Creek drainage Basin. North Lake has an
average depth of 14 feet. Lake Killarney averages 9 feet in depth. Both lakes support
populations of stocked trout (rainbow and cutthroat), largemouth bass, and other fish species
including yellow perch, pumpkinseed sunfish, and brown bullheads (King County, 2005).
Salmonids inhabiting East Hylebos Creek, which is fed by both North Lake and Lake Killarney,
include coho salmon, chum salmon, and cutthroat trout (Taylor Associates, 2002). A bald eagle
nest has been identified within one quarter mile of North Lake (WDFW, 2004).
Five Mile Lake
Five Mile Lake is within the White River Drainage Basin. It has an average depth of 18 feet, and
supports populations of stocked trout and bass (King County, 2005). There is no surface water
connection from Five Mile Lake to the White River. The White River subbasin provides'
spawning or rearing habitat for fall and spring chinook, pink, fall chum, and coho salmon in
addition to bull trout/dolly varden, winter steelhead, and cutthroat trout. Sockeye salmon adults
are observed almost annually in this subbasin but there is some question to their ability to be
natUrally sustaining (Kerwin, 1999; WDFW, 2006).
5.2.4 Instream and Riparian Habitats
Streams and riparian corridors provide valuable wildlife habitat, a source of fluvial sediments to
the marine shoreline, recreational opportunities, and support for a range of fish species. Five
drainage basins have been identified in Federal Way that affect shorelines: Lower Green River,
Mill Creek, White River, Hylebos Creek, and Lower Puget Sound. Of these, the Hylebos Creek
and White River are within Watershed Resource Inventory Area (WRlA) 10 - Puyallup/White;
the other drainage basins, including the portion ofthe Lower Puget Sound basin,which covers the
Redondo Subarea, are within WRlA 9 - DuwamishlGreen.
Information on riparian habitat conditions was drawn in particular from the following
documents: Habitat Limiting Factors and Reconnaissance Assessment Report, Green/Duwamish
and Central Puget Sound Watersheds (Water Resource Inventory Area 9 (1nd Vashon Island)
(King County, 2000); A Catalog of Washington Streams and Salmon Utilization - Volume 1,
Puget Sound Region (Williams et al. 1975), and Federal Way Potential Annexation Area
Inventory (Federal Way, 2002). The following characterization is focused on conditions relative
to fish and wildlife habitat.
5.2.4.1 Lower Green River Drainage Basin
Approximately 18 percent of the riparian zone in the Lower Green River sub-watershed supports
native deciduous trees. However, deciduous stands are usually narrow (<100 feet) or comprised
of small, sparse trees mixed with patches of grass, pavement, or bare ground. Almost 50 percent
of the riparian zone is comprised grass or shrubs, many of which are non-native. Over 80 percent
ofthe riparian zone is currently considered to provide poor shade, organic matter recruitment,
and sediment filtration because native vegetation communities have largely been converted to
grass or shrubs and because development often extends to within 75 feet of the channel (King
County, 2000). The lower Green River is on Ecology's 2004 303(d) list for fecal coliform.
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City of Federal Way Draft Shoreline Inventory & Characterization
Star Lake, located in the Lower Green River Basin, is surrounded by residential land use. Much
of the shoreline is armored, and there are several piers and floats within the lake. Virtually no
riparian buffer exists on this lake. The riparian zone is largely vegetated with pasture grass
(lawn) and ornamental tree species.
5.2.4.2 Mill Creek Drainage Basin
The Washington State Department of Ecology's (Ecology) Aquatic Use Category sets criterion
for the protection of spawning, core rearing, and migration of salmon and trout, and other
associated aquatic life. Mill (Hill) Creek has been categorized as Non-Core Salmon/Trout
aquatic use. The creek is on Ecology's 2004 303(d) list for temperature, dissolved oxygen, and
fecal coliform bacteria.
Dolloff Lake and Lake Geneva are located within the Mill Creek Drainage Basin. Residential
land use surrounds Lake Dolloff. Riparian vegetation appears to be somewhat intact at the north
end of the lake, but at the south end, lawns and ornamental trees and shrubs dominate the
riparian zone.
Lake Geneva is almost completely surrounded by residential land use. There are patchy areas of
intact riparian vegetation. For the most part, vegetation within the riparian zone is composed of
lawn and ornamental tree and shrub species. '
5.2.4.3 White River Drainage Basin
The White/Stuck River is channelized between levees along both banks from its confluence with
the Puyallup upstream to RM 8.5. Water quality in the basin is generally good to excellent, but
some parameters he.we exceeded water quality standards because of sanitary sewage effluent
form the cities of Buckley and Enumclaw. Mud mountain dam at RM 29.6 interrupts
recruitment ofLWD and gravel to the lower reaches of the White River. Riparian condition is
affected by land use in the basin, which is predominantly mixed commercial/residential below
RM 8 (Kerwin, 1999). The lower Wh,ite River is on the 2004 303(d) list for temperature and pH.
Five Mile Lake is both located within the White River Drainage Basin. This lake is almost
completely surrounded by residential land use. There are patchy areas of intact riparian
vegetation, particularly along the north shore near the Buddhist Center and Lakeview Christian
Conference Center. Riparian vegetation in the residential areas is composed primarily oflawn
and ornamental tree and shrub species.
5.2.4.4 Hylebos Creek Drainage Basin
The Hylebos Creek drainage basin is located primarily in southwest King County and includes
the East Hylebos Creek (tributary 0006) and its three major tributaries (0016A, 0016, 0015).
Habitat within the Hylebos Creek subbasin has been severely altered from its historical natural
state. Residential development, erosion and frequent flooding threaten the creek. Portions of this
subbasin have been channelized with an associated loss of riparian habitat (Kerwin, 1999).
In the upper portion ofthe basin, one tributary drains from Lake Killarney over a relatively flat
upland till surface, south to 28th Avenue South and South 360th, then continuing to just south of
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City of Federal Way Draft Shoreline Inventory & Characterization
Kits Comer Road to join East Branch ofHylebos. East branch Hylebos Creek flows from North
Lake, then south through the Parkway Subarea ranging between 21 st Place South and 25th Place
South. The tributaries combine south of SR 161 and flow through a long, steep gradient reach
over Vashon advance outwash. The East and West Branches of Hylebos Creek converge within
the broad floodplain of Lower Hylebos Creek near the King-Pierce County line to form the
mainstem (Taylor Associates, 2002). East Hylebos Creek habitat was surveyed in 2001 from
RM 5.3 to RM 6.4. In this reach, habitat vvas predominantly low-gradient riffle stream habitat.
The mean width of the wetted channel was 10 feet and the mean bankfull width was 30 feet. The'
mean maximum depth of all pools was 1.4 feet. The stream had 63 pools per mile, though there
were no large pools (i.e., greater than one meter in depth), and no high-quality pools observed.
L WD recruitment was good, as the native. riparian buffer was wide and dense, composed of
medium sized (12-20 inch diameter) hardwoods, with approximately 20 percent ofthe trees
being mature conifers (Taylor Associates, 2002).
Both the East and West tributaries of the Hylebos Creek are perennial streams. Salmonids
inhabiting each tributary of Hylebos Creek include coho salmon, chum salmon, and cutthroat
trout. The streams appears to contain good salmonid habitat but the indicators in the pathway for
watershed conditions are not properly functioning due, to urbanization in the watershed (Taylor
Associates, 2002)Lake Killarney has patches of riparian vegetation surrounding the lake. Most of
the western riparian shoreline of North Lake is currently open space. The east shore of North
Lake is entirely residential, and has essentially no native riparian vegetation. In contrast, open
space and the Weyerhauser industrial and office park dominates the west shore ofthe lake, with
healthy intact riparian vegetation overhanging the shoreline.
5.2.5 Water Quality
To summarize lake condition in terms of water quality, the lake's trophic status is evaluated.
Trophic status refers to the combination of clarity, nutrient concentrations and algae levels that
are often used to determine how productive a lake is. Lake, productivity is often considered to be
undesirable because it leads to increase in plant and algae growth. The three major divisions of
trophic statu~ are: oligotrophic (refers to lakes of low productivity; clear water and few plants
and algae), mesotrophic (moderate productivity with some plants and algae) and eutrophic
(highly productive, algae and/or plant rich systems).
Lake flushing is a critical aspect of determining how vulnerable a lake may be to pollution.
Lakes with higher flushing rates are less vulnerable to the effects of pollutants because they have
a shorter residence time. This means that pollutants entering the lake via the stormwater outfalls
can move through the lake and exit through the outflow. Increases in impervious surfaces in the
upland environment can also affect subsurface groundwater flow into the lake h~ading to changes
in water quality. In general, many of the lakes have a low flushing rate because of the small
volume of water that enters and exists them.
Another aspect of water quality relates to turbidity and suspended sediment. Sedimentation and
stormwater runoff in the lakes has been identified as an issue of concern by the Surface Water
Management (SWM) Division. SWM currently has several programs in place to reduce the
transport of sediments and other pollutants to lakes and streams. These programs include street
sweeping, catch basin monitoring and cleaning, erosion/sedimentation control construction
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City of Federal Way Draft Shoreline Inventory & Characterization
inspections and stormwater facilty improvements in the form of pollution control structures and
regional detention facilities.
Steel lake
Steel Lake has an outflow and is expected to have a moderate flushing rate. Steel Lake can be
classified as mesotrophic, indicating moderate productivity with very good water quality (King
County,2006). Water clarity is in the mid-upper range of the small lakes monitored in King'
County. The average depth of the lake is 13 feet. Steel Lake is included in Washington States
list of impaired waters (the 303(d) iist) as a Category 5 water due to invasive exotic species. A
Category 5 listing indicates that the water is polluted and is of concern (Ecology 2004). In recent
years, the lake has been treated for Eurasian watermilfoil (Myriophyllum spicatum). Other state-
listed noxious weeds at Steel Lake include fragrant water lily (Nymphaea odorata) and yellow
flag iris (Iris pseudacorus). The Steel Lake Management District was created in 2003 for the
, purpose of managing aquatic vegetation and maintaining beneficial uses of the lake.
Star lake
Star Lake discharges to Bingham Creek via a culv~rt; however the outflow is considered small,
therefore, it will have a low flushing rate. This means that once pollutants enter the lake they
essentially remain there. The low flushing rates make the lake vulnerable to contamination and
nutrient loading from shoreline development and activity. On the other hand, the lack of a major
inflow stream can be a benefit since these streams are the primary source of pollutant
contribution from the surrounding watershed. Increases in impervjous surfaces in the upland
environment can also affect subsurface groundwater flow into the lake leading to changes in
water quality.
According to data collected by volunteers, Star Lake can be classified as oligotrophic, indicating
low productivity with excellent water quality (King County, 2006). Water clarity is in the upper
range of the small lakes monitored in King County. Elevated concentrations of fecal coliform
bacteria have been measured on occasion in the lake, resulting in the inclusion of the lake 'in
Washington States list of impaired waters (the 303(d) list) under Category 2. A Category 2
listing represents waters of concern where more monitoring is warranted, but where pollution
levels are not high enough to violate, water quality standards or where data are inadequate
(Ecology 2004).
lake Dolloff
Although Lake Dolloff does have an outflow, low flows will result in a low flushing rate. Data
collected by volunteers from 1996-2000 classified it as eutrophic, indicating it had high
productivity with fair water quality (King County, 2002). Elevated concentrations offecal
coliform have been measured on occasion in the lake. In addition, water samples collected
between 1998-2001 contained elevated total phosphorus concentrations resulting in the inclusion
ofthe lake in Washington States list ofimpaired waters (the 303(d) list) under Category 2. A
Category 2 listing represents waters of concern where more monitoring is warranted, but where
pollution levels are not high enough to violate water quality standards or where data is
inadequate (Ecology, 2004).
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City of Federal Way Draft Shoreline Inventory & Characterization'
lake Geneva
Since the lake does have an outflow, it will have a certain degree of flushing. According to data
collected by volunteers, Lake Geneva can be classified as being borderline mesotrophic
indicating it has low to moderate productivity and good water quality (King County, 2006).
Water clarity is high and is in the upper range for the small lakes in King County monitored in
2004. Lake Geneva is listed as a Category 1 lake in Washington's Water Qu~lity Assessment
meaning it met tested water quality.~tandards (Ecology 2004).
North lake
SinceNorth Lake does have an inflow and an outflow, it may have a moderate flushing rate,
though volumes are still low. North Lake can be classified as being mesotrophic indicating
moderate productivity and good water quality (King County, 2006). Water clarity is good. The
average depth of North Lake is 14 feet. North Lake is listed as a Category 1 lake in
Washington's Water Quality Assessment meaning it met water quality standards (Ecology 2004).
lake Killarney
Lake Killarney has only a small outflow, it will likely have a low flushing rate. Lake KilIarney
can be classified as being borderline eutrophic indicating moderately-high productivity and good
water quality (King County, 2006). Water clarity is low due to the naturally high color resulting
from the wetland along the northern shoreline. Elevated concentrations of fecal coliform and
phosphorus have been measured on occasion in the lake"resulting in the inclusion ofthe lake in
Washington States list of impaired waters (the 303(d) list) under Category 2. A Category 2
iisting represents waters of concern where more monitoring is warranted, but where pollution
levels are not high enough to violate water quality standards or where data is inadequate
(Ecology 2004).
Five Mile lake
Since Five Mile Lake is fed by wetlands to the north as well as springs, runoff and groundwater.
According to data collected by volunteers, Five Mile Lake can be classified as mesotrophic,
indicating it is only moderately productive with generally good water quality (King County,
2006). However, water clarity has been historically low and is rated as the third lowest ofthe
small lakes monitored in King County. Elevated.concentrations of fecal coliform have been
measured on occasion in the lake, resulting in the inclusion of the lake in Washington State's list
of impaired waters (the 303(d) list) under Category 2. A Category 2 listing represents waters of
concern where more monitoring is warranted, but where pollution levels are not high enough to
violate water quality standards or where data are inadequate (Ecology, 2004). '
5.3 Land Use Patterns
Land use patterns are described in the context of existing land use, as well as planned or future
land uses that are established by Comprehensive Plan land use designations and zoning
designations. '
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City of Federal Way Draft Shoreline Inventory & Characterization
5'.3.1 Existing Land Use
Existing land use is illustrated by the air photo depicting current conditions on Figures lI-D
through II-H. Existing land use was quantified using King County Assessor data. Existing or
current use categories for each parcel were regrouped into generalized existing land use
categories that correspond to the future land use categories used in the City's Comprehensive,
Plan. Additional categories of existing land use that do not have a corresponding
Comprehensive Plan land use designation are vacant, agriculture, and unknown. Table 10
summarizes the existing land uses for each of the freshwater lake reaches below.
Table 10. Existing Land Use
Single Multi Office Religious Right-of- Open Space Vacant Other
Family Family Industrial Services Way Park
Steel Lake 67.3 5.4 4.8 9.7 12.7 0.1
(Reach 2)
Star Lake 80 6.5 4.7 2.1 6.7
(Reach 3)
Lake Dolloff 60.2 8.2 ' 29.8 1.8
(Reach 4)
LakeGeneva 58.3 3.6 16.1 20.1 1.9
(Reach 5)
North Lake 34.7 20.9 3.1 14.4 21.2 5.7
(Reach 6)
KilIarney Lake 53.8 21.6 0.1 11.6 12.1 0.8
(Reach 7)
Five Mile Lake 32.06 5.8 11.5 39.09 9.1 2.45
(Reach 8)
5.3.2 Comprehensive Plan
According to the City ofFederafWay Comprehensive Plan Map (2006), the shoreline planning
area for lakes in the City is largely comprised of properties designated as low- to medium-
density residential (1 to 4 dwelling units per acre). Parks, Open Space, Public FacilitieslUtilities
designations comprise the second largest portion of the shoreline. Small areas designated as
commercial, office and multi-family comprise the remainder. The exception to this is North
Lake, which is about one-half single family and one-half office park uses. The Comprehensive
Plan Map does not include future land use designations for lakes in the P AA.
The City's existing Shoreline Master Program goals and policies are included as an element in
the land use chapter of the City's current Comprehensive Plan. This document also establishes
shoreline environment designations as Urban, Rural, and Conservancy Enviromnents, depending
on the land use and intensity of development. All freshwater lake shoreline planning areas' are
designated Urban. Lake Dolloff (Reach 4) has the additional designation of Rural along the
northern and northeastern shorelines. North Lake (Reach 6) has the additional designation of
Conservancy along the northeastern and eastern shorelines. Existing shoreline environment
designations are shown on Figures l2-D through l2-H.
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City of Federal Way Draft Shoreline Inventory & Characterization
5.3.3 Zoning Designations
Zoning' designations in the City of Federal Way and the PAA follow the land use designations
established in the City's Comprehensive Plan (Figures l2-D through 12-H) and King county
Comprehensive Plan. King County zoning designations apply in the P AA until those areas are
incorporated through annexation at which time, the pre-annexation zoning classifications
established in the city's Comprehensive Plan will apply. Star Lake, Lake Dolloff, Lake Geneva,
and Five Mile Lake are all completely within unincorporated King County; these lakes are,
however, included within the City's PAA. Lake Killarney is on the border between incorPorated
Federal Way and the PAA. North Lake and Steel Lake are completely within the City's current
incorporated area. County zoning designations in the pertinent freshwater lakes' shoreline
planning areas are primarily Moderate-Density Single-Family Residential (Urban Residential
Zones R-4 and R-6). More than 90 percent of the Star Lake and Lake Dolloffshoreline planning
areas in the PAA are zoned by King County as Urban Residential R.,6. The remaining
freshwater lake shoreline planning areas within the P AA are zoned by King County as primarily
, Urban Residential R-4 (KCC Chpt. 2lA.04.080 http://www.metrokc.gov/mkcc/Code/, KC Imap
viewer http://www.metrokc.gov/gis/mapportal/iMAPmain.htm# ). Federal Way pre-annexation
zoning classifications in the P AA are very similar to existing county zoning classifications for
the area.
City zoning within the North Lake, Steel Lake, and Lake Killarney shoreline planning areas is
consistent with the Comprehensive Plan shoreline environmental(?) designations. Lake
Killarney and Steel Lake are both designated as Urban shorelines and North Lake as both Urban
and Conservancy shoreline. Steel Lake is zoned as primarily Single-Family Residential with
small areas of Multi Family Residential and Commercial zoning. Lake Killarney is zoned as
roughly two-thirds Single-Family Residential with the majority of the remaining area zoned as
Office. Approximately one-half of the North Lake shoreline planning area is zoned Single-
Family Residential with Corporate Park (33.90 percent) and Office (6.20 percent) zoning
designations over the majority of the remaining area.
Table 11. Land Use, Zoning, and Shoreline Designations
Shorelin~ Existing
Segment Existing Land Use Zoning Shoreline
Designation
Multi-Fam 5.44% Commercial 2.82% Urban
Open Space 0.00% Multi-Family 5.89%
Park 9.65% Single-Family 86.53%
Right-of-Way 4.76%
Single-Famiiy 67.29%
2 Vacant ]2.68%
Commercial 3.71% Single-Family 93.46% Urban
Open Space 2.83%
Park ].90%
Right-of-Way 6.54%
Single-Family 80.82%
3 Vacant 2.07%
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City of Federal Way Draft Shoreline Inventory & Characterization
Shorelim Existing
Segment Existing Land Use Zoning Shoreline,
Designation
Right-of-Way 8.17% Single-Family 90.67% Urban
Single-Family 60.20% Rural
4. Vacant 29.82%
Open Space' 2.82% Single-Family 96.49% Urban
Park 13.24%
Right-of-Way 3.63%
Single-Family 58.30%
5 Vacant 20.66%
Industrial 5.73% Corporate Park 33.90% Urban
Office 15.20% Office 6.20% Conservancy
Open Space 8.11% Single-Family 51.17%
Park 6.33%
Right-of-Way 3.06%
Single-Family 34.73% I,
6 Vacant 21.1 9%
Office 21.58% ,Office 21.58% Urban
Open Space 0.43% ' Multi-Family 11.58%
Park 11.20% Single-Family 67.01%
Right-of-Way 0.12%
Singh~-Family 53.79%
7 Vacant 12.07%
Park 25.98% Single-Family 88.4 7% Urban
Quasi-Public 13.11%
Religious Ser, 5.82%
Right-of-Wav 11.53%
Single-Family 32.06%
8 Vacant 9.14%
5.3.4 Roads and Bridges
Roads and transportation infrastructure in the freshwater lake shoreline planning areas reflect the
existing land use patterns described above. The density of roads is relatively low within the
shoreline planning areas at all lakes due to the residential development and .open spaces that
surround. In areas where roads do pass into the City's freshwater lake shoreline planning areas,
the majority of roads are functionally classified as 'local streets'. According to the Federal Way
Comprehensive Plan, these roads primary function is to "provide direct access to abutting land
uses and serve as feeders to [road] facilities with higher functional classifications" (FWCP Chpt.
3, III-IS). Traffic levels on local roads are light relative to what is seen on collector or arterial
roads.
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City of Federal Way Draft Shoreline Inventory & Characterization
Roads and transportation infrastructure near or adjacent to waterbodies can create adverse
impacts to those natural systems by blocking flow or cre~ting impervious surfaces. Roadways
represent a significant source of impervious surface in urban areas. Auto-related pollutants
including petroleum products, hydrocarbons, and heavy metals accumulate on road surfaces and
are carried to nearby waterbodies during storm events through sheet runoff or stoimwater
collection systems.
5.3.5 Wastewater and Stormwater Utilities
Lakehaven Utility District (District) provides sanitary sewer service within the City's boundaries
and to unincorporated areas to the east and north ofthe City (including all PAA regions except a
small area at the northeast most extent of the PAA area). The District's system is described in .
Section 4.3.5.
Of the 27 pump stations in the District system, 2 are in close proximity to the City's freshwater
lake shoreline planning areas. Pump Station Number 31 is near Star Lake to the south, across
Star Lake Road along 37th Avenue South. Pump Station Number 12 is near Lake Dolloff to the
northeast, near the intersection of 37th Avenue South and South 304th Street.
The City of Federal Way's Comprehensive Plan is described in Section 4.3.5. The plan describes
that residential area's in Federal Way and the surrounding PAA at that time of adoption in 2002
.... primarily utilized septic tanks and drainfields. Recommendations within the plan include the
expansion and upgrade of existing treatment and conveyance facilities, and installation of new
, conveyance facilities to provide service to areas in the City and P AA using on-site septic
systems.
The City of Federal Way operates a Surfacewater management Utility. According to the City's
.' Comprehensive Plan (2002), the City has completed projects to create regional detention and
treatment facilities serving the City over the last decade. Localized stormwater treatment is also
required for new developments. The 1994 Surface Water Facilities Plan (City of Federal Way,
1994) indicates that regional facilities have been designed with a 100-year flood storage
capacity. Chapter 21 of the Federal Way Municipal Code establishes stormwater standards for
new development.
5.3.6 Other Utiliti~s
According to the City's Comprehensive Plan (2002) and the Lakehaven Utility District's
(District's) Comprehensive Water System Plan (1994), the District maintains decentralized water
supply production facilities that serve the majority of the City. The District operates 27 wells
with the water system connected by interties to the water supply of other utility districts. The
system allows the District to buy and sell water according to intra-District supply demands.
Water systems attached to the District through interties include the Highline Water District,
Tacoma Public Utilities, and the City of Milton's water supply system. Portions of the City's
water supply is provided by these surrounding water supply systems and other neighboring water
suppliers. The City's PAA is partially within the Districts water supply area and those of
neighboring water suppliers. . In addition, the City of Tacoma, Fruitland Water District, and
several private landowners own production wells.
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City oj Federal Way Draft Shoreline Inventory & Characterization
A variety of gas, telephone, electric, and related utilities serves the existing residential and
commercial developments within the freshwater lakes' shoreline planning areas.
5.3.7 Existing and Potential Public Access Sites
The City of Federal Way has a diversity of parks, open space, and public facilities, some of
which provide shoreline access. Ofthe seven freshwater lakes included in this shoreline plan
inventory, only Star Lake and Lake Dolloff are without public access~ Existing public access
parks are owned and operated by the City, King County, and Washington State. The City's
Parks Web site (2006), King County's Parks Website (2006a), and Washington State's Park
, Website (2006) describes the foilowing parks, open spaces, and public facilities in the City's
freshwater lake shoreline planning area. These areas are shown on Figure 13.
Steel lake Park
Public access is provided at various locations within the park including a Washington
Department ofFish and Wildlife boatramp located int eh northeast corner of the park. This park
is located on the southern shore of Steel Lake. Included in the 51.7 acre park is beach and lake
access, a boat launch, and swimming and fishing areas. Other park amenities include a
children's playstructure, a sand volleyball court, 5 picnic areas, restrooms, a parking area and a
concessions building. The park continues across South 3l2th Street to the south, with additional
parking (roughly 100 total stalls), 3 ballfields, and a skate park. Trout and largemouth bass are
stocked in the lake for fishing. Other fish found in the lake include yellow perch, pumpkinseed,
and brown bullhead.
Star lake and lake Dolloff
Although there is not a park at either Star Lake or Lake Dolloff, the public has access via public
boat ramps at each lake. Trout and largemouth bass are stocked each of these lakes.
lake Geneva Park
Lake Geneva Park, owned and operated by King County, extends to the east from the northeast
shore of Lake Geneva. Included in the 18.64 acre park is beach and lake access, a fishing area, a
boat ramp, and a non-motorized boat put-in area. Other park amenities include a children's play
structure, open playfields, 5 picnic areas, 1 covered picnic area, restrooms, a parking area and
two ball fields. Trout and largemouth bass are stocked in the lake
lake Killarney and North lake Public Fishing Areas
Washington Department ofFish and Wildlife owns and operates public fishing areas at Lake
KiIlarney and North Lake. Both areas include public access to the respective lakes as well as
public restroom facilities. Lake KiIlarney Public Fishing Area, located at the north end ofthe
lake, includes gravel parking area as well as a boat ramp into the lake. North Lake Public
Fishing Area, located at the north end ofthe lake, includes two paved parking stalls. A trail
maintained by Weyerhaeuser runs along thewestern shoreline of North Lake.
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City of Federal Way Draft Shoreline Inventory & Characterization
, lake Killarney Park
Lake Killarney Park, owned and operated by the City, extends northwest from Lake Killarney to
the corner of South 349th Street and Weyerhaeuser Way South. Included in the 12-acre park is
lake access along walking trails and at picnic facilities. The City describes the park as being a
'Neighborhood / Open Space Park'. A WDFW boat ramp provides water access on the eastern
shore. Fishing and boating are popular activities at Lake Killarhey. Trout and largemouth bass
are stocked in the lake, though other species present include perch, pumpkinseed and catfish
Five Mile lake Park
Five Mile Lake Park, owned and operated by the King County, extends to the northeast from the
lake's eastern shore. Included in the 31.94 acre park. is beach and lake access, including
swimming and fishing areas. The swimming area includes a floating swim platform and a
bathhouse facility. The fishing area includes a pier. Other park amenities include a children's
j>laystructure, a sand volleyball court, 2 picnic areas, 3 picnic shelters, 2 barbeque areas with 7
barbeque pits, a lookout tower, local trails, several sports courts, 2 baseball fields, an open play
field, restrooms, 2 parking area and a concessions building.
5.3.8 Historical/Cultural Resources
The existing Federal Way Comprehensive Plan provides a general goal to identify, protect, and
restore those areas and facilities within the City that are of historical or archeological
significance (City of Federal Way, 2002). The plan establishes a goal to ensure that historic
properties and archeological sites are protected as 'important elements in the overall design of
the City. Policies in the Comprehensive Plan define characteristics that enable the identification
of historic and archeological sites, and direct the City to preserve and protect these sites from
incompatible land uses.
There are no known archeological or historical resources within the freshwater lake shoreline
planning areas. However, native American archaeologi.cal resources may exist along the
shoreline ofthe freshwater lakes in the City and its PAA. The Washington State Department of
Archeology and Historical Preservation does not indicate any areas within and adjacent to
freshwater lake shoreline designation as being included in their database of listed properties
(DAHP). The Historical Society of Federal Way documents the history of a series of dance halls
associated with parks and resorts at several of the lakes within the City and the PAA, however
none of the dance hall structures remain (Historical Society of Federal Way, 2000). The City
requires review of archeological and historical resources on a parcel-by-parcel basis during
development review.
6.0 RESTORATION AND OPPORTUNITY AREAS
This section summarizes key findings concerning how functions of coastal and freshwater lake
shorelines have been impaired, both by land use activities and alterations occurring at an
ecosystem-wide scale, and by activities within the City, its PAA, and its shoreline planning area.
This section also identifies opportunities for the protection or enhancement of areas where
shoreline ecological functions are intact, and opportunities for restoration of impaired shoreline
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City of Federal Way Draft Shoreline Inventory & Characterization
functions, at both a programmatic (i.e., City-wide) and site specific level. Opportunities for
enhanced or expanded public access to the shoreline are also discussed.
6.1 Coastal Areas I Nearshore Environment
6.1.1 Status of Shoreline Functions
Table 11 provides a summary of shoreline ecological functions for the CoastallNearshore ,
Environment. Causes of impairment and the relative scale at which impairments are occurring
(e.g., watershed, PAA-wide, shoreline reach scale, or multiple scales) are id~ntified. Finally,
general or programmatic restoration opportunities to address impairments are described.
Following Table 11 is a more detailed discussion of site-specific restoration opportunities.
Table 11. Summary of Shoreline Functions and Programmatic Restoration
Opportunities - Coastal Puget Sound
;,
~ ,J ~
';;'Condition and €auses (),fJniP~iltw~*t.
Bulkheads on shoreline deflect wave
action and disrupt natural coastal
processes. Bulkheads disrupt natural
delivery of sediment to the coastal areas,
as well as increase beach scouring and
wave deflection.
Alteration to and development on feeder
bluffs reduce the potential ofthese areas
to provide sediment delivery to coastal
zones, disrupting natural coastal beach
accretion.
Wetlands adjacent to the Puget Sound
coast are altered due to development and
land use and can no longer provide
essential storage, recharge, or water
quality functions.
Riparian habitat along the coast has
been impaired through lanel
development. Forest riparian vegetation
exists but over time has been reduced.
Large woody debris recruitment is
limited.
Scal;,of '7,
:. !'., AIteration~, and,
:~,,\:> .:<,.....' ':. . . -':"':,:'::":- .<~> '.:' - :/'
.'.. Impairm~n,t
Watershed scale,
Reach scale
Watershed scale
Watershed and
Reach scale
Watershed scale
and Reach scale
. Ii B.~Q~ogic~1
. s,'Affected
Hydrologic, Sediment
transport and
deposition
Sediment Delivery
Hydrologic
Hyporheic
Water quality
Riparian habitat
structure
.f,t:og;ani'r(iafic;';' .
RestoratiQn:, ". .
'Opportu~ities .
Remove bulkheads or
replace with soft-shore
armoring wherever
possible.
Protect high priority
feeder bluffs' and
preserve these areas.
Restore feeder bluffs,
remove bulkheads and
reestablish some
sediment delivery
processes.
Target local cQastal
wetland restoration and
mitigation so they
provide storage, ,
detention, and water
quality functions.
Restore and reconnect
wetlands adjacent to
Puget Sound coast to
provide salmonid
habitat.
Protect and restore
tributaries to the Puget
Sound which provide
habitat and deliver
woody debris and
sediment.
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City oj Federal Way Draft Shoreline Inventory & Characterization,
Man-made debris and remnant
structures in the coastal areas disrupt
intertidal habitats and salmonid passage.
Water quality in the nearshore
environment is impaired due to
remaining creosote pilings and other
toxic debris. Sediment transport and
accretion processes disrupted.
, '"':,,::;,~]~~~~:!:~~~::; ,
{~;,2::~nj:pitirnient ,
Watershed and
Reach Scale
co~ogic,ltl, '
Affect~d' :'
,. ,'Ci; , r~Qgr~jfi'in~hc '
, Rest-orat-io'll'
.' (i)pportit~it,ies'"
Target removal of
abandoned man-made
structures and
dilapidated docks where
possible. Remove
creosote pilings and
debris, which hann
intertidal habitats.
Intertidal habitat,
Water quality
6.1.2 Programmatic Restoration Opportunities
There are several general protection and restoration measures that can be applied to all of the
coastal/nearshore shorelines in Federal Way (see King County, 2005b). These include the
following:
· Protect and maintain existing riparian vegetation and forested areas:
· Prevent encroachment on functional riparian and wetland habitat;
· Educate property owners on the importance of the nearshore zone;
· Allow L WD to remain in the shoreline to provide structure for refuge;
· Limit additional bulkheads; promote devdopment of natural shorelines and habitats;
· Include the use of shoreline setbacks for new construction and promote shoreline
vegetation buffers;
· Maintain public access to the shoreline;
· Conserve or restore stream mouths; and
· Conserve or restore connections to upland sediment sources (feeder bluffs).
A recent study, conducted by Johannessen et aI. (2005), prioritized all drift cells within the
WRIA 8 and 9 marine shores for restoration and conservation. The results ofthe study indicate
that the WRIA 8 and 9 marine shorelines of the Puget Sound East reach are of moderate to high
conservation and restoration priority. The bluffs ofPuget Sound West were slightly less ofa
conservation and restoration priority, as much of the shoreline already falls within public park
boundaries, where development is already prohibited.
The historic character or shoretype (feeder bluff, transport zone, or accretion shoreform) of
modified shores was investigated in Johannessen et aI. (2005). Reaches that are currently
modified but contained historic sediment sources were compared across the shoreline planning
area. This data was prioritized based on the level of impact to the drift cell the unit falls within
and the value of that particular shore unit as a sediment source. Individually mapped feeder bluff
units were also compared across the entire study area and prioritized for conservation based on
the variable impacts to geomorphic processes'(the amount of rem aini rig feeder bluff in the drift
cell compared to historic conditions) and the value ofthat unit as a sediment source.
Three bulkheaded bluff segments in Puget Sound East were selected as bluffs of high restoration
priority or bulkhead removal (numbers 20-22 In Johannessen et aI. 2005). Three segments were
August 2006
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City of Federal Way Draft Shoreline Inventory & Characterization
also identified in Puget Sound West, each located within the bulkheaded shores between Dumas
Bay Park and Dash Point State Park. Several bluffs that are still functioning feeder bluffs were
identified as being of high conservation priority within the Federal Way shoreline: Only one
bluff is of high conservation priority in Puget Sound East, which is located approximately 0.5
miles from the eastern limit ofthe study area. Several bluffs in Puget Sound West were identified
for conservation. These include all mapped feeder bluffs in Dash Point State Park, and most of
the feeder bluffs mapped along the north and northwestern sides of the headland just west of
Dumas Bay Park.
6.1.3 Site-Specific Restoration Opportunities
The following specific restoration opportunities are listed for each coastal Puget Sound reach, in
order from east to west (Johannessen et aI., 2005; Anchor, 2006). General locations are shown
on Figure 14.
Puget Sound East
· Bulkhead removal (points 44, 45 in Johannessen et aI. 2005)
· Conserve feeder bluffs in the center of drift cell
· Rehabilitate riparian vegetation" at residential properties along the shore
Dumas Bay
· Remove fill and bulkhead
· Remove concrete footings of relict boat ramp
· Remove boulders, concrete from boat house acting as groin
· Remove concrete rubble
· Remove bulkhead and invasive species from Poverty Bay Park
· Remove creosote logs
· Remove Japanese knotweed
· Remove approximately 20 creosote piles
· Conserve and restore tributary mouths at Dumas Bay
· Fully reconnect the marsh at west end of Dumas Bay that is currently restricted by a berm
Puget Sound West
· Conserve unarmored shoreline west of Dumas Bay
· Remove creosote dolphin washed ashore
· Remove decaying barge and creosote dolphins
· Remove creosote soldier pile bulkhead
· Remove tires buried in sediment
· Remove creosote piles
· Remove 50 creosote piles and failed creosote bulkhead
· Remove riprap downstream of bridge in Dash Point State Park and substantially enlarge
creek estuary
· Restore the mouth of Dash Point Creek by removing armor (currently in planning stages
by WRlA 9), add sinuosity, and add riparian vegetation
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City of Federal Way Draft Shoreline Inventory & Characterization
6.2 Freshwater Shoreline Lakes
6.2.1 Status of Shoreline Functions
Table 12 provides a summary of shoreline ecological functions for the Freshwater Lakes
classified as shorelines in the City of Federal Way. Causes of impairment and the relative scale
at. which impairments are occurring (e.g., watershed, PAA-wide, shoreline reach scale, or
multiple scales) are identified. Finally, general or programmatic restoration opportunities to
address impairments are described. Following Table 12 is a more detailed discussion of site-
specific restoration opportunities per each lake identified.
Table 12. Summary of Shoreline Functions and Programmatic Restoration
Opportunities - Freshwater Lakes
Condition andea,use~,Qf!,
Impail'me)lt
Stream base flows may be impaired.
Summer low flows in the Hylebos
Creek have declined. Potential causes
include increased impervious area and
increased stormwater runoff. Lakes
store surface waters and support stream
base flows.
Wetlands separated from the lakes can
no longer provide essential storage,
recharge, or water quality
improvement functions.
Bulkheads and other hard shore
armoring disrupt natural connections
between the lake and riparian habitats.
Habitat is impaired along the lake
shores. The lack of lakeshore
vegetation and riparian structure has
. limited the habitat diversity, habitat
quality, and reduced large woody
debris.
Watershed scale,
Reach scale
Watershed, and
reach scale
Watershed, Reach
Watershed scale,
Reach scale
1'\.'>;'-""-'-'~L;~'8"-W'l'<-i~r ,~~~
SbOl1eline ECQlo.gi~~l
Functions Affected
Hydrologic
Hyporheic
Hydrologic
Hyporheic
Water quality
Hydrologic
Riparian Habitats
Instream and riparian
habitat structure
Water quality
Biological functions
.':~r':'-"~"':t'P::;', ""',>,~'::" .,':-'
.. P.rogramm~tlc'
Restoration
6npprtunitie~
Protect groundwater
and natural surface
water sources to the
lakes. Restore natural
flow patterns where
possible.
Target local wetland
restoration and
mitigation so they
provide storage,
detention, and water
quality functions.
Restore and reconnect
wetlands adjacent to
lakes and Hylebos
Creek. .
Promote replacement of
bulkheads with soft
shore alternatives.
Replant riparian
habitats using native
tree.s and shrubs.
Provide/encourage.
native landscaping
along the lakeshores,
including forested
riparian habitat
wherever possible.
Minimize future
removal of trees.
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City of Federal Way Draft Shoreline Inventory & Characterization
COl.HHti~l1 al1d'~auses of
. Xmpairl'lllln't
~." "" ..: .. '-.i
Water quality
Riparian habitat
j.,"'"
:: SI!,oreline Ecologi<llll
, F",n<;~,ions Affected
Surface water runoff from impervious
surfaces delivers pollutants and
sediment to the lakes, which in turn
adversely affects lake water quality.
The potential causes of water quality
impairment (i.e.; contamination by
fecal coliform) include leaking septic
systems and animal wastes entering the
stream (in the City and upstream in the
watershed). Resi.dentiallandscaping or
other sources may be delivering
increased nitrates, phosphorus and
pesticides. Stormwater related
polhitants (concentrated in urbanized
areas including the City) may be the
primary cause.
Erosion and stream scouring caused by
flash run-off from imperVious surfaces.
6.2.2 Programmatic Restoration Opportunities
"1F.r()gr:,lQ1
"j,~estora
. ~.G~~port!l'!1iti
Provide continued
efforts in surface water
quality improvement.
Manage, detain and
treat stormwater
discharging to the lakes.
Coordinate with King
County. to develop
BMPs with existing
property owners to
reduce runoff and
pollutant loading.
Protect adjacent
wetlands that serve to
improve water quality
to lakes.
Target wetland
restoration and
mitigation in areas
where they would
provide water quality
functions.
Encourage Low Impact
Development and
infiltration.
There are several general protection and restoration measures that can be applied to all of the
shoreline lakes in Federal Way. These include the following:
Protection Opportunities:
. Protect and maintain existing wetlands and riparian vegetation
. Protect existing forested areas in the parks and along the shoreline
. Prevent encroachment on functional riparian and wetland habitat
. Educate propertY owners on the importance ofthe nearshore zone and general lakeside
stewardship practices
. Promote development of nearshore, in-water structure such as downed trees
. Limit shoreline modifications
. Limit additional bulkheads; promote development of natural shorelines and habitats
. Include the use of shoreline setbacks for new construction and promote shorelirie
vegetation buffers
. Maintain public access to the lakes
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City of Federal Way Draft Shoreline Inventory & Characterization
Restoration Opportunities:
· Restore nearshore structUres or develop buffer zones where possible
· Expand buffer zones or improve buffer quality around wetlands where possible
· Direct stormwater runoff away from the lake or into containment ponds
· Highlight locations for effective storm water retrofitting
6.2.3 Site-Specific Restoration Opportunities
General locations of site-specific opportunities are shown on Figure 15 and described below.
More detail in site-specific restoration opportunities will be provided for the freshwater lakes in
the Restoration Planning element of the SMP update.
Steel Lake
The stewardship efforts of the Steel Lake Management District should be supported. This lake
also has a higher percentage of armored shoreline and this practice should be discouraged.
Existing bulkheads could be replaced with bioengineered shore protection. Although the park is
large for this size lake, little nearshore vegetation remains. Sections could be restored and used
as educational demonstrations for other property owners
Star Lake
Although most of the shoreline is developed, bulkheads are used minimally at Star Lake. This
should be showcased and additional armoring should be discouraged. Property owners could
also be further educated on the advantages of creating 15 to 20- foot wide native vegetation
buffers to protect the water quality at the lake.
Lake Dolloff
Since Lake Dolloff still has good riparian vegetation, it is important to maintain and enhance
current practices. Through continued education these buffer zones may continue to be kept in a
functional state. The floodplain boundaries should be used to keep development away from the
shoreline.
Lake Geneva
Along the eastern shoreline, special consideration should be given to creating a conservation
zone or strong development regulations. The steeper shoreline lends itself to tiered development,
which would greatly reduce the potential for recruitment of large woody debris. Currently, the
mature trees along this area provide excellent habitat.
North Lake
Support Weyerhaeuser's continued maintenance of the large conservation area on thewestern
shoreline. Continue to support the North Lake Steering Committee to promote lake stewardship
activities.
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. City of Federal Way Draft Shoreline Inventory & Characterization
Lake Killarney
Promote the importance of mature trees on properties, since most properties still contain multi-
storied vegetation. The southern shoreline is moderately steep, however development is not yet
tiered and should not be permitted.
Five Mile Lake
. With bulkheads existing already along at least 50 percent of the shoreline, it is most important to
limit any additional armoring of the shoreline. Property owners should also be educated about
the importance of maintaining mature trees in the riparian area.
7.0 DATA GAPS
Data gaps were identified through the preparation of this report and through this <(haracterization.
These gaps include:
. Information on surface water flow and lacustrine habitat for lakes in the PAA;and
. Site-specific information related to bulkheads, docks and lakeshore vegetation, especially
on the lakes within the P AA.
8.0 CONCLUSIONS
The City of Federal Way shoreline planning area includes both the coastal area ofPuget Sound
and seven freshwater lakes within the City and its P AA. There are 16.9 miles of shoreline
within the Federal Way planning area of which the Puget Sound coastal shoreline consists of 4.8
miles of shoreline, and freshwater lakes comprise 12.1 miles. Lakes included in the shoreline
planning area are Steel Lake, Star Lake, Lake Dolloff, Lake Geneva, North Lake, Lake
KiUarney, and Five Mile take.
8.1 Coastal Puget Sound
Bluffs, beaches, bays, and the mouths of several freshwater streams characterize the coastal /
nearshore shoreline. Feeder bluffs occur along approximately 37 percent of the coastal
shoreline, with most ofthese occurring near Dash Point State Park. The net-shore drift direction
is generally west to southwest, except at Dumas Bay where the drift cells converge to direct
sands and beach substrate into the Bay from both the southwest and the northeast.
Approximately 40 percent of the City's coastal shoreline has been modified with riprap, concrete
or wooden bulkheads. Structures in the shoreline can limit the amount of sediment transported
from upland areas to the beach, and are known to cause erosion and loss of some habitats such as
sand and fine gravel beaches. Currents naturally move sediments. across the beach and
alongshore in continual cycles, but these structures interrupt the natural supply and distribution
of sediments, causing a change in sediment composition within the nearshore area. However,
shoreline in Dumas Bay and Dash POint State Park are in a more natural condition, and coastal
processes are less altered.
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City of Federal Way Draft Shoreline Inventory & Characterization
The City's coastal shorelines are used by a variety of aquatic and terrestrial species including
fish, salmonids, birds, mammals, and a wide variety of invertebrates. Of special interest are
areas that provide habitat for federally listed species and species of local importance, including
bull trout (threatened), Chinook salmon (threatened), coho salmon, as well as great blue heron
nest sites. Forage fish such as surf smelt and sand lance (prey for salmonids) spawn on local
beaches.
The major land uses along the Federal Way coastal I nearshore shoreline are single-family
homes, parks, and public facilities. The City's most common shoreline use fs sillgle-family
residential, which occupies 55 percent of the coastal shoreline. Parks and public recreational
facilities occupy 18 percent of the coastal shoreline. These uses include Dash Point State Park,
Dumas Bay Park, Dumas Bay Centre, and Poverty Bay Park. These areas provide opportunities
for fishing, hiking and beach recreation. . .
The Puget Sound shoreline in Federal Way is characteristic of urbanizing shoreline elsewhere in
the region. Public access to the shoreline, recreational opportunities, and water-oriented uses
such as boating and fishing are provided in the City. In this regard, the goals of the SMA related
to public use and enjoyment of the State's shorelines are being met in the City.
Opportunities for site-specific habitat enhancement or restoration of shoreline ecological
functions have been identified based upon watershed information. In the coastal Puget Sound
areas, restoration focuses on removal of abandoned creosote pilings, debris and concrete from
the shoreline. Restoration in the coastal shoreline also focuses on bulkhead replacement with
soft-shore armoring and the use of native marine riparian plantings. These site-specific projects
would provide small but valuable efforts toward habitat enhancement and restoration of impaired
ecological functions.
8.2 Freshwater Lakes
The freshwater lakes in the City are located on abroad plateau in the eastern half of the City and
in the P AA. The plateau developed from glacial recessional deposits and tills. As the glaciers
melted, lakes formed in the scour areas. Lakes in the City drain to five main drainage basins
including 1) the Puget Sound, 2) the Lower Green River, 3) Mill Creek, 4) the White River, 5)
and the Hylebos. Lake shorelines have been modified with bulkheads and other bank protection,
but also have significant areas of natural shoreline conditions. On Steel Lake, Star Lake and Five
Mile Lake, approximately 20 to 50 percent of the shoreline has been modified with bulkheads.
Shoreline modifications are less apparent on the remaining lakes in the City.
The City's freshwater lake shorelines are used by a variety of aquatic and terrestrial species
including fish, birds, and mammals. Many of the lakes are stocked with trout, bass or other
game fish. Anadromous fish (including coho) are not likely present in the freshwater lakes due to
blockages to fish passage. Salmonids within the lakes are limited to stocked cutthroat trout. .
Bald eagle and loon also use the lakes with the shoreline planning area.
August 2006
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City of Federal Way Draft Shoreline Inventory & Characterization
Land uses along the City's freshwater lakes are primarily single-family residential and public
parks. Single-family residential use occupies between 55 and 80 percent of the shoreline on
most lakes, with the exception of North Lake (35 percent) and Five Mile Lake (32 percent).
Parks, boat ramps, and public facilities occupy 9 to 39 percent of the lake shorelines. Public
access to the lakes occurs via parks including Steel Lake Park, Lake Geneva Park, Lake
KiIlarney and Five Mile Lake Park, as well as several boat ramps owned by Washington
Department of Fish and Wildlife.
Development on a watershed scale has affected the shoreline by increasing impervious area in
uplands, resulting in increased peak flow velocities and volumes, impaired water quality, and
erosion in streams. On the lake shorelines, alterations have affected water quality, in lake habitat,
and downstream habitat for salmonids.
In the freshwater lakes, restoration opportunities include enhancement of lakeshore riparian areas
with native vegetation, removal or replacement of failing bulkheads, and protection of natural
vegetation when present.
Programmatic restoration opportunities include coordination with the City's surface water
management program~ public education and outreach to provide technical guidance for shoreline
homeowners, and the possibility for community-based restoration on private property..
Opportunities for enhancing public awareness and education could include installation of
informational kiosks at public parks and waterfront use areas. The City could also coordinate
with King County, the Water Resource Inventory Area (WRlA) 9 forum, and other regional or
Puget Sound-wide planning efforts to implement identified restoration policies and actions.
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City of Federal Way Draft Shoreline Inventory & Characterization
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between 1996 and 1999, Publication #01-06-019, Shorelands and Environmental
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for King County Department of Natural Resources and Parks. July 2002.
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15. no. 3; p. 3-11.
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August 2006
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City of Federal Way Draft Shoreline Inventory & Characterization
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rec/detaiI.asp?region=NPS# 12
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page 81
City of Federal Way Draft Shoreline Inventory & Characterization
Washington State Department ofNatl.ual Resources (WDNR). 2001. Washington State
ShoreZone Inventory. Nearshore Habitat Program, Washington State Department of
Natural Resources. Olympia, W A.
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Utilization: Volume I, Puget Sound Region. Washington State Department of Fish eries,
Olympia, Washington.
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Investigations Report 92-4098, prepared in cooperation with State of Washington
Department of Ecology, Regional Water Association of South King Co., and Seattle-
King County Dept. of Public Health, Tacoma.
August 2006
page 82
City of Federal Way Draft Shoreline Inventory & Characterization
APPENDIX A - MAP FOLIO
August 2006
Appendix A
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D City of Federal Way
Other Incorporated Area
Map Source: City of Federal Way, King County
Map Date: May, 2006
City of Federal Way
33325 8th Ave S,
PO Box 9718
Federal Way, WA 98063-9718
(253) 835-7000
www.cityoffederalway.com
5 Miles
This map is accompanied by NO warranties,
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I Figure 15
Federal Way Shoreline
Master Program
lake Restoration
Opportunities
Legend
[j Open Space
. Parks
~ Wetlands
~ Protection Opportunity
~ Restoration Opportunity
\~, ~ Other Location-Specific Action
o (Star Lake - General) Limit additional
bulkheads
f) (Star Lake - General) Encourage Buffers
e (Star Lake - General) Showcase properties
with 15-20' wide native vegetation buffers
e (Star Lake - General) Encourage continued
protection where native vegetation exists
^ (Steel Lake)
v Protect outlet and natural shoreline
o (Steel Lake) Restoration potential
G (Lake Dolloff) Protection Opportunity
o (Lake Dolloff) Encourage
. continued use of vegetation buffers
o (North Lake) Protection Opportunity
~ (North Lake) Possible protection
of south end of lake
~ (Lake Killarney) Continuation of
protection activities
~ (Lake Killarney) Encourage protection
of multi-storyied vegetation
~ (Lake Killarney - General) Encourage native.
vegetation
~ (Lake Geneva) Protection area due
. . to native shoreline and steep shoreline
~ (Five Mile Lake) Protection Opportunity
r---
--'I
I
Map Source: EnviroVision Corporation
Scale: City of Federal Way
o 0,25 0.5Mile I 33325 8th Ave S
~ ~ PO Box 9718
. . N Federal Way, WA 98063
Map Date: May, 2006 (253) 835-7000
~ Federal Way
This map is accompanied by NO warranties, and is simply
a graphic representation. For more information, visit us on
the web: www.cityoffederalway.com
July 13,2006
RECEIVED t3V
COMMUNITY DEVElOPMENT DEPARTMENT
JUL 14 2.006
TO: Sandra Lange, Department of Ecology .t~
FROM: Teresa Vanderburg, Adolfson Associates, Inc. .
...:. .'-
RE: City of Federal Way Grant Task 2. Deliverable
Inventory of Data Sources
Federal Way Shoreline Master Program Update
A first step in development of the shoreline inventory and characterization is determining
available spatial data for mapping and analysis, as well as existing reports and plans. Below is a
list of items identified to date. The list was initially prepared in March and circulated to the .
Federal Way Shoreline Technical Advisory Committee (TAC). As a member of the TAC, you
received an earlier version of this list at that time. This list has been revised based on review
and input by City staff and the Technical Advisory Committee.
The first table below lists mapping data layers typically used for analysis and preparation of the
map folio for shoreline inventory and characterizations. Many of the themes are city owned or
maintained. Others are standard from state resource agencies or King County. The City GIS
staff has reviewed and provided input on this list. Other items are identified as a data gap.
The second table below is a working bibliography of existing reports, plans, and studies we are
using. This list reflects input from the TAC, most notably WDFW and King County.
Table 1. Mapping Data Sources
:;Jt
,~=
Soils
Surficial Geology
Critical Areas (wetlands, geologic hazard
areas; flood hazard areas)
Streams
Drainage basin boundaries (surface water
and or storm water basins)
Topography
LI OAR data
Air Photos / Orthophotography
Historic air photos or scanned GLO maps
(T-sheets) .
WDFW PHS / Stream net
Parcels
Existing Land Use I Assessor data
Zoning
~~~;~~f!~~;f~~~
~~~~~~iii~~~~{;"~:~i~~:'f~r;',.~~:
Digital NRCS Soil Survey for King County
Digital surface geology layer for King County
City GIS files for wetlands (1998); King County GIS
data for landslide and erosion hazard areas;
Ecology GIS data for shoreline slope stability (WA
Coastal Atlas)
City GIS data (other sources include Washington
Trout and King County GIS)
City GIS (from surface water division)
5' contours - City GIS
WRIA 9 has data for Puget Sound nearshore
June 2002 imagery from King County/USGS
From UW Puget Sound River History Project and/or
UW Library
Included in Adolfson on-call area
City GIS data
City GIS data
City GIS data
Future land Use / Comp Plan land Use City GIS data
Designations
Impervious Area City GIS data
Vegetation / land Cover DATA GAP; could be described qualitatively from
existing reports (e.g., WRIA 9 marine inventory)
and aerial photo interpretation
Stormwater and wastewater pipes and Partial data from City Surface Water Division; some
outfalls data available from King County
Other utility lines (water, electric, natural DATA GAP; some data may be available from
gas, etc.) lakehaven Utility District (water and sewer)
Septic tanks DATA GAP; some data available online from King
County iMAP.
Contaminated Sites DATA GAP; some data available from Ecology..
2004 Water Quality Assessment (303d list) Adolfson has most current from Ecology
Historic / Cultural Resources DATA GAP; some info available online from state;
some data available from King County
. Parks, Trails, Playfields, Designated Open City GIS data
Space (any public access location to the
shoreline)
GIS data from WRJA 9 Marine Inventories/ GIS data created for these studies:
Studies I) Inventory and Assessment of Current and
Historic Beach Feeding Sources/Erosion and
Accretion Areas for the Marine Shorelines of
Water Resource Inventory Areas 8 & 9. 2005.
Prepared by Coastal Geologic Services, Inc~ for
WRIA 9 Steering Committee; and
2) Marine Shoreline Inventory Report for WRIA 9.
2004. Prepared by Anchor Environmental for WRIA
9 Steering Committee.
Table 2. Working Bibliography
~lto.Q'~.i~htTft.le, , .~', ~":Q~tlt abd;.
Comprehensive Plan . City of Federal Way
Parks and Open Space Plan City of Federal Way
Surface Water Management Comprehensive City of Federal Way
Plan or current Capital Improvement Plan
Prioritization of Marine Shorelines of Water
Resource Inventory Area 9 for Juvenile
Salmonid Habitat Protection and Restoration
Adolfson Library
Adolfson Library
Adolfson Library.
Anchor Environmental.
2006.
Adolfson Library
Inventory and Assessment of Current and
Historic Beach Feeding Sources / Erosion and
Accretion Areas for WRIAs 8 and 9, Appendix
D: Restoration Potentials
Salmon Habitat Plan - Makin Our Watershed
Coastal Geologic Services,
Inc. 2005, Prepared for
. King County Department of
Natural Resources and
Parks
Au ust 2005, Green /
Adolfson Library
or Server
Adolfson Libra
2
Fit for a King- Green I Duwamish and Central Duwamish and Central . or Server
Puget Sound Watershed Water Resource Puget Sound Watershed
Inventory Area 9 Steering Committee (WRIA Water Resource Inventory
9). Area 9 Steering Committee'
(WRIA 9).
2005-2007 Puget Sound Conservation and . Puget Sound Action Team Adolfson Library
Recovery Plan. (PSA T). 2005 or Server
Overview of Puget Sound Nearshore Project Puget Sound. Nearshore www. pUQetsoun
Project (PNSP). 2002, dnearshore.orQ
Guidance for Protection and Restorationof the Puget Sound Nearshore www.puQetsoun
Nearshore Ecosystems of Puget Sound, Project (PNSP). 2004a dnearshore,orQ
Guiding Restoration Principles Puget Sound Nearshore www. pUQetsoun
Project (PNSP), 2004b. dnearshore.orQ
Section 905(b) Analysis: General Investigation United States Army Corps Adolfson Library
Reconnaissance Study, Puget Sound of Engineers (USACOE). or Server
Nearshore, Washington 2000
Restoration Planning and the 2003 Shoreline Washington Department of Adolfson Library
Management Guidelines. Ecology (Ecology). 2004 or Server
Marine Shoreline Inventory Report - WRIA 9 Anchor Environmental, Adolfson Library
L.L.C. 2004 or Server
Net shore-drift of King County, Washington: Chrzastowski, M.J., 1982 Adolfson Library
Western Washington University Master of - hard copy
Science thesis
A marine and estuarine habitat classification Dethier, M. N. 1990 Adolfson Library
system for Washington State. or Server
Geology and ground-water resources of Luzier, J. E., 1969. Adolfson Library
southwestern King County, Washington: . or Server
Washington Department of Water Resources
Water
Shoreline armoring effects on physical coastal Macdonald, Keith, Adolfson Library
processes in Puget Sound, Washington Simpson, David, Paulsen, or Server
Bradley, Cox, Jack, and
Gendron, Jane, 1994
National Wetlands Inventory, Federal Way, United States Department Adolfson Library
Washington 7.5-minute USGS Quadrangle of the Interior (USDI). or Server
1987a
Washington State S.horeZone Inventory Washington State Adolfson. Library
Department of Natural or Server
Resources (WDNR). 2001
A Catalog of Washington Streams and Salmon Williams, R. W., R. M. Adolfson Lib.-
Utilization - Volume I, Puget Sound Region Laramie, and J. J. Ames. hard copy
1975
Occurrence and quality of ground water in Woodward, D.G., Packard, Adolfson Library
Southwestern King County, Washington FA, Dion, N.P., and or Server
Sumioka, S.S., 1995
Natural Heritage Plan. Washington State Adolfson Library
Department of Natural
3
. Resources (WA DNR). or Server
2003
Steel lake Management District 2005 Annual City of Federal Way, Public Envirovision
Report Works Department, Surface
Water Management
Division. 2005
Steel lake IA VMP City of Federal Way, Public EnvirovisiQn
Works Department, Surface
Water Management
Division. 2004
Lake Dolloff Survey EnviroVision. 2004 Envirovision
Water Quality of Small lakes and Streams, King County Metro. Water Envirovision
Western King County 1990-1993 Pollution Control
Department. 1994
A Trend Report on King County Small lakes King County WlRD. 2001 Eiwirovision
King County Lake Monitoring Report. Volunteer King County DNRP, WRLD. http://dnr.metrok
Lake Monitoring Results for the Water Year 2005 (data from 1993- c.Qov/wlr/waterre
2002-2003 present available from King s/smlakes/lkmon
County) 03.htm
Lake Killarney IA VMP King County DNRP, WRLD. Envirovision
1997
North Lake IAVMP and SWM 2005 Annual King County. DNRP. Envirovision
Report WRLD. 2004
Lake Bathymetry Washington State http://www.ecy.w
Department of Ecology. a.Qov/services/Qi
1995 s/data/data. htm#
lake bath
Motorized Boat Launch and Public Moorage Washington State http://www,iac.w
Facilities in Washington State Interagency Committee for a. Qov/maps/boat
Outdoor Recreation. 2000 .htm
Lakes Monitored by Ecology's Lake Water Washington State http://www.ecy.w
Quality Monitoring Program from 1989 through Department of Ecology a. Qov/proQramsl
1997. eap/fw lakes/lk
Iist.html
Lake Killarney - Lake Water Quality Monitoring Washington State http://www.ecy.w
Station Department of Ecology a.Qov/proQramsl
eap/wrias/lak/10.
html
WRIA 9 Strategic Assessme.nt Report- King County Water and Adolfson library
Scientific Foundation for Salmonid Habitat Land Resources Division. or Server
Restoration 2004.
White PapelTs: Overwater Structures, Shoreline Washington Department of Available online
Modifications, Dredging. Fish and Wildlife (WDFW)
Low Impact Development Technical Guidance Puget Sound Action Team Available online
Manual for Puget Sound (PSAT). Jan. 2005
WDFW Management Recommendations - Washington Department of Available online
4
Riparian Fish and Wildlife (WDFW)
WDFW Integrated Streambank Protection Washington Department of Available online
Guidelines Fish and Wildlife (WDFW)
Regional Approaches to Address Coastal Washington State Available online
Erosion Management, Coastal Erosion Department of Ecology.
Management Studies, Volumes 1, 5, 7, & 9, Publications # 94-82, # 94-
80, #94-78, # 94-74.
Management Options for Unstable Coastal Department.of Ecology. Available online
Bluffs in Puget Sound, Washington. Coastal June 1994. Publication #
Erosion Management Studies, Volume 8. 94-81.
Alternative Bank Protection Methods for Puget Ian Zelo, Hugh Shipman, Adolfson Library
Sound Shorelines. and Jim Brennan. May
2000. DOE. Publication #
00-06-012.
Draft Puget Sound Salmon Recovery Plan. Available online
Volume One. Shared Strategy.
Annual Inventory of Sheilfish Harvest Areas Washington State Available online
Department of Health.
Spawning Areas of the Pacific herring (clupea), Penttila, D.E. 1995/1999. Available online
surf smelt (hypomesus) and Pacific sand lance.
(ammodytes) in Central Puget Sound,
Washington.
Effects of urbanization on small streams in the Curtis May, etal, 1997. Available online
Puget Sound lowland ecoregion.
5
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2
CHAPTER #. SHORELINE MASTER PROGRAM
Purpose
The Shoreline Management Act (SMA) identifies eight elements that, if appropriate to
the community, are to be dealt with in the development of area-wide shoreline goals.
They include: shoreline use, economic development, public access, conservation,
recreation, historicaVcultural,.circulation, and flood prevention. Master programs are also
encouraged to include any other elements which, because of present uses or future needs,
are deemed appropriate to effectuate the policy of the SMA.
Residential land use of shorelines of 1. he state within Federal Way makes up the largest
share of the developed shorelines in the City. Undeveloped shoreline is a mix oflarger
parcels designated as parks and open space areas and smaller lots presently zoned to
allow for residential use.
The following comprehensive set of shoreline goals and policies provide the foundation
and framework on which the balance of the master program has been based. The policies
contained herein are enforced through Article III, Shoreline Management, and any other
applicable chapters of the FWCC.
Shoreline Use Element
This element addresses the distribution, location, and extent of use of shorelines and
adjacent areas for housing, recreation, transportation, office, public buildings, utilities,
education, and other uses. The shorelines in Federal Way are more widely used for
residential purposes than for any other use. Much of the undeveloped shoreline is
privately owned, subdivided into small lots, and zoned to permit residential development.
Goal
SMPGl Shoreline areas shall permit a variety of development types in accordance
with the City's zoning and Comprehensive Plan designations. Designs,
densities. and locations for all allowed uses and developments should
consider physical and natural features of the shoreline and should avoid, to
the greatest extent possible. adverse effects on shoreline ecological functions.
Policies
SMPPl
Shoreline land and water areas particularly suited for specific and appropriate'
uses should be designated and reserved for such uses.
Shoreline land and water uses should satisfy the economic, social, and
physical needs of the regional population, but should not exceed the physical
carrying capacity of the shoreline areas.' .
Like or compatible shoreline uses should be clustered or distrjbuted in a
rational manner, rather than allowed to develop haphazardly.
SMPP2
SMPPJ
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page I
EXHIBIT
PAGE
.E
OF
12/15/2006
".
SMPP4 Multiple uses of shoreline should be encouraged where location and
integration of compatible uses or activities are feasible.
SMPP5 Shoreline ecological functions should be protected from uses Or activities
that will have an adverse effect on them.
SMPP6 Non-residential uses or activities that are not shoreline dependent should be
encouraged to . locate or relocate away from the shoreline.
SMPP7 F ederal Way shall consider the goals, objectives, and policies of the shoreline
master program in all land use management decisions regarding the use or
development of adjacent uplands where such use or development may have
an adverse effect on designated shorelines.
SMPPS Development should be excluded from shoreline areas known to contain
development hazards or which would adversely impact designated critical
areas as identified in Chapter 18, Division 6.ofthe FWCC.
a. All development should be prohibited within the toO-year floodplain.
b. Development should be prohibited in ~horeline areas having severe or
very severe landslide hazard unless demonstrated that proposed
development would be safe and would not impact natural shoreline
functions.
c. All development should be regulated in shoreline areas with slopes of 40
percent or greater.
d. Shoreline areas containing other potential hazards (e. g., geological
conditions, unstable subsurface conditions, erosion hazards, or
groundwater or seepage problems) should be regulated as necessary to
avoid unsafe development and disturbance of sensitive areas.
e. The burden of proof that development of these areas is feasible, safe, and
ecologically sound is the responsibility of the developer.
Goal
SMPG2 Residential use of shoreline areas should be continued and encouraged,
allowing a variety of housing types. New development or redevelopment of
residential uses, should avoid, to the greatest extent possible, adverse effects
on shoreline ecological functions.
Policies
SMPP9
Residential developments should avoid or have minimal impact on the land
and water environment of the shoreline and minimize visual and physical
obstruction. Unavoidable impacts to the shoreline environment from
residential development should be mitigated to assure no net loss of shoreline
ecological functions.
a. Residential development in designated critical areas or their associated
buffers should be regulated as required under the City's critical areas
regulations.
b. Residential development on piers or over water should not be pennitted.
DRAFT Goals and Policies 'SI"', t'-~~$ ~." ".. ,
Federal Way Shoreline Master"IUan.. ~~ ~ iC.\ E f":~ ) "L ;:
Prepared for Ecology Review, B~~fllber 2006 '~'''', page 2
. , """?"'"' ".. .".~ li....., "'" .., .'~ ," ,
12/15/2006
c. Landfill for residential developrnent that reduces water surface or
floodplain capacity should not be pennitted.
. d. In residential developments the water's edge should be kept free of
buildings.
e. Development standards should require the retention of natural shoreline
vegetation and other natural features of the landscape to the greatest
extent possible during site development and construction.
SMPP10 Residential use of shorelines should not displace or encroach upon water-
dependent shoreline uses.
SMPPll Residential densities in shoreline areas should be consistent with zoning and
should consider physical capabilities of the shoreline areas and public
services requirements when considering new plats or rezoning applications.
a. Subdivisions and new development should be designed to adequately
protect the water and shoreline aesthetic characteristics.
b. New residential development should only be allowed in those shoreline
areas where the provision for sewage disposal and drainage ways are of
such a standard that adjoining water bodies would not be adversely
affected by pollution or siltation.
c. New residential development or redevelopment along shorelines should
be set back from the ordinary high water mark far enough to make
unnecessary such protective measures as filling, hard annored bulk
heading, construction of groins or jetties, or substantial regrading of the
site. Where a site cannot be developed without the use of the protective
measures listed above due ~o other site constraints, the least ecologically
harmful method shall be utilized.
d. Residential developments should be designed to enhance the appearance
of the shoreline and not substantially interfere with the views from public
property or access to the water.
SMPP12 Residential subdivisions in shoreline areas should provide public pedestrian
access to the shorelines within the development in accordance with public
access and recreation element of this master program.
SMPP13 Developers of recreational projects such as summer homes, cabins,
campgrounds, and similar facilities should satisfactorily demonstrate:
a. The suitability of the site to accommodate the proposed development
without adversely affecting the shoreline environment and water
resource.
b. Adequate provisions for all necessary utilities, including refuse disposal.
Goal
SMPG3 Shoreline areas designated by the Comprehensive Plan to allow for
commercial development shall permit a variety of commercial and office
park development types. New development or expansion of existing
commercial and office uses should avoid, to the greatest extent possible,
adverse effects on shoreline ecological junctions.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared forEcology Review, December 2006
Page 3
12!lS/2006
Policies
SMPP14 Consideration should be made of the effect a structure will have on scenic
value.
SMPP15 Commercial structures and ancillary facilities that are not shoreline
dependent or water-oriented should be set back from the water's edge and
designed to avoid adverse impacts to shoreline ecological functions.
SMPP16 The use of porous materials or other low impact development design
alternatives should be encouraged for paved areas to allow water to penetrate
and percolate into the soil. Use of holding systems should be encouraged to
control the runoff rate from parking lots and rooftops.
SMPP17 Commercial development located within shoreline areas should be
constructed to withstand normal rain and flooding conditions without
contributing pollution to the watercourse or shoreline.
SMPP18 Commercial development that is not water-dependent should provide a buffer
zone of native vegetation for erosion control.
SMPP19 Commercial aquaculture activities should be prohibited.
Goal
SMPG4 Regional and subregional utility facilities, including communications (radio.
TV, and telephone), energy distribution (petroleum products, natural gas,
and electricity), water, sanitary sewers, and storm sewers should be allowed
in shoreline areas. Design. location. construction, and maintenance of utility
facilities should avoid, to the greatest extent possible, adverse effects to
shoreline ecological functions.
Policies
SMPP20 Utilities that could allow for growth should not be extended into or along
shorelines without prior approval of such extension by appropriate land use
authority .
SMPP21 Utilities located in shoreline environments inappropriate for development
should not make service available to those areas.
. SMPP22 In developed shorelines not served by utilities, utility construction should be
encouraged to locate where it can be shown that water quality will be
maintained or improved.
SMPP23 Federal Way should be consulted prior to application for construction of
regional utility facilities to be located in or along shorelines.
SMPP24 Utility corridors crossing shorelines should be encouraged to consolidate and
concentrate or share rights-of-way where:
a. Public access or view corridors would be improved.
b. Concentration or sharing would not hirider the ability of the utility
systems to be installed, operated, or maintained safely.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 4
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c. Water quality would be as good or'better than if separate corridors were
present.
SMPP25 Public access should be encouraged where rights-of-way for regional utility
facilities cross shorelines in the City and where public safety and facility
security would not be compromised.
SMPP26. New utility facilities should be located so as to neither require extensive
shoreline protectiori nor to restrict water flow, circulation, or navigation.
SMPP27 New utility facilities and rights-of-way' should be located to preserve the
natural landscape and minimize conflicts with present and planned uses of
the land on which they are located.
SMPP28 New utility facilities and rights-of-way should be located and designed to
minimize detrimental visual impacts from the water and adjacent uplands.
SMPP29 New freestanding personal wireless service facilities are discouraged from
locating within the shoreline environment.
Goal
SMPG5 Encourage soft shore armoring and bioengineering solutions to limit
traditional hard shoreline armoring techniques such as rip rap or
vertical bulkheadingfor shoreline protection or stabilization to reduce
adverse impacts to development caused by current, flood, wake, or
wave action.
Policies
SMPP30 Shoreline armoring, including replaceme!lt of existing hard bulkheads,
should be allowed only if it is clearly demonstrated that shoreline armoring is
necessary to protect existing improvements. Repair of existing shoreline
armoring structures should be permitted.
SMPP31 Structural solutions to reduce shoreline erosion should be allowed only after
it is demonstrated that nonstructural solutions such as bioengineering or soft-
shore armoring would not be able to protect exi~ting development. .
SMPP32 Planning of shoreline erosion control or bank stabilization should encompass
sizable stretches of lake or marine shorelines. This planning should consider
off-site erosion, accretion, or flood damage that might occur as a result of
shoreline protection structures or activities.
SMPP33 Shoreline erosion control or bank stabilization on marine and lake shorelines
should not be used as a means of creating new or newly developable land.
SMPP34 Shoreline stabilization structures should allow passage of ground and surface
waters into the main water body.
SMPP3S Shoreline erosion control or bank stabilization should not reduce the volume
and storage capacity of rivers~ streams, and adjacent wetlands or flood plains.
SMPP36 Whenever shoreline stabilization or erosion control is needed, bioengineered
alternatives such as natural benns and erosion control vegetation plans
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 5
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should be favored over hard surfaced structural alternatives such as concrete
bulkheads and sheet piles.
SMPP37 The burden of proof for the need for shoreline stabilization to protect existing
or proposed redevelopments rests on the applicant.
SMPP38 Shoreline stabilization that would result in the need for new or increased
shoreline stabilization on the same or other affected properties where there
has been no previous need should not be allowed. .
SMPP39 New development should be designed and located so as not to require hard
armoring or other structural shoreline stabilization.
SMPP40 Areas of significance in the spawning, nesting, rearing, or residency of
aquatic and terrestrial biota should be given special consideration in review
of proposed shoreline protection activities.
SMPP41 Shoreline protection activities should be discouraged in areas where they
would disrupt natural feeder bluffs processes important for maintaining
beaches.
Goal
SMPG6 Piers and moorages should be allowed when associated with residential,
recreational, or other public facilities. The design, location, and
construction of any pier or moorage should, avoid, to the' greatest extent
possible, adverse effects on shoreline ecological functions.
Policies
SMPP42 Open pile pier construction should be preferred where there is significant
littoral drift, where scenic values will not be impaired, and where minimal
alteration to the shoreline and minimal damage to aquatic resources can be
assured.
SMPP43 Piers should be discouraged where conflicts with recreational boaters and
other recreational water activities would be created by pier construction.
SMPP44 The random proliferation of single purpose piers should be discouraged.
Preference should be given to shared use of piers in all shoreline areas.
SMPP45 Temporary moorages should be permitted for vessels used in the construction
of shoreline facilities. The design and construction of such moorages shall be
such that upon termination of the project, aquatic habitat can be returned to
original condition within one year. with no adverse impact to the environment
or cost to the public.
SMPP46 Shoreline structures that are abandoned or structurally unsafe should be
removed.
SMPP47 Piers, docks, buoys, and other moorages should be located and designed to
minimize adverse effects on wildlife and aquatic life, water quality, unique
and fragile areas, submerged lands, and shoreline vegetation.
SMPP48 Moorage buoys should be preferred over floating and pile constructed piers
on all tidal waters.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 6
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Public Access and Recreation Element
. This element addresses the preservation and expansion of all types of public access and
recreational opportunities through programs of acquisition, development, and various
means of less-than- fee acquisition.
Goal
SMPG7 Increase public access to shoreline areas provided that private rights. public
safety, and the natural shoreline character are not adversely affected.
Policies
SMPP49 Development of public access should respect and protect the enjoyment of
private rights on shoreline property.
SMPP50 Public access should be maintained and regulated,
a Public access should be policed and improved consistent with intensity
of use.
b. Provisions to restrict access as to nature, time, number of people, and
area may be appropriate for public pedestrian easements and other public
access areas where there are spawning grounds, fragile aquatic life
habitats, or potential hazards for pedestrian safety,
SMPP51 Design of access should provide for the public health, safety, and enjoyment.
a. Appropriate signs should be used to designate publicly owned shorelines.
b. Pedestrian and non-motorized physical and visual access to the shoreline
should be encouraged.
c. Public access to and along the water's edge should be made available in
publicly,owned shorelines in a manner that protects shoreline ecological
functions.
SMPP52 Acquisition and development of new shoreline public access locations should
be consistent with overall parks and open space planning goals and policies.
a. Acquisition and development of shoreline properties should be consistent
with criteria and standards as part of an overall parks and open space
master plan.
b. Where appropriate, utility and transportation rights-of-way on the
shoreline should be made available for public access and use, consistent
with the shoreline use and circulation element policies.
c. Where appropriate, publicly-owned street ends that abut the shoreline
should be retained and/or reclaimed for public access, consistent with the
circulation element policies. .
d. Shoreline recreational facilities and other public access points should be
connected by trails, bicycle pathways, and other access links where
possible.
DRAFT Goals and Policies
Federal Way Shoreline MasterPlan
Prepared for'Ecology Review, December 2006
Page 7
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SMPP53 Public access should be provided in new shoreline developments.
a. Incentives should be used to encourage private property owners to
provide public shoreline access,
b. Public pedestrian easements should be considered in future land use
authorizations, and in the case of projects along lakes, streams, ponds,
and marine lands, whenever shoreline features are appropriate for public
use. Shorelines of the City characterized by the following should be
considered for' pedestrian easements:
I. Areas of significant, historical, geological, and/or biological features
and landmarks.
2. Areas presently being legally used, or historically having been
legally used, by the public along the shoreline for access. .
3. Where public funds have been expended on or related to shoreline
developmen~.
SMPPS4 Shorelines in the City should beavaHable to all people for passive use, visual
access, and enjoyment.
a. The City should preserve and provide publicly accessible viewpoints,
lookouts, and vistas of shorelines.
b. New developments should minimize visual and physical obstruction of
the water from adjacent roads and public properties.
SMPP55 Physical and/or visual access to the water should use steep slopes, view
points from bluffs, stream valleys, and features of special interest where it is
possible to place pathways consistent with public safety and without
requiring extensive flood or erosion protection.
Goal
SMPG8 Provide additional shoreline dependf!nt and water oriented recreation
opportunities that are diverse. convenient, and adequate for the regional
population consistent with the carrying capacity of the land and water
resources.
Policies
SMPP56 Areas containing special shoreline recreation qualities not easily duplicated
should be available for public use and enjoyment.
a. Opportunities should be provided for the public to understand natural
shoreline processes and experience natural resource features.
b. Public viewing and interpretation should be encouraged at or ne.ar
governmental shoreline facilities when consistent with security and
public safety.
SMPP57 Shoreline recreational use and development should enhance environmental
quality with minimal adverse effect to natural resources.
DRAFT Goals and Policies
Federal Way Shofeline Master Plan
. Prepared for Ecology Review, December 2006
Page 8
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-.
a. Shoreline recreational facilities shall be developed at a level of use and
intensity that is consistent with and does not exceed the carrying capacity
of the site.
b. Overall design and development in shoreline recreational areas should be
sensitive to the physical site characteristics and be consistent with the
level of use in the area concerned.
c. Recreation areas and ancillary facilities on or adjacent to the shoreline
should have adequate surveillance and maintenance.
d. Non-water oriented recreational facility development should be setback
from the water's edge, except where appropriate in high intensive
shoreline use areas.
SMPP58 The provision of adequate public shoreline recreation lands should be based
on an acquisition plan that is consistent with overall goals for enhancing
public access to the CIty's shorelines.
SMPP59 Existing buildings that enhance the character of the shoreline should be
incorporated into recreation areas wherever possible.
SMPP60 A balanced variety of recreational opportunities should be provided for
people of different ages, health, family status, and financial ability.
a. Shoreline recreation areas should provide opportunities for different use
intensities ranging from low (solitude) to high (many people).
b. Opportunities for shoreline recreational experiences should include
developing access that accommodates a range of differences in people's
physical mobility, capabilities, and skill levels.
c. Recreational development should meet the demands of population
growth consistent with the carrying capacity of the land and water
resources.
Goal
SMPG9 Recreational experiences that depend on, or utilize, the shoreline (including:
harvesting activities of fish, shellfish, fowl, minerals, and driftwood; various
forms of boating, swimming. and shoreline pathways; and watching or
recording activities, such as photography, painting, or the viewing of water
dependent activities) shall be encouraged within parks and other public
access areas, given that they avoid, to the greatest extent possible. adverse
effects on shoreline ecological functions.
Policies
SMPP61 Underwater parks should be extensions of shoreline parks, and, whenever
possible, be created or enhanced by artificial reefs where natural conditions
or aquatic life could be observed with minimal interference.
SMPP62 During storm events, hazardous conditions, or emergencies, temporary use of
public recreational shoreline areas by boaters should be allowed.
SMPP63 Prime-fishing areas should be given priority for recreational use.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 9
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SMPP64
Recreational shellfish harvesting should be allowed on public beaches
subject to rules, regulations, and periodic closures by Washington
Department of Health and or Washington Department of Fish and Wildlife.
Boating activities that increase shore erosion should be discouraged.
Effective interpretation should be provided to raise the quality of visitor
experiences and provide an understanding of aquatic and shoreline reso,urce.
SMPP65
. SMPP66
Conservation and Restoration Element
This element promotes and encourages the conservation of natural shoreline resources
and shoreline ecological functions, considering, but not limited to, such characteristics as
scenic vistas, parks and open space, fish and wildlife habitat, beaches, feeder bluffs,
estuaries and other valuable natural or aesthetic features. Additiomilly, this element
promotes and encourages restoration of shoreline functions and ecological processes that
- have been impaired as a result of past development activities.
Goal
SMPGIO Preserve and protect the ecological functions provided by designated critical
areas located in the shoreline.
Policies
SMPP67 Manage designated critical areas in the shoreline - such as critical aquifer
recharge areas and wellhead protection areas, frequently flooded areas,
geologically hazardous areas, regulated wetlands, and streams - in a manner
consistent with the policies contained in Chapter 9, Natural Environment, of
the Comprehensive Plan.
SMPP68 Develop standards, buffers, and mitigation requirements for designated
critical areas in the shoreline consistent with city-wide regulations unless
more protective measures are required to protect shoreline ecological
functions.
Goal
SMPGll Assure preservation of unique and non-renewable natural resources and
assure conservation of renewable natural resources for the benefit of existing
and future generations and the public interest.
Policies
SMPP69 All new development and activity in or adjacent to shoreline areas should be
designed, constructed, and operated as to not cause significant adverse
impacts to ground or surface water quality.
SMPP70 Shorelines that are of unique or valuable natural character should be
considered for acquisition. Subsequent management of such areas should
prote~t or enhance shoreline ecological functions..
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 10
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SMPP71 All renewable natural resources should be managed so that use or
consumption does not exceed the natural rate of replenishment.
SMPP72 Resource conservation should be an integral part of s.horeline planning.
a. All future shoreline development should be planned, designed, and sited
to minimize adverse impact upon the natural shoreline environment and
ecological functions.
SMPP73 Scenic and aesthetic qualities and ecological functions of shorelines should
be recognized and preserved as valuable resources.
a. When appropriate, natural flora and fauna should be preserved.
b. In shoreline areas, the natural topography should not be substantially
altered.
c. Shoreline structures should be sited and designed to minimize view
obstruction from public properties and should be visually compatible
with the shoreline character.
d. Wildlife and aquatic habitats, Including spawning grounds, should be
protected.
SMPP74 Resources should be managed to enhance the environment with minimal
adverse effect.
a. Shoreline, in-water and over-water activities and development should be
planned, constructed, and operated to minimize adverse effects on the
natural processes of the shoreline, and should maintain or enhance the
quality of air, soil, natural vegetation, and water on the shoreline.
b. Use or activity which substantially degrades the natural resources or
ecological functions of the shoreline should not be allowed without
mitigation as required under FWMC Chapter 18; Environmental
Protection.
SMPP75 Critical saltwater and freshwater habitats (critical habitats) support valuable
recreational and commercial fisheries and should be protected for their
importance to the aquatic ecosystem as well as state and local economies.
a. Non-water-dependent and non-water-related uses, activities, structures,
and landfills should not be located in critical habitats.
b. Where uses, activities, structures, and landfills must locate in critical
habitats, impa<;:ts on these areas should be lessened to the maximum
extent possible. Significant unavoidable impacts should be mitigated by
creating in-kind replacement habitat near the project where feasible.
Where in-kind replacement mitigation is not feasible, rehabilitation of
out-of-kind or off-site degraded habitat should be required. Mitigation
proposals should be developed in consultation with the City, the State
Department ofFish and Wildlife, and any affected Indian Nations;
c. Development that is outside critical habitats that has the potential to
significantly affect said habitats should be located and designed as to not
create significant negative impacts to said habitats.
d. Whenever feasible, bioengineering should be used as the bank protection
technique for all streams considered .to have critical habitat.
DRAFT Goals and Policies
Federal Way Shorefine Master Plan
Prepared for Ecology Review, December 2006
Page II
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e. Whenever feasible, open pile bridges should be used for all water
crossings over areas considered critical habitat.
f. . Impervious surfaces should be minimized in upland developments to
reduce stormwater runoff peaks. Structures and uses creating significant.
impervious surfaces should include stormwater detention systems to
reduce stormwater runoff peaks.
g. The discharge of silt and.sediments into waterways shall be minimized
during in-water and upland construction.
h. Adopt-A-Stream programs and similar efforts to rehabilitate critical
habitats should be encouraged.
I. Fishery enhancement projects should be encouraged where they will not
significantly interfere with other beneficial uses.
J. Project proponents should contact the Habitat Division of 1. he State
Department of Fish and Wildlife and affected Indian Nations early in the
development process to determine if the proposal will occur in or
adjacent to critical habitat.
k. When reviewing permits for uses, activities, and structures proposed in,
over, or adjacent to marine waters, streams, wetlands, ponds connected to
streams, or any other shoreline area, City staff should contact the Habitat
Division of the State Department of Fish and Wildlife to determine if the
proposal will occur in or affect any adjacent critical habitats. Staff
should also contact affected Indian Nations.
Goal
SMPG12 Develop regional solutions with other jurisdictions, tribes and interested
parties to resolve the challenge of protecting shoreline ecological functions
while also proiecting shoreline developments.
PoliCies
SMPP76 Continue to work with the State, King County, Watershed Resource
Inventory Area (WRIA) 9, and other governmental and non-governmental
organizations to explore how local governments can contribute to the
preservation and restoration of ecological processes and shoreline functions.
SMPP77 Continue to work with the WRIA 9 to restore shoreline habitats and seasonal
ranges that support listed endangered and threatened species, as well as other
anadromous fisheries.
Goal
SMPG13 Pursue projects to restore and enhance shoreline habitats. functions and
processes on private and publicly owned lands.
Policies
SMPP78 Prioritize restoration and enhancement first based upon the greatest net
ecological benefit, as compared to the project cost.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
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SMPP79 Focus restoration and conservation activities on public parks and open space
lands for public enjoyment.
SMPP80 Work with owners of other publicly-owned land, such as Washington State
Parks to encourage restoration and enhancement projects, including funding
strategies.
SMPP81 Work with the public and other interested parties to prioritize restoration
opportunities identified in Shoreline Inventory and Characterization Report.
SMPP82 Promote shoreline vegetation restoration, and the control of invasive weeds
and nonnative species, to enhance marine riparian and freshwater lakeshore
habitats.
SMPP83 Promote shoreline vegetation restoration to reduce the hazard of slope
failures or accelerated erosion.
SMPP84 Develop a program to implement restoration projects, including funding
strategies.
SMPP85. Monitor and adaptively manage restoration projects.
Goal
SMPG14 Evaluate potential shoreline impairments when they are identified by the
community or stakeholders,
Policies
SMPP86 Collect information to evaluate and assess potential shoreline degradation and
impairments observed by the community.
SMPP87 Develop strategies to address impairments to shorelfne functions through
restoration actions, if appropriate.
SMPP88 Restoration projects with broad ecological benefit will.be given greater
weight or priority than projects with.localized benefits.
. Goal
SMPG15 Encourage voluntary restoration projects on private property in degraded
shoreline environments,
Policies
SMPP89 Create incentives that will make it economically or otherwise attractive for
development proposals to integrate shoreline ecological restoration into
development projects.
SMPP90' Encourage protection, enhancement, or restoration- of native riparian
vegetation through incentives and non-regulatory programs.
SMPP91 Promote bioengineering and/or soft engineering alternative design
approaches to shoreline stabilization and provide technical guidance to
shoreline landowners.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 13
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SMPP92 Establish public education materials to provide shoreline landowners
technical assistance about the benefits of native vegetation plantings.
SMPP93 identify and pursue funding sources for shoreline restoration actions on
pri vate lands.
Goal
. SMPG16 Provide ample opportunity for the public to learn about the ecological
aspects and community values of the City's shorelines.
Policies
SMPP94 Explore opportunities with other educational organizations and agencies to
develop an on-going program of shoreline education for all ages.
SMPP95 Identify areas where kiosks and interpretative signs can enhance the
educational experience of users oftne shoreline.
SMPP96 Develop strategies to fund these projects.
Historic and Cultural Resources Element
This element addresses identification and preservation of historic and cultural resources
that are located in or associated with Federal Way's shorelines. Such resources may
include historic structures or buildings, historic use or activities in the shoreline, and
archaeological resources.
Goal
SMPG17 Identify. protect. preserve, and restore important archaeological. historical.
and cultural sites located in or associated with Federal Way's shorelines for
scientific and educational purposes.
Policies
SMPP97 Manage cultur~l and historic resources in the shoreline consistent with city-
'wide policies for treatment of such resources in the Comprehensive Plan.
SMPP98 Recognize that shoreline areas are of moderate to high probability for
archaeological resources and require appropriate review and site
investigation for proposed development or modifications.
Circulation Element
This element deals with the location and extent of existing and proposed thoroughfares,
transportation routes, and other public facilities; and coordinating those facilities with
shoreline uses.
Goal
SMPG18 Circulation systems in shoreline areas should be limited to those that are.
shoreline dependent or would serve shoreline dependent uses or those that
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 14
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must pass through the shoreline environment. The environment shall be
protected from any significant adverse effects of circulation systems required
in the shoreline environment.
Policies
SMPP99 New surface transportation development should be designed to provide the
best possible service with the least possible infringement upon the shoreline
environment.
a. New transportation facilities and improvements to existing facilities that
substantially increase levels of air, noise, odor, visual, or water pollution
should be discouraged.
b. Transportation corridors should be designed to harmonize with the
topography and other natural characteristics of the shoreline through
which they traverse.
c. New surface transportation facilities in shoreline areas should be set back
from the ordinary high water mark far enough to make unnecessary such
protective measures as rip-rap or other bank stabilization, landfill,
bulkheads, groins, jetties, or substantial site regrade.
d. New transportation facilities crossing lakes, streams, wetlands, o~ other
critical areas should be encouraged to locate in existing corridors, except
where any adverse impact can be minimized by selecting an alternate
corridor.
e. Shoreline circulation systems should be adaptable to changes in
technology.
SMPPIOO Circulation systems should be located and attractively designed so as not to.
unnecessarily or unreasonably pollute the physical environment or reduce the
benefits people derive from their property.
a. Motorized vehicular traffic on beaches and other natural shoreline areas
should b~ prohibited.
b. Transportation facilities providing access to shoreline developments
should be planned and designed in scale and character with the use
proposed.
c. New transportation facilities should minimize total impervious surface
area by generally being oriented perpendicular to the shoreline where
topographic conditions will allow.
SMPPIOl Circulation systems should be designed to enhance aesthetic experiences
through creating shoreline vista and access points and encouraging
alternative modes of transportation.
SMPPI02 New transportation developments in shoreline areas should provide turnout
areas for scenic stops and off road rest areas where the topography, view, and
natural features warrant, consistent with the public access and recreation
element policies.
SMPPI03 Shoreline roadway corridors with unique or historic significance, or of great
aesthetic quality, should be retained and maintained for those characteristics.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
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SMPPI04 Shoreline circulation routes should provide for non~motorized means of
travel and should incorporate multi modal provisions where public safety can
be assured.
SMPPIOS Shoreline roadways should have a high priority for arterial beautification
funds. .
SMPPI06 Pedestrian access should be built where access to public shorelines is
desirable and has been cut off by linear transportation corridors. New linear
facilities should enable pedestrian access to public shorelines where access is
desirable.
SMPPI07 Transportation and utility facilities should be encouraged to coordinate joint
use of rights-of-way and to consolidate crossings of water bodies when doing
so can minimize adverse impact to the shoreline.
Shoreline Environments
Purpose
In order to more effectively implement the goals, objectives, and policies of this master
program and the SMA, the shorelines of the state within Federal Way have been
categorized into three separate environment designations. The purpose of these
designations is to differentiate between areas whose geographical features, ecological
functions, and existing development pattern imply differing objectives regarding their
management, use, and future development.
Each environment represents a particular emphasis in the type of uses and the extent of
development that should occur within it. The system is designed to encourage uses in
each environment which enhance the character of the environment while at the same time
requiring reasonable standards and restrictions on development so that the character of
the environment is not destroyed.
The detennination as to which designation should be given to any specific shoreline area
has been based on, and is reflective of, the existing development pattern; the biophysical
capabilities and limitations of the land; and the goals and aspirations of the local
citizenry. .
Each environment designation category includes: (1) a purpose statement which clarifies
the meaning and intent of the designation; (2) criteria to be used as a basis for classifying
a specific shoreline area with that environment designation; and, (3) general management
policies designed to guide management decisions and development consistent with the
character of the environment.
Shoreline Residential
Purpose:
. The purpose of the "shoreline residential" environment is to accommodate residential
development and appurtenant structures that are consistent with this chapter. An
additional purpose is to provide appropriate public access and rec.reational uses.
Criteria:
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 16
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Assign a "shoreline residential" environment designation to shoreline areas inside urban
growth areas, as defined in RCW 36. 70AII 0, incorporated municipalities, "rural areas of
more intense development," or "master planned resorts," as described in RcW
36.70A.360, ifthey are predominantly single-family or multifamily residential
development or are planned and platted for residential development.
Management Policies:
1. Residential uses should be the primary use. Development and redevelopment
activities should be focused within already developed areas. Any commercial
development allowed in residential areas should be water-oriented or should
support water-oriented uses.
2. Standards should be developed and implemented for setbacks or buffers, lot
coverage limitations, shoreline stabilization, vegetation conservation, critical
area protectiori, and water quality. These standards should be employed in
residential designs so that new development would not degrade shoreline
ecological functions or aesthetic values, taking into account the environmental
limitations and sensitivity of the shoreline area, the level of infrastructure and
services available, and other comprehensive planning considerations.
3. Multifamily and multi-lot residential and recreational developments should
provide public access and joint use for community recreational fa,cilities.
4. All residential development should occur in a manner consistent with the
policies listed under Goal SMPG2 of the shoreline use element.
Urban Conservancy
Purpose:
The purpose of the "urban conservancy" environment is to protect and restore ecological
functions of open space, flood plain and other sensitive lands where they exist in urban
and developed settings, while allowing a variety of compatible uses.
Criteria:
Assign an "urban conservancy" environment designation to shoreline areas appropriate
and planned for development that is compatible with maintaining or restoring of the
ecological functions of the area, that are not generally suitable for water-dependent high-
intensity uses and that lie in incorporated municipalities, urban growth areas, or
commercial or industrial "rural areas of more intense development" ifany of the
following characteristics apply:
(A) They are suitable for water-related or water-enjoyment uses;
(B) They are open space, flood plain or other sensitive areas that should not be more
intensively developed;
(C) They have potential for ecological restoration;
(0) They retain important ecological functions, even though partially developed; or
(E) They have the potential for development that is compatible with ecological
restoration.
Management Policies:
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
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1. Residential, recreational, commercial, and public facility uses should be
allowed provided they preserve the natural character of the area or promote
preservation of open space, flood plain, bluffs, or sensitive lands either directly
or over the long term. Water-oriented and single-family residential uses should
be given priority over nonwater-oriented uses. For shoreline areas adjacent to
commercially navigable waters, water-dependent uses should be given highest
priority. Uses that result in restoration of ecological functions should be
allowed if the use is otherwise compatible with the purpose of the envirorUnent
and the setting.
2. Standards should be developed and implemented for management of
environmentally sensitive or designated critical areas to ensure that new
development does not result in a net loss of shoreline ecological functions or
further degrade other shoreline values. Development standards should be
developed and implemented for setbacks or buffers, lot coverage limitations,
shoreline stabilization, vegetation conservation, critical area p'rotection, and
water quality.
3. Public access and public recreation objectives should be implemented
whenever feasible and significant ecological impacts can be mitigated.
4. To enhance the waterfront and insure maximum public use, commercial or
office facilities should be designed to permit pedestrian waterfront activities
consistent with public safety, security, and protection of shoreline ecological
functions.
5. Aesthetic considerations should be actively promoted by mearis of sign control
regulations, architectural design standards, landscaping requirements, and other
such means. . .
Natural
Purpose:
The purpose of the "natural" environment is to protect those shoreline areas that are
relatively free of human influence or that include intact or minimally degraded shoreline
functions intolerant of human use.. These systems require that only very low intensity
uses be allowed in order to maintain the ecological functions and ecosystem-wide
processes. Consistent with the policies of the designation, local government should
include planning for restoration of degraded shorelines within this environment.
Criteria:
A "natural" environment designation should be assigned to shoreline areas if any of the
following characteristics apply: .
(A) The shoreline is ecologically intact and therefore currently performing an
important, irreplaceable function or ecosystem-wide process that would be
damaged by human activity;
(B) The shoreline is considered to represent ecosystems and geologic types that are of
particular scientific and educational interest; or
(C) . The shoreline is unable to support new development or uses without significant
adverse impacts to ecological functions or risk to human safety.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 18
12/1512006
Management Policies:
1. Any use that would substantially degrade the ecological functions or natural
character of the shoreline area should not be allowed.
2. The following new uses should not be allowed in the "natural" environment:
. Commercial uses;
. Industrial uses; . .
. Nonwater-oriented recreation; and
. . Roads, utllity corridors, and parking areas that can be located outside of
"natural" designated shorelines.
3. Single-family residential development may be allowed as a conditional use
within the "natural" environment if the density and intensity of such use is
limited as necessary to protect ecological functions and be consistent with the
purpose of the environment.
4. Scientific, historical, cultural, educational research uses, and low-intensity
water-oriented recreational access uses may be allowed provided that no
significant ecological impact on the area will result.
5. New development or significant vegetation removal that would reduce the
capability of vegetation to perform normal ecological functions should not be
allowed. Do not allow the subdivision of property in a configuration that, to
achieve its intended purpose, will require significant vegetation removal or
. shoreline modification that adversely impacts ecological functions. That is,
each new parcel must be able to support its intended development without
significant ecological impacts to the shoreline ecological functions.
DRAFT Goals and Policies
Federal Way Shoreline Master Plan
Prepared for Ecology Review, December 2006
Page 19
.12/15/2006
FEDERAL WAY
SHORELINE MASTER
PROGRAM UPDATE
DRAFT RESTORATION PLAN
SMA GRANT No. GO.600 1 19
DECEMBER 2006
PREPARED FOR:
.CITY OF FEDERAL WAY
FEDERAL WAY, WA
PREPARED By:
ESA Adolfson
5309 Shilshole Avenue NW, Ste 200
Seattle, Washington 98107
206.789.9658
EXHIBI:T of
PAGE OF
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan.
Table of Contents
1.0 INTR 0 D U CTI 0 N ........................................... ..........................;.......... .......................................... ....... 2
REGULATORY BACKGROUND ......... .......................... ...... ................. ..... ..... .............. ........................... ...... 3
DEFINING RESTORATION .... .......... ..................... ............ ...... ,....... ..... ..... .......... ... ... ........ ..... ... ............ ... .... 3
KEY ELEMENTS OF RESTORATION PLANNING IN THE SMP UPDATE PROCESS .....................................,.. 4
2.0 ASSESSMENT OF SHORELINE FUNCTIONS ..............................................................................5
WATERSHED CONTEXT ..................................................................... ........................................................ 5
PHYSICAL & BIOLOGICAL ...... .............. ..... ...... ................ ........................... .............. ..... ..... ......... .... ,........ 5
HABITAT AND SPECIES.... ........ ....... ........... ......... ..... ..~........ ..... ...... ..... ....... ......... ........... ..... ............. ...'.. ..... 7
LAND USE AND PUBLIC ACCESS............................................................................................................... 7
RESTORATION OPPORTUNITIES ...................... ........ ............ .... .............................. ..... ........... ... ..... ... ..... .... 8
3.0 DEVELOPING RESTORATION GOALS AND POLICIES........................................................... 9
FEDERAL WAY SMP UPDATE - RESTORATION GOALS AND POLICIES ....... .........................................9
4.0 EXISTING PLANS' AND PROGRAMS .......................................... ...............................;.......11
REGIONAL 'PROGRAMS. ........................ ........... ........... .......... ........... ......,..............~..... ............... ..... 11
. ~:;:~ ~~~~~ ~~;:;:~::,:'2005~200.7'p~~~; S;~~d ..C~~;~;;,~;i,~.,.,....,'.".,...,.,.. ".~..,.,.'.,.,..,v..,'.,..',e.f..',.,.'~~':;i~~:::::::: :'. ::::::::::: ::::::::: :::::: ::: ~;
Puget Sound Nearshore Project (PSNP)..,............................ ... ........... ................................................., 13
Shared Strategy for Puget Sound: Draft Puget Sound Sal .0' ~a[ ...................;.............................. 13
Water Resource Inventory Area (WRIA) 9 Forum: Salmo ~ ...,. Pan f,. ..................................................14
~~:::~s::~~:rn;~;:;';;::~~~~1lr:;i:;,~~;IA.~.~~~, .. ..~~~~~.~~..~f ,~,~.~~.~~~..~~~~.~~~~.~,~~~......... 14
Water Resource Inventory Area (WRIA) 10 Fo'!!.: 'Salm2~t Pla.{.... ..................................................15
cascad,e Land conservancy.....:.......,.,. ',.'..,..'.".'",......... ."...'....,.....,1'.......,'...}...... ......... .,.,.... ......................:...........................15
COUNTY AND CITY PROGRAMS .....~. . ........ ,...... ...... ......... ....... ............................................. 15
K~ng County Shoreline Maste: Pr ;.!rJl......, . ..~...... ......:,..,..... ...........,.'" .........,........................................ 15
Kmg County Lake StewardshlIJ. ...... ...,. ..... ................... .:... .................................................. 16
City of Federal Way Surface .ge iv \.iO {--...............I,... ..................................................16
ADDITIONAL OR NEEDED PR ....I.... "it'T" . ............... _... .............................................. 16
5.0 IMPLEMENT AT... .... ......~!!.~ .... ..~~t!'.~r. .................................................................. 17
IDENTIFY RESTO ATJ&: RP01. IES..............................................;.............17
PROGRAMMATIC ......... ............,......... .. ...~1................................................................... 18
City of Federal thEro; m ..J.:.......,..... .~/........................................................................... 18
SIT~~::::~~~itat ,.,...... ........ ... ,:,..~.)....:: ::: ::~'.'.'.':::::::'.'.'''''::: :::~'..::::::: :~.....:::: ::::~','''::::::::'''''.'.':::::: ~... ~~
Puget Sound M. J~.I,~~:.......................,.....,.................,..............,..................,..20
Freshwater Lak . .........,.....,................."... ...................,.........................., ......,.....24
FUNDING AND P S ,...................................................................................... 24
Puget Sound Ac ....... ...........,.................,. ....,......"............... .....,................;.,........ ........ 25 .
Puget Sound W, & estoration Grant Program;................................................................. 25
Salmon Recove 'SRFB),.. ..."..............,......,..... ................."..........,.....,............. ........., ..........,,25
King County C ;C!.~,;(}. Dl ict........... ........ ....................... .................................. ................................ ........ 25
NOM Commun . Restoration Program.....,.,....,....,........... .......,.....",.... ............... ..............................., 26
Federal Way S ter Management CIP..................................................................................................26 .
Other Possible g Sources..., ........ ..,.......,....................,.............,..... ....."..............,.................. .........,.......26
TIMELINES AND CHMARKS ........... .............................................. ................. ..................... ................ 27
MONITORING AND ADAPTIVE MANAGEMENT ........................................................................................ 27
6.0 CON cL US IONS............... ..................... ............. ................ .:......... .......................:..................;.......... 28
RE FEREN CES........ ............................... ....................... .................... ...... ............................ ...... ................. 29 .
'-f'P"'P 1. ~ ~" " .
'I ... " .~ 'q"1 j'f." ~
...,. .:..~ ~. ~ ,-;s ~>~ :
. "'1> \ . ).' ,,,"
~,_ ,,,~::~....,_.......,....... of. .\~ ......."....\':0. ,,:w....:......:.,4'-' ~'J.;~ :',,,,,,, . ~
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
1.0 Introduction
Incorporated in 1990, the City of Federal Way is the sixth largest city in the State of Washington.
The City is located 25 miles south of downtown Seattle and eight miles north of downtown
Tacoma. The City of Federal Way is located in the southwestern comer of King County, and
occupies approximately 22.5 square miles of area, including Puget Sound waterfront to the west
(Figure I, Vicinity Map). The City is bordered to the north by the City of Des Moines, to the
east by King County, and to the south by the City of Fife and Pierce County.
The City (and its Potential Annexation Area to the east) includes nearly 17 miles of marine and
freshwater lake shorelines subject to the Shoreline Management Act (SMA or the Act) as
"shorelines of the state." The SMA (RCW 90.58) is charged with balancing how shorelines
should be developed, protected, and restored. The Act has three broad olicies or mandates; it
strives to: 1) encourage water-dependent uses, 2) protect shoreline I resources, and 3)
promote public access. In addition, restoration planning is an im t\component of the
environmental protection policy ofthe Act.
The City has two main types of water bodies that are r nde the SMA and the City's
SMP: marine coastal, and freshwater lakes. The Ci or I e In lude the lower Puget Sound
marine coastal shoreline, which is designated a "sha n f stat .'Wi e significance." Several
freshwater lakes also fall under SMA regulaf wit e City liiiii s. These are Steel Lake,
North Lake and the northwestern. shore of L ill~. gurt horeline Planning Areas).
ar largy' y tOJh> east of the City and the
ea s re; ;J ed t., a the Potential Annexation
b ,'; III not b~ eective in the area until it
io'Jo ated wit~in the City's PAA include Star
ate remaitf} g portions of Lake Killarney.
" ~J,'we the state." Lakes or portions thereof in
ing'@Q\u MP. There are no rivers or streams in
This report suppo to: y~\1 element to the City of Federal Way's
Shoreline Master ad~ in 1999. The SMP is being updated to
comply with the S 0.58), and the state's SMP guidelines (Washington
Administrative C ~ R II), which went into effect in 2003. The SMP
guidelines specify ts must include within their shoreline master program, a
"real and meaning s g ,address restoration of shorelines. The guidelines also specify
how the policies i " p mote "restoration" of impaired shoreline ecological functions, in
places where sUCh~,ng$JOrS are found to have been impairecl based on the inventory and
characterization 0 shoretme ecological functions and ecosystem processes. Local governments
are required to CoI1tlripuf'e to restoration by planning for and supporting restoration through the
SMP and other re~atory and non-regulatory programs. .,
This report provides a framework to: 1) understand how restoration of ecologicalfunction can be
accomplished; and 2) suggest pathways to use the SMP process to accomplish the restoration of
.2
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
impaired shoreline functions associated with the Puget Sound shoreline in Federal Way and
seven freshwater hikes in the City and/or its P AA.
Regulatory Background
The restoration plan is an important component oftlte SMP process under the new guidelines.
As such, local governments must develop provisions".. . to achieve overall improvements in
shoreline ecological functions over time when compared to the status upon adoption of the
master program."
It is important to note that the restoration planning component of the SMP is voluntary, not
regulatory. Restoration planning is focused on incentives, available funding sources, volunteer
programs, and other programs that can contribute to a no net loss strategy.
To date, restoration, rehabilitation, enhancement or other improve ~to shoreline ecological
functions have either been voluntary or in the form of mitigatior_1~~acts resulting from
development. Conservation or preservation of existing condo . as 'een, and continues to be,
the primary regulatory approach to protecting ecosystem 9-~~
Through numerous references to and emphas
restoration, and preservation of"fragile" sh
health, " "the land and its vegetation a wil
life," "ecology," and "environment," "'~ ct
environment an essential statewide "oli
goals of the act (WAC 173- 186( 'J);
ance, protection,
esources, " "public
and their aquatic
of the shoreline
h the other policy
For counti
functions,
restoratio
The guidelines to
The goal 0
when impl
resources
201(c)).
Defining Res
rograms which include planning elements that,
e 0 i 'Prove the overall condition of habitat and
s ~/ine area of each city and county (WAC 173-26-
There are numerous definitions for "restoration" in scientific and regulatory publications.
Specific elements of these definitions often differ, but the core element of repairing damage to an
existing, degraded ecosystem remains consistent. In the SMP context, the WAC defines
"restoration" or "ecological restoration" as:
3
Federal Way Shoreline MasterProgram Update - DRAFT Restoration Plan
"... the reestablishment or upgrading of impaired ecological shoreline processes or
functions. This may be accomplished through measures including, but not limited to,
revegetation, removal of intrusive shoreline structures and removal or treatment of toxic
materials. Restoration does not imply a requirement for returning the shoreline area to
aboriginal or pre-European settlement conditions" (WAC 173-26-020(27)).
Using the WAC definition of restoration in regards to state shorelines, it is clear the effort should
be focused on specific shoreline areas where natural ecological functions have been Impaired or
degraded. The emphasis in the WAC is to achieve overall improvement in existing shoreline
processes or functions, if these functions are impaired. Therefore, the goal is not to restore
historicaHy natural conditions, but rather to improve on existing, degraded conditions. In this
context, restoration can be broadly implemented through a combination of programmatic
measures' (such as surface water management; water quality improvement; public education) and
site-specific projects (such as beach nourishment projects or riparian 1 ntings). It is important .
to note that the guidelines do not state that local programs should ' ld require individual
permittees to restore past damages to an ecosystem as a conditi tm rmit for new
development (Ecology, 2004). The restoration planning ele . i d therefore focuses on
the City as a whole rather than parcel by parcel, or permi
Key Elements of Restoration Planning lil
%"
.
.
ms that are currently being implemented
on goals (such as capital improvement
s (WRlA habitat/recovery plans);
.
ch arks for implementing restoration projects and programs
tion goals;
harisms or strategies to ensure that restoration projects and programs will
,~~~ ccording to plans and to appropriately review the effectiveness of the
,J)! grams in meeting the overall restoration goals (e.g., monitoring).
The following sections ofthis report discuss these subjects as they relate to the City of Federal
Way Shoreline Master Program.
.
Identify ti
and achiev
.
4
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
2.0 Assessment of Shoreline Functions
Shoreline restoration planning begins with the identification of "degraded areas" or areas with
"impaired ecological functions." The City's Shoreline Inventory and Character(zation
(Adolf son, 2006) examined nearshore and ecosystem-wide processes that maintain shoreline
ecological functions; identified impaired ecological functions; and identified programmatic and
site-specific opportunities for restoration and/or enhancement. Key findings of the inventory and
characterization are summarized below.
Watershed Context.
The City of Federal Way is located within two watersheds or Water Resource Inventory Areas
(WRIAs) - the Duwamish-Green River WRIA No.9 and the Puyallup- ite River WRIA 10
(Figure 3, Regional Context). The marine coastal areas ofPuget So ithin the city as well as
Steel Lake and Star Lake and Lake Dolloff in the city's PAA are .~ ed as part ofWRIA 9.
Lands w~thin the City th~t dr~i~ to the Puget Sound to the wes '. ~ill Creek and th: lower
Green River to the east he wlthm the WRIA 9 watershed. ~g.' s the northern portions of
the City and Potential Annexation Area (P AA). .;
Shoreline Planning areas or re
characterization as shown in
determined based upon land fi
current land uses. In c~ll,
to those within the
s to either the White River
The majority of the Federal Way area lies within
Or to Hylebos Creek. North Lake, Lake Genev.
lands within the City drain to the southwest.
before entering Puget Sound at Commence
Tacoma and enters the Hylebos Waterway
Bluffs, beaches, b ,~ eshwater streams characterize the City's
coastai / nearshor ~F:~o~ percent ofthe City's coastal shoreline has been
modified with ripr ulkheads. Structures in the shoreline can limit the
amount of sedime 1" and areas to the beach, and are known to cause erosion
and loss of some sa and fine gravel beaches. Currents naturally move
sediments across t!' ,~. nEI'3l' ongshore in continu.al cycles, but these structures interrupt the
natural supply and.~~tri~~tiOIrof sediments, causing a change in sediment composition within
the nearshore area ..~ow ver, coastal shoreline in Dumas Bay and Dash Point State Park are in a
more ~atural cond'lpn and coa, stal processes are les~ aIt~red. .Fish ~nd wildlife. that utilize. the
shorelIne depend 0;!Yt ese nearshore processes to mamtam their habitats and ultimately their
populations. .
5
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Table 1. City of Federal Way Shoreline Planning Areas
Coastal
Puget
Sound -
East
Coastal
Puget
Sound -
Dumas Ba
Coastal
Puget
Sound -
..West
Steel Lake
Star. Lake
.,.~ '
Gen'era~.J)es~!{ipJi~g,
:.Appro~im~te
. :"~ Reach. (:, . ]jength, .
:'~uml)er., ,(Ulil~s)
1.67
Frorn the city limits boundary with Des
Moines on Puget Sound, near ] 51 A venue
South, extending west to Dumas Bay
Green
River ]A
9
IB
9
Ie
9
1.43
1.74
xtending west to the city
with Pierce County,
sh Point State Park
limits, west of 1-5.
9
2
9
.; e st portion of 1. he city's
o ndary with City of Kent
3
Lake 9
Dolloff
Lake
Geneva
North
Lake
. Lake
Killarney
Five Mile
Lake
Total
16.93
Partially in the. city limits, partially in the
southeast portion of 1. he city's PAA, east ofI-
5 and SR ]8.
In the southeast portion of the city's PAA,
near Military Road.
A total of 4.84 miles ofPuget Sound
shoreline and approximately 12.09 miles of
lake shoreline.
6
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
The freshwater lakes in the City are located on a broad plateau in the eastern half ofthe City and
in the P AA. The plateau developed from glacial recessional deposits and tills. As the glaciers
melted, lakes formed in the scour areas. Lakes in the City drain to five main drainage basins
including 1) the Puget Sound, 2) the Green River, 3) Mill Creek, 4) the White River, 5) and the
Hylebos. Lake shorelines have been modified with bulkheads and other bank protection, but also
have significant areas of natural shoreline conditions. On Steel Lake, Star Lake and Five Mile
Lake, approximately 20 to 50 percent of the shoreline has been modified with bulkheads.
Shoreline modifications are less frequently occurring on the remaining lakes.
Habitat and Species
The City's coastal and freshwater shorelines are used by a variety of aquatic and terrestrial
species including salmon ids and other fish, birds, mammals, and a wide variety of invertebrates.
Of special interest are areas that provide habitat for federally listed sp' es and species of local
importance (primarily nearshore areas), including bull trout (threat , Chinook salmon
(threatened,)' coho salmon, as well as great blue heron.n..."e..,.",.s,..,'.t,..,s~I.,te,."..,'"....,..., , '.. fish such as .surf smelt
and sand lance (prey for salmon ids) spawn on local be~ches:..:"~s eds are also present
along the City's coast.al/nearshore areas, specifically nea ".,. ',.Roin State Park and in the
northern end of Dumas Bay and northward. Dumas B \;1112 " has been identified as a
pocket estuary with regional importance within the ti' .":IlA7 ar e habitat.
The freshwater shoreline lakes within the Ci d it i',p" ~ do n"l,.,12".,., ovide salmonid habitat or .
habitat for federally listed species. Howeve '.,,' se I k!".,..,e~ Q.o1provlo,i,.'...~ general habitat for .
waterfowl" trout, and other aquatic species i'Q;Q ntp tS 1harae of Federal Way and the
lakeshore Fesidents. . Also,. go~d w7;~gual~ i.n.,' '., he jeS,h~ter I is important fo.r
downstream salmomd habItat I "."",j.,,',., sue;n~l~"..,.,t e ',lI! bos Cre oe's Creek, Mill Creek,
Lakota Creek, and the Green .
S, .
a., eoasta / rshore shoreline are single-family
e ityi's most mon shoreline use is single-family
e"..".nt of.',.,"t."..".",e""O'~~~I oreline. Parks and public recreational
pa i~, oreliitZ These uses include Dash Point State Park,
. t .overty Bay Park. These areas provide opportunities
The major land us
homes, parks, and '
residential, which
facilities occupy 1
Dumas Bay Park,
for fishing, hiking
Land uses along t s re.:, at wakes are primarily single-family residential and public
parks. Single-fam nt;l~se occupies between 55 and 80 percent of the shoreline on
,most lakes, with t o of North Lake (35 percent) and Five Mile Lake (32 percent).
Parks, boat ramps, lie facilities occupy 9 to 39 percent ofthe lake shorelines. Public
access to the lakes s via parks including Steel Lake Park, Lake Geneva Park, Lake
KiIlarney Park an e Mile Lake Park, as well as several boat ramps owned by Washington
Department ofFis . and Wildlife. Parks and open space areas within Federal Way are shown on
Figure 4 (Parks and Open Space).
7
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Restoration Opportunities
Programmatic restoration opportunities include restoration of public properties, coordination
with the City's Surface Water Management Division, public education and outreachprograms to
provide technical guidance for shoreline homeowners, and the possibility for incentive-based or
community-based restoration on private propetty. Opportunities for enhancing public awareness
and education could include installation of informational kiosks at public parks and waterfront
use areas. The City could also continue to coordinate with King County, the Water Resource
Inventory Area (WRIA) 9 forum, and other regional or Puget Sound-wide planning efforts to
implement identified restoration policies and actions.
Opportunities for site-specific habitat enhancement or restoration of shoreline ecological
functions (primarily in the marine shoreline) have been identified in the shoreline inventory and
characterization report based upon watershed information and field st ~es conducted by the
WRIA groups. In the coastal Puget Sound areas, restoration focus .'. removal of abandoned
creosote pilings, debris and concrete from the shoreline. Resto in1,he coastal shoreline also
focuses on bulkhead replacement with soft-shore armoring~ e use 6f native marine riparian
plantings. These site-specific projects would provide smaH.. valuat5le efforts toward habitat
enhancement and restoration of impaired ecological .S~n I
In the freshwater lakes, restoration opportunitie hav Q v een s . fically studied. WRIA
information for these lakes is lacking due to . mp . on restt, on of nearshore marine
habitats: However, restoration opportunitie . e be e '~rally tified through the shoreline
~:~;e~~g:~~~~:;:I~~n;'~,I~~::~/:'~:U;~ ::':J1.I: O::v~':~::~:~~ter
~~~~;t:~a~en~~~~' s:~~~:~ov,. <<,.',i,~',j,~i".VVi. s~',.,.t.,'".,.,,'I,',,'1 ts; ~~~l~ :e~: ~t~: :~:Pb;'""1 10
lakeshore residents and by th .~u ~i1'
8'
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
3.0 Developing Restoration Goals and Policies
The guidelines provide that local shoreline master programs shall include "goals, policies and
actions for restoration of impaired shoreline ecological functions." Under the guidelines,
restoration planning has a purpose distinct from development regulations and mitigation
standards. "The guidelines expressly focus restoration requirements on the use of master
program policies, as opposed to development regulations" (Ecology 2004). "Master program
provisions should be designed to achieve overall improvements in shoreline ecological functions
over time, when compared to the status upon adoption of the master program" (WAC 173-26':'
.201(2)(f)). . .
Federal Way SMP Update ~ Restoration Goals and Policies
Goal!. D
to resolve
shoreline
1. Co. to work with the State, King County, Watershed Resource Inventory
Ar (WRlA) 9, and other governmental and non-governmental organizations to
explore how local governments can contribute to the preservation of ecological
processes and shoreline functions. .
The existing Shoreline Master Program (SMP) goals and policies ar
Federal Way Comprehensive Plan (FWCP). This is asubsection
section (Section 2.8) of the Land Use Chapter of the Compre
does not contain specific goals and policies related to resto
ecological functions. However, some policy statements.
and in Chapter 9, Natural Environment, address pres
shoreline features such as natural vegetation and fish
SMP goals and policies should be consisten
Plan. As the City works through the SMP u
objectives, and policies related to shoreline
the Conservation Element and re . "C
below is simply a starting poi 'ev 10
focused around (our key area Q;cp.Q~, in
opportunities focused 0 ubi . at
incentive based resto ^ op
opportunities. Th . s
organization of th
Shoreline Restor
shoreline function
development activ
9
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
2. Continue to work with the WRlA 9 to restore shoreline habitats and shoreline
functions that support listed endangered and threatened species, as well as other
anadromous fisheries.
Goal 2. Pursue projects to restore and enhance shoreline habitats, functions and'
processes on private and publicly owned lands.
Policies:
1. Prioritize restoration and enhancement first based upon the greatest net ecological
benefit, as compared to the project cost. .
. .
2.. Focus restoration and conservation activities on public parks and open space lands
for public enjoyment.
3. Work with own.ers of other publicly owned land such a ashington State Parks
to encourage restoration and enhancement projects.:i:L, ing funding strategies.
4. Work with the public and other interested partil~i9 'tize restoration
opportunities identified in Shoreline Invento , d €h cterization Report.
5. Promote shoreline vegetation restoratio ~ con rol of invasive weeds and
nonnative species, to enhance marine ,~rre hwater lakeshore habitats.
6. Promote shoreline vegetation re Jorat reduc th hazard of slope failures or
accelerated erosion.
7. Develop a program to imple
strategies.
8. Monitor and ada
including funding
Goal 3. Evaluate pot
com' 0
are identified by the
1.
1m
2.
3.
e voluntary restoration projects in degraded shoreline environments.
1. Create incentives that will make it economically or otherwise attractive for
development proposals to integrate shoreline ecological restoration into
development projects.
10
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
2. Encourage protection, enhancement, or restoration of native riparian vegetation
through incentives and non-regulatory programs.
3. . Promote bioengineering and/or soft engineering alternative design approaches to
shoreline stabilization and provide technical guidance to shoreline landowners.
4. Establish public education materials to provide shoreline landowners technical
assistance about the benefits of native vegetation plantings.
5. Identify and pursue funding sources for shoreline restoration actions on private
lands.
Goal 5. Provide ample opportunity for the public to learn about the ecological aspects
and community values of the City's shorelines.
Policies:
I. Explore opportunities with other educational or
develop an on-going program of shoreline ed
2. Identify areas where kiosks and interpre ~Jve
experience of users of the shoreline.
3. Develop strategies to fund these roje
n enhance the educational
4.0 Existing Plans
A number of regional and Pu
water resource managern t,
and programsprovi ra
Pu et Sound P
In December 2005 overnor Gregoire formed the Puget Sound Partnership to focus attention on
the overall needs and health ofPuget Sound and to promote public education and interagency
coordination for clean up of the Sound. The vision of the new Partnership is:
11
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
To ensure that the Puget Sound forever will be a thriving natural system, with clean
marine and freshwaters, healthy and abundant native species, natural shorelines and
places for public enjoyment, and a vibrant economy that prospers in productive harmony
with a healthy Sound.
At the direction of the Governor, the .Puget Sound Partnership drafted recommendations for
preserving and restoring Puget Sound and its species and habitats. A summary ofthose
recommendations was released on October 13, 2006, along with a full report to the state
legislature, congress and Governor. The recommendations include a 2020 Action Agenda with
overarchlng goals and outcomes for a healthy Sound. The Partnership proposing eight priorities
needed to conserve and restore Puget Sound; these are:
1. Protect existing habitat and prevent further losses.
3.. Significantly reduce toxics entering Puget Sound
arine waters.
2. Restore the amount and quality of habitat, and reduce fr
4. Significantly reduce pollution from human
waters.
5.
6.
7.
8. Build and sustain
This renewed focus 0
wide funding for re
Pu et Sound A
Plan
The Puget Sound
Washington State' e vi
Sound Action Tel ~c
Action Team part f,S i
tribal, federal and oe I
and restoration oflu n
Every two years t~RS partnership develops a plan to guide their work. The 2005-2007 plan
provides a total of) million funded through state agency budgets to address eight priority
areas:
SAT) defines, coordinates and implements
r Puget Sound. The legislature created the Puget
) 6 as the state's partnership for Puget Sound. The
d' ctors from 10 state agencies and representatives from
nts with direct responsibilities and authorities for conservation
· Clean up contaminated sites and sediments;
· Reduce continuing toxic contamination and prevent future contamination;
]2
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
. Reduce the harm from stormwater runoff;
. Prevent nutrient and pathogen pollution caused by human and animal wastes;
. Hood Canal: a geographic priority for 2005-2007;
. Protect shorelines and other critical areas that provide important ecological functions;
. Restore degraded nearshore and freshwater habitats; and
. Conserve and recover orca, salmon, forage fish, and groundfish (PSA T, 2005).
Each of these priorities is applicable to Federal Way with the exception of Hood Canal.
Puget Sound Nearshore Proiect (PSNPl
The Puget Sound Nearshore Project (PNSP) (also referred to as the P t Sound Nearshore
Ecosystem Restoration Project (PSNERP)) is a large-scale, multi-a initiative to address
habitat restoration needs in the Puget Sound basin. Nearshore P ....g"?l g, als are to identify
significant ecosystem problems, evaluate potential solutions . restoJ: and preserve critical
nearshore habitat. PSRP represents a partnership betwee . ,(my Corps of Engineers
(Corps), state and federal government organizations, 11 'Ii . dustries and environmental
organizations.
. Providing marshes, m
. Removing, movin an
gates, etc.);
. Using alte
. Restoring
2000; PSN"
and gravel materials;
eads, rip rap, dikes, tide
om erosion and flooding; and
eelgrass beds and kelp beds (USACOE,
PSNERP also pro
restoration princip
Shared Strate
Plan
Shared Strategy fi (Shared Strategy) is a collaborative effort between local
stakeholders and r ,p.ao/. eaders to protect and restore salmon runs across Puget Sound that was
initiated as: a resul Ejidangered Species Act (ESA) listings of salmonid species in the Puget
Sound region. Sh ',~ Strategy engages local citizens, tribes, technical experts and policy makers
to build a practical, cost-effective recovery plan endorsed by the people living and working in the
watersheds ofPuget Sound.
13
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
, Shared Strategy has developed a draft salmon recovery plan (Shared Strategy, 2005) that
provides a blueprint for salmon recovery strategies throughout Puget Sound and incorporates, by
reference, local watershed plans for salmon recovery. Amongst other strategies described in the
draft plan, Shared Strategy describes their 'Top 10 Actions Needed for Salmon Recovery', many
of which .have additional beneficial impacts for humans.
Water Resource Inventory Area (WRIA) 9 Forum: Salmon Habitat Plan
The city is a participating local agency in WRIA 9 watershed planning. After several years of
planning and scientific study, WRIA 9 recently completed the Salmon Habitat Plan (WRIA 9,
2005). The plan is both broad in scope and specific in recommendations for protection,
enhancement, and restoration of habitat along the Green River and Puget Sound coastal
shorelines. The plan identifies needs and includes recommended policies, programs, and
projects for both the entire watershed and the sub watersheds (Middle a d Lower Green River)
within the City of Federal Way. Identified needs for the nearshore ower watershed which
are relevant to the City include:
.
.
.
.
.
Green-Duwamish River;
.
.
rotect downstream salmonid habitats.
As part of the , a study was undertaken to identify and prioritize
habitat protection a s along the marine shorelines of the Green / Duwamish
and Central Puget ed, mcludingthe City of Federal Way (Anchor, May 2006).
The study used ha r characterize marine shoreline habitats arid select priority
habitat action area. throu a cience-based prioritization process. Priority conservation,
rehabilitation, and lion projects were identified for WRIA 9 using a GIS model approach.
Restoration action .e identified as two scales: first, at the extent of the entire WRIA
nearshore area, an econd, at the extent of each of 12 subareas within the study area.
Based upon this WRIA study, the overall habitat needs and goals for the Federal Way marine
shoreline include:
14
Federal Way Shoreline Mas/er Program Update - DRAFT Res/ora/ion Plan
. maintaining and conserving the shoreline sediment supply through protection of feeder
bluffs; and,
. conserving and restoring tributary mouths and marshes present in Dumas Bay.
These were identified as important habitat needs within the WRIA 9 nearshore environment due
to the location of Dumas Bay and the bay's potential to provide marsh and pocket estuary habitat
for feeding and refuge of salmonids.
Water Resource Inventory Area (WRIA) 10 Forum: Salmon Habitat Plan
Federal Way lakes also drain to the White River and the Hylebos, within WRIA 10. A Salmon
Habitat Plan has not yet been developed for WRIA 10; however a framework for plan
completion has been developed. Pierce County is acting as the lead a cy for WRlA 10, with
King County and other basin jurisdictions, including the City of A " providing support. The
framework for plan completion can be found in the Pierce Cou ap r of the Tri-County 4(d)
Rule submittal. Upon completion, the WRIA 10 Salmon Ha' tan ill provide broad and
specific goals and recommendations for protection, enhan.,.., . restoration of habitat
throughout the basin. An existing document, The Sal ~a 13 l Pn tection and Restoration
Strategy (Pierce County, 2005), provides initial asse . 1 p.o itizes initial
recommendations and actions forWRIA 10.
The following cou
restoration and/or
.s are in place, which provide guidance for lakeshore
. arine shoreline.
Cascade: Land Conservancy
King County is u s S oreline Master Program concurrent with the cities in the County.
The County is cur 1)V nderway with its shoreline inventory and characterization, which will
address the lake s { es within the Federal Way's PAA. In 2007, King County will be
developing its rest ation plan for shorelines within unincorporated county lands. The City
should coordinate efforts with King County for restoration opportunities identified for lakes in
the PAA, as well as for regional collaboration in restoration with WRIAs 9 and 10.
]5
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Kina County Lake Stewardship Proaram
King County Natural Resources and Parks, Water and Land Resources Division, has conducted
volunteer lake monitoring for all of the larger lakes in King County since the 1980s. The
monitoring was continuous on many of these lakes during the period from the mid 1990's to
2004. Lakes within the City of Federal Way were part of this program until 2004, when the City
. took over water quality monitoring. Monitoring data included watershed mapping, bathymetric
mapping, mapping of aquatic vegetative communities, and water quality data.
The City should coordinate efforts with King County for shoreline restoration opportunities on
lakes currently within the City's PM. Lake characteristics and health are summarized in the
King County Lake Monitoring Report for Year 2004
(http://dnr .metrokc. gov Iwlr/waterres/smlakesD.
Cit of Federal Wa Surface Water Mana
e Water Facilities Plan
a Management Division
i, 's surface water systems.
flooding, runoff and water
t. The S WM Division also
Ishery resources and
ram identifies, funds, and
alleviation, improve and
nd improve water quality
program is currently
lakes and marine
ci
C.."".' ,
}' e c~~k
Additional or <,~;
An additional or e ed City program is needed to coordinate shoreline restoration
opportunities with Federal Way. While restoration along the Puget Sound coastal shoreline has
been identified by the WRIA 9 work, restoration opportunities within the freshwater lakes has
not been formally identified by regional or watershed programs. Current programs on the lakes
.are focused on water quality, aquatic weed removal, and public education. Further, the City's
,~FIP program is the Lakota Creek
d~i~he main stem and west branch of the
1:(;':1, t' er Treatment Plant near Dumas Bay
'~e ~'k: tream banks and restore the natural
em, d, spawning gravels were placed, and large
.ed s ream. Invasive plants were replaced with native
. imilar stream restoration projects on the East Branch
t Hylebos. While not specifically in the shoreline,
k Creek serve to protect and restore water quality, natural
sses, all of which contribute to the health ofPuget Sound.
16
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Storm water CIP program does not specifically address restoration within marine coastal areas of
Puget Sound, but focuses on freshwater restoration, specifically streams and salmonid habitat. A
new citywide program or an expanded CIP program is needed, which focuses on restoration in
both the coastal marine shorelines and freshwater lake shorelines.
5.0 Implementation
The implementation portion of restoration planning typically requires more detailed site-specific
information than is available at this time, especially with regard to the timing of projects.
However, potential projects and priorities have been provided for shorelines in Federal.Way
based UpON the WRIA studies and other information. This implement . on section is intended to
provide information about the implementation approach consistent guidance for SMP
development (WAC 173-26-201 (2)(f)(vi)).
1) Restoration or enhancement should
master programs "serve to improve
the shoreline area"; and .
2) Restoration should be d
have been impaired as
oal that local shoreline
abitat and resources within
In Federal Way, both
restoration or enha
(e.g., WRlA 9 Sal
Inventory. and Ch
prioritizes the pre
undertaking both
restoration.
i ~~'!1~. in this restoration plan. Conservation refers to
s t, "currently provide valuable functions. An important part
"~n is protecting priority ecological processes and habitats that
'red. Conservation opportunities in the City's shoreline are
primarily provided\tl:1.~911g A 9 studies and are intermixed with restoration opportunities for
marine shorelines. . rvation of shorelines will also be addressed in the City's shoreline
regulations.
]7
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Programmatic Restoration
City of Federal Way Restoration Proaram
To organize and implement protection and restoration measures, Federal Way could consider
establishment of a City Restoration Program, which targets and directs aquatic habitat protection
and restoration opportunities within the jurisdiction. This program could implement stream and
wetland restoration, which is currently occurring through the Surface Water Management Utility
, as well as restoration for freshwater lakes and Puget Sound coastal shoreline areas. The
program could either be integrated into the existing Surface Water Management Utility or be
established as a stand-alone program. This program could be charged with integration and
cooperation with the WRIA 9 and 10 committees, and King County, to identify funding
opportunities and collaborate on watershed projects. The new or expanded program would be
responsible for:
1)
Coordination with and leveraging of regional pr
, d organizations;
2) Identification of restoration opportunities, .
3) Prioritization and selection of restorat'
4)
5)1 Implementation of restoratio '
6) of restoration projects.
the City's Shoreline
atic opportunities in the
values:
a)
re
at the Federal Way shoreline parks and
n formational kiosks could be erected at
e' s 10, tions in the City. The kiosks would serve
mpG anceofthe nearshore area and coastal
tion on what people can do to help preserve or
, ai' s escribing existing wildlife viewing opportunities. A
e 1#. hi b))pe of kiosk can be found at Dash Point State Park.
c slt~'J'ce and public outreach for riparian planting enhancement or
nll'his program could be developed in concert with the "toolbox"
d scribed above as part of the WRlA 9 Salmon Habitat Plan. The
lould develop specific technical assistance for appropriate plantings in
riparian zones, lakeshores and along freshwater streams that discharge to
t Sound in the City of Federal Way.
b)
]8
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
c) Distribution of public education material. Residential property owners could
receive printed material emphasizing stewardship; natural processes and native
plantings, such as a blueprint for a lake-friendly landscape and a Puget Sound
shoreline stewardship guidebook.
WRIA 9 Habitat Plannina
The WRlA 9 Salmon Habitat Plan recommends development of several programs relevant to the
City of Federal Way shoreline master program update. The programs would be developed by
King County in coordination with local jurisdictions and could be implemented at the local level
by the County or by the City of Federal Way. The city should support and participate in the
development of these programs, which would be administered by the city's new or expanded
shoreline restoration program. These include:
1.
Blueprint of
ote voluntary restoration
de ign and shoreline
y.tlJ ef unneeded shoreline
'ne riparian vegetation. The
d would seek to develop
ate property.
re Program. This program
horeline armoring
. ing techniques where
ite to site depending on the.
nd example designs are
ound Shorelines (Ecology,'
directly benefit from this
d Puget ound West. Public education
ld help restore natural shoreline
ts and formerly important reaches of
2.
3. Citizen JIj
opportuni
identify a
4. Create an
program
structures
remove su
abundanti
Remove Relict Structures from Intertidal areas. This
d 0 reclaiming intertidal habitat located beneath relict
footings and failed erosion control structures. Opportunities to
ure are found throughout the Federal Way shores, and are most
Sound East.
19
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Site-Specific Restoration and Conservation
The City's Shoreline Inventory and Characterization (Adolfson, 2006) evaluated and described
how shoreline ecological functions have been impaired in the City of Federal Way and identified
site-specific opportunities for shoreline restoration, enhancement, and conservation.
Puaet Sound Marine Shorelines
Site-specific restoration opportunities for the coastal shorelines have been identified through
WRIA 9 planning efforts (Anchor, 2006; Coastal Geologic Services, Inc., 2005). These
restoration opportunities focu~ on Dumas Bay due to its overall importance to salmonid habitat
within the nearshore environment. These high priority nearshore restoration projects are
identified. bYWRlA 9 in the Federal Way area of the Puget Sound and i lustrated on Figure 5:
4. Conserve
at the west
extended reach of feeder
tation and the feeder bluff
ce for down drift areas,
1. Conserve unarmored shoreline west of Dumas Bay.
unarmored feeder bluffs with mature marine riparian v
Dumas Bay. The sections are separated by a reach .
Nearshore habitat would be enhanced and maint .
supplies to the intertidal zone in this area.
2. Restore the tributary mouth at Dash oint
reaches of this creek could be restor re
meanders, and restoring riparian ve f n
~ _.,..~'
3. Conserve unarmored fee
bluff exists east of Dum
area would preserve t
including Dumas Bay.
as Bay. Restoration of tributary mouth
itat and associated wetlands.
5. Restore ri
rIparIan ve
degraded n
tia operties east of Dumas Bay. Marine
fDumas Bay where native vegetation is
Coastal Geologic'
during the WRIA
specific shoreline
listed as priority r
opportunities are
However, it shoul oted that the following projects have not been assessed or ranked based
upon ecological be efit to the City's shorelines. Further, feasibility studies may be required for
some of the projects to ensure that no critical design flaws are identified in the proposal.
20
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
.
Dumas Bay RestorationlEnhancement Opportunities. Several restoration and/or
enhancement opportunities are found within the shores of Dumas Bay. Opportunities
range from recovering and restoring upper beach habitat, upland planting/marine riparian
restoration and invasive species eradication, to the removal oftoxic material from the
sub-tidal to upper beach. A boulder rockery lines the City of Federal Way (Dumas Bay
Center) shoreline for approximately 860 feet between 2 creek mouths. The rockery is
currently over the upper intertidal zone and is failing in a number of places. The buildings
at Dumas Bay Center have a very large setback and the removal of all or portions of the
rockery would allow for upper beach and backshore restoration, and reestablishment ofth
sediment supply from the bluffs. Portions of the bluff toe could be partially protected
from erosion by installation of soft shore protection, if the bluff toe were first graded
further landward to make space for thi.$. However, it may be more cost effective to allow
the toe to erode naturally.
Currently much of the banks are covered with Polygonum c alum (Japanese
f;~:~:~)~I::~Ct~:~:~~~: :~~~~c::~~~:~~:~ ::~lle~. J~q~;! ~:~~~7c:%~Z;:[:~~~:'
possible. Over 30 relict creosoted pilings and a nu ',iipfiGr'~ted drift logs are found
within the B~y. The toxic creosote could be rem~J '~m beaches. These restoration
opportunities are well suited as a demonstrati0:,~9j~ "q~ to its location within a
public park enabling citizens to participate in'Q~nity '.ed re~toration such as
invasive species eradication and/or re . tin bank. s and signs describing the
restored geomorphic and ecological sse ul " Iso ide an opportunity to
engage and educate community me ~
Buena Bulkhead Remova~~ars
bulkhead removal are t:~d;!.ne, B
. armored shore segme Ii are 10c te
from "feeding" be '~re
drift cell that ..,.,.,...',p i~ ho,
shore-drift. n,umb r '. dri J' on sediment from these bluffs to
maintain n ore a a (J mkterate eo. io' rates. This drift cell has incurred the
greatest re 0 in n se .~~SU~ in Federal Way and was identjfied as a
moderatel h ~~,F~ r' crofY e entire WRlA 9 nearshore (Coastal
Geologic 'f)"
Removal 0 r~g the base of these bluffs would restore the function
ofthe blu se'.f nt source; however, bluff erosion rates may need to be
moderated en ,'g homes residing in the upland. Following removal of
shoreline sO,','s ore protection should be used to mitigate and slow "deferred"
erosion. .PI ~t~ a ne riparian buffer, comprised of native shrubs and trees, will also
reduce ero rj:s as well as eventually providing large woody debris to the nearshore.
Federalry/#delaide Bulkhead Removal. This opportunity entails removing an
unnecessa/6ulkhead from the backshore of an accretionary beach. The bulkhead
measures approximately 475 feet long and runs adjacent to shore, with the nearest home
set back considerably from the shore. The structure is largely aesthetic and provides no
function as erosion control. Removing the structure and restoring the upper beach and a
.
.
21
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
.
more natural shore profile would enhance nearshore habitats. Beach nourishment could
replace lost upper beach sediment and allow for the creation of a protective storm berm.
Dune and marine riparian plants should be planted to further enhance beach habitat, by
providing shade to the upper beach, a source of large woody debris and pollution
abatement.
Poverty BaylLakota Bulkhead Removal. This accretionary (depositional) beach has
suffered considerable impact resulting from paving the upper beach for what is assumed
to be recreational or aesthetic purposes. The pavement extends across approximately 55
feet of shoreline and is roughly 16 feet in width. This paved area could be deconstructed
to improve shoreline functions. Following removal of the backshore pavement the upper
beach could be nourished and dune and marine riparian vegetation could be planted to
further restore nearshore processes.
Remove Relict Struct!lres in Intertidal Lakota - Northeast D as Bay (3 locations).
These opportunities entail removing several relict concrete ures from the intertidal
beach that currently preclude access to the underlying h 1. 0 ofthese structures
appear to also obstruct littoral transport of sediment, ause erosion of down-
drift beaches as well as degrading nearshore habi ,L. heastern-most opportunity
entails removing the relict concreted footings a bo These footings extend from
the bulkheaded upper beach to the lower-mo oJ central enhancement
opportunity includes removal of a large con at was likely used as a boat
ramp. This solid concrete, angular st re a impeding littoral transport.
This structure also reduces alongsho ne ing juvenile salmonids,
which are likely to be forced into de at e thought to be more
~:~~~~a~~~t~;)ti~~~~~W ~ ~t : c~~:~' ~:r~~~~~~~;~~~~r
westthere is another d 'a'Rt~~t~" co 0 of the structure coVer
valuable intertidal for tS. s a i his reli at ramp could be
deconstruc~ ,~ d" t a ;~:i::l ;~s::;;~;:::;e:::~
~:~:~:: ;t;~~~j'~ ier pile bulkhead that is no longer
providing i i te I; and a decaying barge that is
interruptin t sa, ringes on upper intertidal habitats, is
composed e .,,/ i.,.J1>un s upland sediment. Coastal Geologic Services
(2005) ide d be:g,/ high restoration priority due to its value as a
nearshore j4~ ' <'ge is of considerable length and width, and is
positioned 0 s\i0fe. As a result, it both infringes on a substantial area of
intertidal hents net shore-drift along a large portion ofthe beach profile.
Additional eflrdmerous (15~20) car tires that are buried in intertidal sediment
from this p t.o a'pproximately 100 yards to the southwest. Removing these structures
would enh ,..",.i a)6ngshore and cross-shore connectivity, restore feeder bluff function,
and reclai,;~. rfently impacted habitats. , .
Purchase and Relocate Homes at Base of Historic Feeder Bluffs. The bluffs that are
proposed for restoration are located approximately 0.6 and 0.9 miles northeast of the
creek mouth at Dash Point State Park or 300 feet southwest and 1100 feet northeast of the
end of53rd Avenue SW. The bluffs are referred to as Restoration Bluffs No.1 and 2.
.
.
.
22
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Prior to the construction of shore modifications and homes along the base ofthese bluffs,
they were exceptional (historic) feeder bluffs - meaning they regularly contributed large
quantities of sediment to the nearshore (Coastal Geologic Services2005). Shoreline
armoring and bulkheads have considerably slowed erosion rates along these bluffs, which
has likely reduced the sediment supply in this shore reach. Coastal Geologic Services
(2005) identified this area as being a high restoration priority across the entire WRIA 8
and 9 nearshore (over 121 miles of shoreline).
The shore modifications typically extend 20 or more feet from the base of the bluff;
preventing bluff sediment input into the intertidal as well as infringing on upper beach
habitat. As sea levels rise and waves scour the beach waterward of bulkheads, those
beaches will become increasingly narrow and "starved" of littoral sediment. This
eventually leads to the loss of nearshore habitats in a phenomenon referred to as "the
coastal squeeze." Relocating any hazardously positioned homes nd restoring the
nearshore sediment source would restore down-drift shores educe life safety risks.
Additionally a number of creosoted logs likely associate failed bulkhead could be
. removed from the upper beach.
Here it should be noted, that actions such as this
owner consent and a dedicated source of fund'
. Das. h Point State Park Bluff and Estuarine "..l.)..../J.'!jPifJ.' ceme~! I pportunities include the
removal of rip rap from the lower reac oft ...~...~nnamed k and restoring channel
sinuosity and dune/riparian ve..g. etati. e .r~.i..r.;.,.'.ai...,...~...c........Uld placed with limited soft
shore protection and enhanced ripari getl~Q;;:: e st channel should be
widened and logs could be...uu~. >~>.>d to C9 th ai.... r.,ea........ 0) er the channel could migrate
near the bridge. These acf. m 1 it >,~~e rip plantings could enhance the
geomorphic and ecolo n ub .>~ary, wh ould increase habitat
quality and quantity :6 fit t, 10 .~I terrestria aquatic species. A second
restoration actio . to,3 s piles an I creosoted soldier pile
bulkhead loc 'y t t k. The piles also provide an opportune
site for bir .Pt!. to. .~!I onids. Simple pile removal would help
rest. ore na ..Jb.eac...... itio sa .1~~.>';.....p....... ~~,ses. Several of these are creosoted piles,
so addition t waf 11 u Ji~ be efi'co 'rJt l1ieved.
As mentioned abo ;, he er . nagement Capital Improvement Program
identifies and fun's ve . am restoration projects which are completed or
underway. Whileo'~ted within the marine shoreline, their
implementation w! flow regimes in key streams that discharge to Puget
Sound. As such, t g in the context of shoreline restoration planning. Key
projects include:
. Lakota C .'~.~ He toration (2004-2006). Habitat improvements include removal of fish
passage 0 .hmgtions and strea~ restoration (e.g., creation o~ ~pa,:ning pools; placement
of anchor ;tJarge woody debns and boulders; and bank stablhzatIOn).
. West Hylebos Restoration (2004). Habitat improvements, including the installation of
large woody debris and native plants to stabilize and restore the stream channel.
23
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
· Joe's Creek (2006-2007). Involves widening the stream channel to, alleviate flooding
and to restore fish habitat (via addition of spawning gravel, creation of eddy pools,
riparian enhancement for shade, etc.).
· Spring Valley Restoration and Bridge Replacement (2007). The Spring Valley
Restoration Project is ajoint effort between City of Federal Way and Washington
Department of Transportation, which will return approximately 1,400 feet of degraded
creek channel and pasture-land back to its natural state. The creek will be realigned to
follow a more natural, meandering path, with shade cover from native trees and shrubs.
Creating wetland areas and placing logs will provide additional habitat. A major
element ofthis proJect will be the construction ofa new bridge on S. 373rd St. to
eliminate flooding across the road and improve fish and wildlife passage.
Freshwater lake Shorelines
Site-specific restoration opportunities on the City's freshwater}>,>.*~ ha Je not been identified on
the grOun.d due to limited access to private lakeshore pr,o.pe ..>.F.,urt.~,..,.; > er,.lakes within Federal
Way and its PAA have not been specifically evaluated a > ~an comprehensive study such
as the WRIA 9 or 10 efforts. Baseline studies on the 1 ,a er lakes to determine
. ",. ":"u;
specific .restoration needs and opportunities would b ;.110 fi t. ep in identifying and
implementing lakeshore restoration.
· Restoration of native lake
quality and habitat;
y nay,~ trees) to protect water
In general, restoration activities on the lake
.
he lakes;
.
s ng bulkheaQs where feasible; and
.
Funding and
Funding opportun'
administered by st
obtain funding wo
agencies. Targeti
fish spawning enh
restoration plans/
organizations mos
24
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
PUQet Sound Action Team
The state 'legislature has appropriated a total of approximately $182 million for state agencies
and. university education programs for implementing the 2005-2007 Puget Sound Conservation
and Recovery Plan (PSAT, 2005). Funding is allocated by both priority area (e.g., habitat
restoration (13 percent), stormwater (29 percent)) and state agency (e.g., Ecology, WDFW, WSU
Extension, etc.). The habitat restoration funds would be the best fit for opportunities in Federal
VVay.' .
PUQet Sound Watershed Protection & Restoration Grant ProQram
The Environmental Protection Agency through the Washington Department of Ecology is
offering watershed grants to applicants within the 14 Puget Sound Salmon Recovery Planning
Areas. These grants are in collaboration with the Shared Strategy for get Sound, Washington
Department of Fish and Wildlife, and Puget Sound Action Team. governments, tribes,
watershed entities and non-profit groups are eligible for these gr e focus of the grants is
to identify opportunities and barriers for the protection and r water quality, water
quantity, habitat protection and habitat restoration within und Basin.
The King Conserv
founded in 1949. C
by the Washingto $t te
demonstration pro
providing or point
allocates approxi
habitat protection
technical assessm
the activities ofth
forums in King C
projects and progr
Assessment, such
d Specis ct in 1999, the Legislature
itiz' ppointed by the Governor
s to "J!, tect or restore salmon
1 w hed groups and has helped
oard rded $7.1 million during the
toratlo:a d assessment projects in the
~V' A 9) . ese grants build on other
s ti"",District a aterways 2000.
PM.. ~ry natural resources assisrance agency
rsa6ihbrized by the State of Washington and guided
is!~. The District promotes conse.rvation through
) roviding technical assistance, and, in some cases,
u may be available for projects. The WRIA 9 Forum
.' in g Conservation District funds. annually to support
at~nlprojects, stewardship projects and programs, and essential
.",ey comes from a countywide $5 per parcel assessment that funds
on ervation District as well as projects through other watershed
eginning in 2005, the highest priority for WRIA 9 KCD funding is
at are informed by the watershed Habitat Plan and the Strategic
the pocket estuary restoration projects.
Salmon Recovery Funding Board (SRFB)
25
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
NOAA Community-Based Restoration Pro~ram
NOAA's National Marine Fisheries Service houses the Community-Based Restoration Program
(CRP), begun in 1996. The Program promotes local efforts to conduct meaningful, on-the-
ground restoration of marine, estuarine and riparian habitat. The Program provides seed money
. and technical expertise to address important fishery habitat concerns. Projects are developed by
individual and civic organizations. NOAA solicits proposals for locally-driven habitat
restoration projects and works closely with communities to aid their development and
implementation. Successful projects result from significant local support, including citizens'
hands-on involvement to implement the restoration projects. Following development of a
restoration project, the "host" community subsequently monitors and maintains the site. This
model promotes stewardship and a: heightened appreciation for the environment.
Federal Way Surface Water Mana~ement CIP
1. Coastal Protection Account
2. Aquatic Lands Enhance
3. City Fish Passage Ba
Department ofTransp
4. Five-Star Res n
5. Habitat Co
6. Matching
7. Non-point
Agency,
8. Pacific Gr
9. Puget Sou pU S. , Wildlife Service
10. Puget Sou e (l > e tor n Program - Washington State Department of Ecology
11. Regional Fsh r" n n ement Groups - Washington State Department ofFish and
Wil~life!. .
12. Sechon 20 '.,:r.....A,..".'.,q!l ~c Ecosystem RestoratlOn Program - U.S. Arm.y Corps ofEngmeers
13. Transporta18l.'l qUlty Act for the 21st Century (TEA-21) - Washmgton Department of.
Transporta .,'. n
14. Washington State Ecosystems Conservation Program - U.S. Fish and Wildlife Service
15, Wetland Protection, Restoration, and Stewardship Discretionary Funding-
Environmental Protection Agency
j?ram funds projects
l!l~Jor multi-jurisdiction
,t{e Surface Water
c uld consider adding a Puget
. g sources would include
The Federal Way 'Surface Water Management Capital Improve
through a combination ofCIP funds and grants, and/or fundi
projects such as development of comprehensive basin pia
Management Program is focused on freshwater resour
Sound nearshore restoration component to its capital
grants and partnership opportunities.
Other Possible Fundin~ Sources
atural Resources
n Grant Program - W A
rotection Agency
rvice Coastal Program
) - Ducks Unlimited
rogram - Environmental Protection
26
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
Timelines and Benchmarks
In the context of the SMP update, restoration planning is a long-term effort. As stated earlier, the
SMP guidelines inClude the general goal that local master programs "include planning elements
that, when implemented, serve to improve the overall condition of habitat and resources within
the shoreline area" (WAC 173-26-201(c)). As a long~range policy plan, it is difficult to
establish meaningful timelines and measurable benchmarks in the SMP by which to evaluate the
effectiveness of restoration planning or actions. Establishing timelines is further complicated by
the fact that shoreline restoration is almost entirely dependant on grant funding, which is
unpredictable at best. Nonetheless, the legislature has provided an overall timeframe for future
amendments to theSMP. In 2003, Substitute Senate Bill 6012 amended the Shoreline
Management Act (RCW 90.58.080) to establish an amendment schedule for all jurisdictions in
the state. Once Federal Way amends its SMP (on or before December 1,2009), the City is
required to review, and amend if necessary, its SMP once every seve~ ars (RCW '
90.58.080(4)). During this review period, the City should docume 'fm:sgress toward achieving
shoreline restoration goals. The review could include: ' ,.'
· Re-evaluating adopted restoration goals, objectid Fcies;
· Summarizing both planning efforts (includin.ic"k q fo and securing g~ant funds)
and ~~-the-grOund actions.undertak~n in thei~rrt1'to l~~t those .goal~; ~d
· RevlSlng the SMP restoratlOn plann lem ',,~!to reflectJt nges m pnontIes or
objectives. ' .
arks would be
iz?, like 0 egrated with the City's
a tructure. , a shoreline restoration CIP
ld be fo ~u~ d on site-specific projects
projects!fuch as stormwater facIlity
esign could advance shoreline
., Adaptivel
· Use monitoring and maintenance results to inform future restoration activities.
These core objectives have been expanded upon by regional entities focused on restoration such
as the WRIA 9 Forum and the Puget Sound Nearshore Project (PNSP). Strategic principles and
27
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
concepts intended to guide ecosystem recovery are expressed in guidance publications (PSNP,
2004) and the WRIA 9 Salmon Habitat Plan (WRIA 9, 2006). Relevant principles and concepts
are very briefly summarized below:
.
Restoration Principles. Restoration planning should be strategic and restoration design
should be based on carefully developed goals and objectives. Follow-through, or
monitoring, should be employed, including development of performance criteria and use
of adaptive management in project development.
Monitoring Principles. Thr~e types of monitoring are defined: I) implementation
monitoring to track which potential programs and projects are carried out; 2)
effectiveness monitoring to determine if habitat objectives of the program or project have
been achieved on the ground; and 3) validation monitoring to confirm whether proposed
restoration actions are achieving the overall goals and objective for restoration citywide.
Monitoring should be driven by specific questions, goals, an . ectives and should be
used as the basis for determining if restoration goal~ are;, et. Monitoring should be
long-term and interdisciplinary. Another component ~.m.0nitor ng is information
management; data should be well documented and )1"k~rle t others.
Adaptive Management Principles. Adaptiv a' l'!~ s a process that uses.
research and monitoring to allow projects to "oeee ~ eS1Il;~inherent uncertainty and
risk regarding its consequences. Adapt" e m ment i~h t accomplished at a
regional or watershed scale, but can ed roject I ' to increase knowledge
about ecosystems and how they resp act~l), .
.
.
6.0 Conclusions
Several watershed
forums and other
framework and pr'
Federal Way. Th
support WRIA pr
the identified rest
the goals and obje
likely focus on pu
within the coastal
Less infOfmation i
state. Restoration
restoration progra
and assess project
derway through the WRIA 9 and 10
e existing programs provide a regional
, g and implementation in the City of
. lp" III these efforts and should continue to
at ed level restoration goals. Implementation of
at tile WRIA level and in the City, would advance
s · ir ti reline functions in the City. Initial efforts would
(l';.g;th grant opportunities, especially for restoration projects
KiLg~ ound.
a ~,e .p';li he City's lakes, which are also considered shorelines of the
the 11 de al Way's lake shorelines should be included in a citywide .
i~h lhe first step being an initial study to evaluate restoration opportunities
ility .
28
Federal Way Shoreline Master Program Update - DRAFT Restoration Plan
References
Adolfson Associates, Inc. (Adolfson). 2005. City of Federal Way Shoreline Inventory and
Characterization. Prepared for the City of Federal Way. Seattle, Washington.
City of Federal Way. 2005. 2005-2010 Capital Improvement Plan - Surface Water
Management. Federal Way, Washington.
Coastal Geologic Services, Inc. 2005. Inventory and Assessment of Current and Historic Beach
Feeding Sources / Erosion and Accretion Areas for WRIAs 8 and 9, Appendix D:
Restoration Potentials. Prepared for King County Department of Natural Resources and
Parks. Bellingham, Washington.
Green / Duwamish and Central Puget Sound Watershed Water Resou,;. Inventory Area 9
Steering Committee (WRIA 9). August 2005. Salmon Ha ,~. Ian - Making qur
Watershed Fitfor a King. Prepared for the WRIA 9 Fo Se ttle, Washington.
ound Nearshore Project.
. Puget Sound Action Team (PSA T). 2005. 2005-2007 P
Plan. Olympia, Washington.
Technical
United States A
, Investigati
Washingto
C . 2000. Section 905(b) Analysis: General
Pu -et Sound Nearshore, Washington. Seattle,
Washington Depa
Shoreline
Washingto
gy ology). 2004. Restoration Planning and the 2003
ide lines. Ecology Publication No. 04-06-022. Olympia,
29
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legend
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Map Source: City of Federal Way, King County
Map Date: May, 2006
City of Federal Way
33325 8th Ave S,
PO Box 9718
Federal Way, WA 98063-9718
(253) 835-7000
www.cityoffederalway.com
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Shoreline Regulations
To help with your review ofthe updated regulations we included a version showing all
the edits as strikethrough and underline and a clean version, which shows how the
regulations would read if all the edits are accepted.
EXHIBIT ".. G-
PAGE ;:OF
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
...
V6. RS{o tJ S KaNC t-./ f7 f3-D ,13
4.1 Article III.
SHORELINE MANAGEMENT
Sections:
Division 1. Generally
18-161 Purpose and authority.
18-162 Jurisdiction.
18-163 Additional definitions.
Division 2. Shoreline Regulation'
18-164 General development standards.
18-165 Shoreline modifications.
18-166 Environment desiQnations.
18-167 Permitted use table.
18-168 Shoreline residential env' 0'
18-169 Urban conservanc en
18-170 Natural environment.
~1
Division 3. ministrative Procedures
18-171 Shoreline manaQement permit and enforcement procedures,
adoption bv reference
18-172 Permit processinQ and public notice
18-173 Shoreline exemption
18- 173 Shoreline variance
18-174 Conditional uses
18-175 Final apporval of shoreline permits
18-176 Combined hearinQ authority
18-177 Alteration or reconstruction of nonconforminq .use or development
18-178 Shoreline environment redesiQnations
18 161 Environmental designations.
18 165 Urban environment.
18 166 Rur31 en'{ironment.
18 167 Conservancy residentbl environment.
18 168 Natural environment.
18 169 Application and public notice.
18 170 ProcedLire for review.
18 171 Shoreline variance.
18 172 Conditional uses.
18 173 Fin~.approv31 of shoreline permits.
18 171 Comhined hearing authority.
18 175' Alteration or reconstruction of nonconforming use or development.
18 176 Shoreline environment redesignation.
EXHIBIT S-r Page lof 47
PAGE OF
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
, ,
, ,
Division 1. Generally
18-161 Purpose' and authority.
The city adopts these regulations under the authority of the Shorefine
Management Act of 1971, Chapter 90.58 RCW, as amended, and the
Shoreline Management Guidelines, Chapter 17344-26 WAC. (Ord. No.
90-38,91(24.10),2-27-90; Ord. No. 98-323, 93,12-1-98; Ord. No. 99-
355, 9 3, 11-16-99t
(b) No development shall b ; " . n by any person on the
shorelines of the state without ~ing a shoreline permit from the
, department of community dev opment. or an authorized statement of
exemption per; provided, that a permit Shall not be required for
development exempted from the definition of substantial development in
WAC 173-27-040 and for developments exempted by RCW 90.58.140(9)
and (10). (Ord. No. 90-38, 9 1(24.30.10, 24.30.20),2-27-90; Ord. No. 98-
323,93, 12-1-98; Ord. No. 99-355,93, 11-16-99)
18-163 Additional definitions.
Unless otherwise defined in this chapter, the definitions contained in
this chapter, Chapter 22 FWCC, Chapter 90.58 RCW, and Chapter 173-26
WAC shall apply.
Act: means the Washinqton State Shoreline Manaqement Act, .
Chapter 90.58 RCW.
Access: limited public access means:
(1) Actual physical access from land to the ordin::lrY high water mark or
to the 'Netland directly abutting tho ordinary high water mark, such access
being limitod to specific groups of people or to certain regularly prescribed
times; or '
(2) Visual access available to the general public to thoshoroline and
adjacont '.vator body, such access being specifically provided for in the
development of tho site. '
Accoss: public access means actual unobstructed access available to
the goner;)1 public from land to the ordinary high water mark or to the
v.'Otl3nd directly abutting the ordinary high 'Nater mark.
"".", ", .~l" l! ~ ',; ,.' "';',,;,
. ' 6. ~. ,.'i.;". ""';,(j
.'A' . ."., , "
~_,','.'el'.~~l<~''''''''''~''''~''''~'''''- ~JlJI: 1, ~..."
.., r 3' ~ ,. Pi(
, . '\M;
'''''''~>'e''''_. 1 U'u,...;.._.~,_~_ - "J.r", t,
Page 2 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Amendment means a revision, update, addition, deletion, and/or
reenactment to the Federal Way SMP.
Approval means an official action by the City of Federal Way aqreeinq
to submit a proposed SMP or amendments to the Department of Ecoloqy
for review and official action pursuant to the SMA.
Ih<erage grade lova.' me~ms the average of the natural or existing
topography at the center of all exterior walls of a building or structure to bo
placed on a site; provided, that in the caso of structures to be built over
'!.later, avorage grade lovel shall be the elovation ort ordin3ry high w3ter, .
Backshore means a berm, together with associated marshes or
meadows, on marine shores landward of the ordinary high water mark
which is normal above high tide level and has been gradually built up by
accretion.
. Bank means a steep rise or slope at the edqe of a body of water or
water course.
Beach nourishment means the artificial replenishinq of a beach by
delivery of materials dredqed or excavated elsewhere.
Berm means a led e or shoulder consistin of mounded earth or rock.
Breakwater means an off-s.. ~ e structure, either floating or not, which
mayor may not be connected 0 the shore, such structure being
designated to absorb and/or reflect back into the water body the energy of
the waves.
Bulkhead means a solid or open pilo of rock, concrete, steol, timber,
other m3tori3ls, or a combination of theso materials erected gonorally
parallel to 3nd n03r tho ordin3ry high 'N3ter m3rk for tho purpose of
protocting 3djacent shorelands and uplands from W3\'OS or currents.a wall.
seawall. embankment or other structure erected parallel to the shoreline
that retains or prevents slidinq or erosion of land or protects land from
wave action.
Bluff means a steep slope which abuts and rises from Puqet Sound.
Bluffs contain slopes predominantly in excess of 40 percent. althouqh
portions may be less than' 40 percent. The toe of the bluff is the beach of
Puqet Sound. The top of a bluff is typically a distinct line where the slope
abruptly levels out. Where there is no distinct break in slope. the slope is
either the line of veqetation separatinq the unveqetated slope from the
veqetated uplands plateau or. when the bluff is veqetated. the point where
the bluff slope diminishes to less than 15 percent.
Class I beach me3ns a beach or shore having dopend3blo,
geologically fully doveloped, and normally dry b3ckshore above high'tido.
Class!! beach means 3 b03ch or shore having only margin3l1y,
geologically partkilly doveloped, 3nd not dopondably dry backshore above
high tide.
Class I!I beach moans a beach or shore. h3ving no dry backshore
aV3ilable 3t high tide.
Page 3 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Conditional use means a use, development, or substantial
development which is classified as a shoreline conditional use or is not
classified within the SMP.
Critical saltwater and freshwater habitats (critical salmonid habitats)
means habitats that are used by Pacific salmonid species that miwate
between fresh water and salt water during their life cycle. These habitats
include:
1. 'Gravel bottomed streams used for spawninQ;
2. Streams. lakes, and wetlands used for rearinQ, feedinQ, and cover
and refuqe from predators and hiQh waters;
3. Streams and 'salt water bodies used as miQration corridors; am:J
4. Shallow areas of salt water bodies used for rearinQ. feedinQ. as well
as cover and refuqe from predators and currentS. includinq. but not limited
to, foraQe fish habitats such as sandy beaches and eelqrass beds: and
5. Pocket estuaries includinQ steams mouths and deltas where
freshwater mixes with salt water and provides rearinq habitat for
iuvenile salmonids.
ttom of a stream ba
nd/or maintainin a
Gfi.Ih .
or " or "littoral ceW' means a
articular reach of marine sho '~, 'hich littoral drift ma. occur without
siqnificant interruption and which contains any natural sources of such drift
and also accretion shore forms created by such drift.
EcoloqicaJ functions means the work performed or role played by the
physical. chemical. and bioloQical processes in the shoreline that
contribute to the maintenance of the aquatic and terrestrial environments
that constitute the shoreline's natural ecosystem.
Ecosvstem-wide processes means the suite of naturally occurrinq
physical and QeoloQic processes of erosion. transport. and deposition; and
specific chemical processes that shape landforms within a specific
shoreline ecosystem and determine both the types of habitat and the
associated ecological functions.
Environment, or masteF program environment, or sShoreJine
environment desiqnation means the categories of shorelines of the state
established by the city of Federal Way shoreline management master
program to differentiate between areas whose features imply differing
objectives regarding their use and future development.
Exemptions means those development activities set forth in Chapter
XX of the Federal Way SMP which are not required to obtain a Substantial
Development Permit but which must obtain an authorized statement of
exemption and which mus otherwise comply with applicable provisions of
the Act and the City's SMP.
Fill means the addition of soil. sand. rock. Qravel. sediment, earth
retaininq structure, or other material to an area waterward of the OHWM,
Page 4 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
in wetlands. or on shorelands in a manner that raises the elevation or
creates dry land.
Float means a structure or device which is not a breakwater and which
is moored, anchored, or otherwise secured in the waters of Federal Way,
and which is not connected to the shoreline.
Grading means the movement or redistribution of the soil, sand, rock,
gravel, sediment, or other material on a site in a manner that alters the
natural contour of the land.
Groin means a barrier type structure extending from the backshore into
the water across the beach. The purpose of a groin is to interrupt
sediment movement along the shore.
Jetty means an artificial barrier used to change the natural littoral drift
to protect inlet entrances from clogging by excess sediment.
Landslide means an episodic downslope movement of a mass orsoil or
, rock that includes but is not limited to rockfalls. slumps. mudflows. arid
earthflows.
Littoral drift means the natural movement of sediment along marine or
lake shorelines by w:Jve breakefWave-action :Jnd currents in response to
prevailing winds.
Marine means ertainin to tidall influ n
Sound and the ba s estuaries ,and i ts
Nearshore means either ne
'and refer enerall to an area
extends from the to of bluffs
beach to the oint where sunli. netrates marine waters to a de th
where aquatic plant life is supported.
Nonconformina use or develooment means a shoreline use or
development which was lawfully constructed or established prior to the
effective date of the Act or the applicable SMP. or amendments thereto,
but which does not conform to present requlations or standards of the
SMP. . .
Non-water-oriented uses means those uses which have little or no
relationship to the shoreline and are not considered priority uses under the ,
SMA. Examples include professional offices, automobile sales or repair
shops, mini-storage facilities, multifamily residential development,
department stores, and gas stations.
Ordinary Hiqh Water Mark (OHWM) means the mark on all tidal waters
and streams that will be found by examininq the beds and banks and
ascertaininq where the presence and action of waters are so common and
usual and so lono continued in all ordinary years as to mark upon the soil
a character distinct from that of the abutting upland, in respect to
veoetation, as that condition existed on June 1. 1971. as it may naturally
chanqe thereafter. or as it may chanqe thereafter in accordance with
permits issued by a local qovernment or the Department of Ecolooy. In
any area where the ordinary high water mark cannot be found, the
ordinary hioh water mark adioininq saltwater shall be the line of mean
hioher hioh tide.
Page 5 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Public Access means the public's abilitv to Qet to and use the State's
public waters, the water/land interface and associated public shoreline
area.
Restoration means in the context of "ecoloQical restoration ," the
reestablishment or uPQradinq of impaired ecoloQical shoreline processes
or functions. This may be accomplished throuQh measures includinQ, but
not limited to, reveqetation, removal of intrusive shoreline structures and
removal or treatment of toxic materials. Restoration does not im I a
requirement or returninq the shoreline area to aboriginal or pre-European'
settlement conditions.
Riprap means a laver, facinq or protective mound of anQular stones
randomly placed to prevent erosion, scour or slouQhinq of a structure or
embankment; also, the stone so used.
. Shorelands. also referred to as "shoreland areas," means those lands
extendinQ landward for two hundred feet in all directions as measured on
a horizontal plane from the ordinary hioh water mark; floodwavs and
contiouous floodplain areas landward two hundred feet from such
floodwa S' and all wetlands and river deltas associated with the streams
lakes and tidal waters which are sub'ect to the ions of this cha ter'
the same to be desi nated as to location b artment of Ecolo
Shoreline administrator mea
Plannin Director or.
administerin the Federal Wa
Shoreline 'urisdiction mean
"shorelands" as defined in the ederal Way SMP and RCW 90,58.030.
Shoreline Master Proqram (SMP) means the comprehensive use plan
for a described area. and the use regulations toqether with maps.
diaorams, charts, or other descriptive material and text, a statement of
desired ooals, and standards developed in accordance with the policies
enunciated in RCW 90.58.020. .
Shoreline modifications means those actions that modifv the phvsical
confiouration or Qualities of the shoreline area. usually throuqh the
construction of a phvsical element such as a dike, breakwater, pier, weir,
dredged basin, fill, bulkhead, or other shoreline structure. They can
include other actions. such as clearing .and qradinq, or 3pplic3tion of
chemic3ls.
Shoreline stabilization means actions taken to address erosion
impacts to propertv, dwellinQs, businesses, or structures caused bv
natural shoreline processes such as currents, floods. tides. wind or wave
action. '
Shorelines means all of the water areas of the state, including
reservoirs. and their associated shorelands, toqether with the lands
underlyinq them; except (i) shorelines of statewide siqnificance; (ii).
shorelines on seqments of streams upstream of a point where the mean
annual flow is twentv cubic feet per second or less and the wetlands
associated with such upstream segments; and (iii) shorelines on lakes
less than twenty acres in size and wetlands associated with such small '
lakes.
Page 6 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Shorelines of Statewide Siqnificance means those. areas of. Puqet
Sound in the City of Federal Way Iyinq seaward from the line of extreme
. low tide;
Shorelines of the state means the total of all "shorelines" and
"shorelines of statewide siqnificance" within the City of Federal Way. '
Soft-shore bank stabilization means the use of bioenqineerinq or
biotechnical bank stabilization measures where vegetation, loqs, rock and
beach nourishment are used to address erosion control and slope stability.
SMP means the Shoreline Master Proqram.
SMA means the Shoreline Manaqement Act.
Stringline setback means a straight line drawn between the points on
the primary buildings having the greatest projection (including 3ppurtenant
structures such as deck~) ;,.waterward on the two adjacent properties~
one of the adiacent properties is unimproved the line shall be drawn to the
point of the standard shoreline setback at the side property line of the
unimproved lot.
Water-dependent means a use or portion of a use which cannot exist
in any other location and is dependent on the wi t~",\ 'y reason of the
intrinsic nature of its operations. Examples 0 ..', ftiF.r,.'. dependent uses may
include ship cargo terminal loading a n~ passenger terminals,
barge loading facilities, ship bu' . .ockli ,marinas,
'aquaculture, float plane faciliti . ails.
Water-enjoyment means a I uS'e, or other use facilitating
public access to the shoreline rimary characteristic of the use; or a
use that provides for recreational use or aesthetic enjoyment of the
shoreline for a substantial number of people as a general characteristic of
the use and which through the location, design and operation assures the
public's ability to enjoy the physical and aesthetic qualities of the
shoreline. In order to qualify as a water-enjoyment use, the use must be
open to the general public and the shoreline oriented space within the
project must be devoted to the specific aspects of the use that fosters
shoreline enjoyment. Primary water-enjoyment uses may include, but are
not limited to, parks, piers and other improvements facilitating public
access to shorelines of the state; and general water-enjoyment uses may
include, but are not limited to, restaurants, museums, aquariums,
scientific/ecological reserves, resorts and mixed-use commercial;
provided, that such uses conform to the above water-enjoyment
specifications and the provisions of the master program.
Water-oriented means any combination of water-dependent, water-
related, and/or water-enjoyment uses and serves as an all-encompassing
definition for priority uses under the SMA.
Water-related means a use or portion of a use which is not intrinsically
dependent on a waterfront location but whose economic vitality is
dependent upon a waterfront location because:
(1) Of a functional requirement for a waterfront location such as the
arrival or shipment of materials by water or the need for large quantities of
water; or
(2) The use provides a necessary service supportive of the water-
dependent commercial activities and the proximity of the use to its
Page 7 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
customers makes its services' less expensive and/or more convenient.
Examples include professional services serving primarily water-dependent
activities and storage of water-transported foods. (Ord. No. 98-323, 9 3, .,
12-1-98; Ord. No. 99-:-355,93, 11-16-99)
~
~1
Page 8 of 47
I City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
.Division 2. Shoreline Regulation
18-164 [NEW SECTIONl General development standards.
The following general development standards apply to all uses and
activites in all shoreline environments:
(a) Impact mitigation.
(1) To the extent WashinQton's State Environmental Policy Act of 1971 (SEPA),
chapter 43.21 C RCW, is applicable, the analysis of environmental impacts from
proposed shoreline uses or developments shall be conducted consistent with the
rules implemEmtinQ SEPA (FWCC XX and WAC 197-11). MitiQation for adverse
impacts to shoreline functions will be triQQered durinQ the SEPA review or
shoreline land use permit process.
(2) Where required, mitiQation measures shall be applied in the followinQ
sequence of steps listed in order of priority.
a. Avoidinthe im act alto ether b not certain action or arts of an
action ;
b. Minimizin im acts b Ii "n
its im lementation b . u i
ste s to avoid or reduc
c.
rehabilitatin or restorin the affected
d. Reducin9 or eliminatinQ the impact over time by preservation and
maintenance operations;
e. Compensatinq for the impact by replacinq, enhancino, or providino
substitute resources or environments; and
f. Monitorinq the impact and the compensation proiects and takinq
appropriate corrective measures.
t3i(3) In determininq appropriate mitiqation measures applicable to shoreline
development, lower priority measures shall be applied on Iv where hiQher priority
measures are determined to be infeasible or inapplicable.
(4) Required mitioation shall not be in excess of that necessary to assure that
proposed uses or development will result in no net loss of shoreline ecolooical
functions.
(5) Mitiqation actions shall not have a siqnificant adverse impact on other
shoreline functions fostered bv thepolicv of the Shoreline Manaqement Act.
(6) When compensatory measures are appropriate pursuant to the mitiqation
priority sequence above, preferential consideration shall be given to measures
that replace the impactedfunctions directly and are located in the immediate
vicinity of the impact. However, alternative compensatory mitiqation may be
authorized if said mitiqation occurs within the watershed and addresses limitino
factors or identified critical needs for shoreline conservation based on watershed
or comprehensive manaoement plans, Authorization of compensatory mitiqation
Page 9 of 47
City of Eederal Way SMP - Article III. Shoreline Management .,- Draft Regulations
measures may require appropriate safequards. terms or conditions as necessary
to ensure no net loss of ecoloqical functions.
,.
iQl.-Veaetation conserVation: Existing native shoreline veqetation
shall be preserved to the maximum extent feasible within the shoreline
setback consistent with safe construction practices, and other provisions
of this chapter. Specifically native trees and shrubs shall be preserved to
provide habitat. shade and slope stabilization functions to maintain
ecoloQical processes in the City's shoreline.
(c) Water qualitv J stormwater. All activities and development within
the shorelineiurisdiction shall be incompliance with the requirements and
restrictions of FWCC Chapter 21: Surface and Stormwater Manaqement.
(d) Critic.al areas. Activities and development in critical areas found
within shoreline jurisdiction are required to comply with the followinQ
development standards. .
1 Geolo ic Hazard Areas. Re
defined in FWCC Cha ter 22 locate
hazard areas .Iandslide hazard e
a eolo ic hazardous area is I
on the site shall be in com
FWCC Cha ter22 Article XI,
(2) Streams and Wetland. If a stream or wetland (as defined in FWCC
Chapter 22) is located within the shoreline iurisdiction, all activities within the
shoreline iurisdiction shall be in compliance with the requirements and
restrictions of FWCC Chapter 22, ArticleXIV, Divisions 5 & 6: Critical Areas.
(3) Flood Hazard Reduction. If an area of special flood hazard is located on
or adiacent toa development site within shoreline iurisdiction, all activities on the
site shall be in compliance with the requirements and restriction of FWMC
Chapter 18, Article II, Division 6: Critical Areas.
, (e) Critical salmonid habitats. Activities and development in critical
salmonid habitats found within the shoreline jurisdiction are required to comply
with the following additional development standards:
Jk1) SaJ.meR-aRd steelhe:.ld Critical Saltwater :.lnd Freshw:.ltor l=Ia9itats
. (Critical Habitats).
(1) Structures which prevent the migration of salmon and steelhead are'
prohibited in the portions of the water bodies used by fish. Fish bypass facilities
shall allow the upstream migration of adult fish. Fish bypass facilities shall
prevent fry and juveniles migrating downstream from being trapped or harmed.
(2}baM-Efills shall not intrude intosalmon and steelhe:.ld habitats critical
salmonid habitats, except as provided in subsection (KQ)(3) of this section.
(3}baMEfills may intrude into critical s:.llt water are:.lS salmonid habitats
usod by salmon and stoelhead for migration corridors, rearing, feeding. and
Page 10 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
refuge only where the proponent obtains a conditional use permit (CUP) and
demonstr~tes all of the following conditions are met:
Ch +he-laRGfiU-ffi-fef-Water dependent or watef-f€!at~~
a~. An alternative alignment or location is not feasible;
612. The project is designed to minimize its impacts on the environment;
Gf. The proiect faGiJ.ity is in the public interest; and
ego If the project will create significant unavoidable adverse impacts, the
impacts are mitigated by creating in-kind replacement habitat near the project.
Where. in-kind replacement mitigation is not feasible, rehabilitating degraded
habitat may be required as a substitute:
{4-t-bJnless the applicant domonstrates that soft shore bank stabilization or
bioengineering techniques will not be succossful, bulkheads and other shoreline
protection structures are prohibited in salmon and steelhead critical salrrlOnid
habitat.
(5) \lIJhere bulkheads and othor shorelino protection structures are
allmved, the toe of tho bulkhead or structure shall be locatodlandwardof the
ordinary high water mark except as provided in subsection (kg)(6) of this section.
\Nhere an existing bulkhead or structure caRRet be removed because of
east environmontally
. possibleconstructed R
(1e) Bulkheads, brea
. >'structures may intrude into
habitats only where the prop
are met: '
a. An alternative alignment or location is not feasible; .
b. The project is designed to minimize its impacts on the environment;
c. The proiect facility is in the public interest; and
d. If the project will create significant unavoidable adverse impacts, the
impacts are mitigated by creating in-kind replacement habitat near the project.
Where in-kind replacement mitigation is not feasible, rehabilitating degraded
habitat may be required as a substitute.
@) Docks, piers,pPilings and floats-may be located in water area2s used
by salmon and steelhead for migration corridors, rearing, feeding and refuge,
provided the facilities use open piling construction and impacts are avoided to the
maximum extent possible. Approach fills shall be located landward of the
ordinary high water mark.-JJocks, piers, pilings and t!eats-shall not be-lecated ifl
other salmon and steelheadcritical habitats. The preject shall bo designeG--te
minimize its impacts on the environment.
(Q8) Open pile bridges are the preferred water crossing structures over
salmon and stoelheadcritical salmonid habitats. If a bridge is not feasible, one of
the following water crossing structures may be approved if the. impacts af€-can
acceptablebe mitiqated: temporary culverts, bottomless arch culverts, elliptical
culverts or round other fish,:,passable round culverts. These structures are listed
in priority order, with the first' having the highest preference and the last the
lowest preference. In order for a lower priority structure to be permitted, the
applicant must show the higher priority structures are not feasible. The project
shall be designed to minimize its impacts on the environment.
ulkhead.
oins and other shoreline protection
critical salmonid
demonstrates all of the following conditions
Page 11 of 47
City of Federal Way SMP -Article III. Shoreline Management - Draft Regulations
(19) Bridges and in-water utility corridors may be located in salmon and
steelHeaGcritical habitat~ provided the proponent shows that all of the following
conditions are met: .
a. An alternative alignment is not feasible;
b. The project is located and designed to minimize its impacts on the
environment;
c. Any alternative impacts are mitigated; and
d. Any landfill is located landward of the ordinary high water mark.
Open piling and piers required to construct the bridge may be placed
waterward of the ordinary high Water mark, if no alternative method is feasible.
Netwithstanding subsoction (kQ1('1) of this secti9R;-WWhen installing in-
water utilities, the installer may place native material on the bed and banks of the
water body or wetland to re-establish the preconstruction elevation and contour
of the bed. The project shall be designed to avoid and minimize its impacts on
the environment. '
m4.G) Dredging which will damage shallow water habitat used by salmon
and steelhead for migration corridors, rearing, feeding and refuge shall not be
~~ted unless the proponent demonstrates al~1 of the following conditions are
a. The dredging is for a water-de, ", r water-related use;
b. An alternative alignment 0' 0\ 0' ',' t feasible;
. . d. The project faCIlity ,~Ipnterest; and
e. If the project will c,~f - icant unavoidable adverse impacts, the
impacts are mitigated by cre ~ In-kind replacement habitat near the project.
Where in-kind replacement mitigation is not feasible, rehabilitating degraded
habitat may be required as a substitute.
J11) Dredging and the removal of bed materials below the water line is
prohibited ....'ithin salmon and sieelhead spawning areas.
(91112) In-water dredge spoil disposal sites shall not be located in salmon
and steelheadcritical salmonid habitats.
(10~) baRGEfilling, dredging, channelization and other activities which
negatively impact habitat values are prohibited in wetlands, ponds,. and side
channels which provide refugo or other habitat for salmon or stoelheadare
associated with critical salmonid habitats.
(114344) Within salmon and steolhoadcritical habitats, permanent channel
changes and realignments are prohibited.
J1115) Aquaculture uses-shall not be--establ+shed in salmon anG
steeJ.Readcritical salmonid habitat~, except for areas that are only used fer
migration corridors. This regulation only a'pplies to in water 3quaculture uses, not
upland 3quaculture uses.
(49124a) The removal of aquatic and riparian vegetation within or adjacent
to salmon and stoelheadcritical salmonid habitats shall be minimized. Trees
which shade side channels, streams, fivefsestuaries, ponds and wetlands tffieG
by salmon 3nd steelhoadassociated with critical salmonid habitats shall be
maintained. Areas of disturbed earth shall be revegetated.
(471349) Unless removal is needed to prevent hazards to life and property
or to enhance HsA--critical salmonid habitat~, large woody debris below the
ordinary high water mark shall be left in the waterway to provide salmon and
steel head habitat. '
Page 12 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(18) Outfalls \A.:ithin or upstream of salmon or steelhe~d spawning areas
shall be designed and constructed to minimize disturbance of salmon ane
steelhead spawning beds. (Ord. No. 98-323, S 3, 12-1-98; Ord. No. 99-355, S 3,
11-16-99)
18-165 [NEW SECTIONl Shoreline modifications
(a) Shoreline protection stabilization. Shoreline stabilization
protection may be permitted in the shoreline residential and urban
conservancy environment~, provided: [EXISTING TEXT MOVED FROM
ENVIRONMENT DESIGNATIONS SECTION BElOWl
(1) Shoreline . stabilization, includinq bBulkheads shall not be
considered an outright permitted use on the city's Pugot Sound shoreline~.
In order for a proposeG--OO~kReaG shoreline stabilization to be permitted the
City on the Puget Sound shoreline, or for a lake shore bulkhead to qualify
for the ReV'! 90.58.030 (3)(o)(iii) exemption from the shoreline permit
requirements, the city of Federal \j\fay sh311 review the proposed bulkhe3d
design as it relates to I' ,e city of Federal \Nay
sRoroline master program and must find that:
a. Erosion from waves or curr nt J
threat to a legally established i ' '
substantial accessory structu rr
shall rovide a eotechnical '
that estimates the rate of erosi '
b. N
the city of Federal V\/ay shoreline master program in protecting the site
and ~djoining shorelines than othor nonstructural alternatives such as
slope drainage systems, vegetative growth stabilization, gravel berms, and
beach nourishment, and th~t such alternatives shall be prioritized over
structural options such as bulkheads and riprap. The "softest" effective
alternative shall be utilized; and are not technically feasible or '.viII not
adequately protect a legally established primary structureresidence~ or
substantial accessory structure or public improvement;
c. The proposed shoreline stabilizationbulkheaais located landward
of the ordinary high water mark; and
d. The maximum height of the proposed bulkhoad is no more than
eRe-foot above the elevatieA-ef-axtreme high watef--9fHj4aI waters, or four
feet-~~, measured from qrade on the waterward side of the
bulkhoad. on 13kes. The proposed shoreline protection is the minimum
size necessary to protect existinq improvements; and
e. The applicant shall demonstrate that impacts to sediment
transport are minimized to the greatest extent possible; and
. f. Shoreline stabilization shall not have an adverse impact on the
. property of others and shall be designed so as not to create the need for
shoreline protection elsewhere; and
q. Shoreline stabilization shall not significantly interfere with normal
surface and/or subsurface drainaqe into the water body and shall be
constructed usinq an approved filter cloth or other suitable means to allow
, Page 13 of 47
City of Federal Way SMP -- Article III.' Shoreline Management -- Draft Regulations
passaQe of surface and Qroundwater without internal erosion of fine
material; and
h. Shoreline stabilization shall not be used to create new lands.
(2) When a bulkhead is permitted subiect to subsection (1) above, the
following standards shall applv:
. A shoreline protection project ref*icing an existing bulkhead shall be
placed along, tho same alignment as tho shorelino protection it is
replacing, subject to the following:
a. The maximum heiQht of the proposed bulkhead is no more than
one foot above the elevation of extreme hiQh water on tidal waters, or one
foot in heiQht above the elevation of ordinary hiQh water mark on lakes,
measured from qrade on the waterward side of the bulkhead; and
. WRen a bulkhead has deteriefatod such that the ordinary high
'A/ater mark has been established by the-wesence and action of-watef
landward of the existing bulkhead. then the roplacement bulkhead must be
located at or as near as possible to the actual ordinary high water mark.
b. \^/hen an existing bulkhead is being repaired by the construction
of a vertical wall fronting the existing waIH
. . .
rovided that the
or, increased in
c. Beach nourishment and big engineered erosion control projects
may be considered a normal protective bulkhead If/hen any structural
elements are consietent with the above requirements, and 'Nhen the
project has been approved by the Department of Fish and 'Nildlife.
If an existinq bulkhead deteriorates to the point it must be replaced.
fts-feplacement shall be considered a new bulkhead subiect to the
f)fevisions of subsection (1) abov&;
o Shoreline protection shall not have adverse impact on the property of
etRers and shall be designed so as-Ret to create a need f.oF-shoreline
f*9teGtten else'Nhore.
_a. Shoreline protection shall not signific:Jntly intorfere .'Nith normal
surface and/or subsurface drainage into the water body and shall be
ooflst:NGte€.H:ffiing an approved filter clothoF-etRef-SbHtaele meaflS to allew
. passago of surface and groUAtiwateF-WHHout internal eFeS!en of fine
material.
b. Shoreline protection shall not be used to create new lands,
exGep.t--tt-lat groins may used te-Greate-or ma~Jffi-GI.a&s I beach if
tRey--oomp.ly 'Nith all other conditfeflS-G4his section.~
~ Groins are permitted only as part of a public beach
management program. Jetties and breakwaters 3m not permitted.
Page 14 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(b) Piers, Docks, Mooraae, and Floats.
[EXISTING TEXT MOVED FROM ENVIRONMENT DESIGNATIONS
SECTION BELOWl
(e1) PResidential piers, docks, floats, moorage, or launching facilities;
conditionsstandards. Any pier, dock, moorage, float, or launching facility
authorized by subsections XXX of the Environmental Desiqnations section (G1
through (f) of this section shall be subject to the following conditions:
fBa. Residential piers and docks are prohibited on thePuget Sound
shoreline.
~b. Piers shall onlv be permitted for water-dependent uses and public
access.
~No dwelling unit may be constructed on a pier or dock.
~d. Excavated moorage slips shall not be permitted accessory to single
f3mily residences, multif3mily development, or 3S common use facilities
accessory to subdivisions and short subdivisions. are prohibited as accessories
to residential development.
t41ea. No covered pier, covered moorage, covered float, or other covered
structure is permitted waterward of the ordinary high water mark.
~fe. .
. n for 3 building
moora es floats and launchin facilities
shall meet the side ard setb f the underl in zonin classification exce t
in the case of shared facilities. in which case no side vardsetback is required.
~such joint use piers may be permitted up to twice the surface af€a-allewed by
this title;
f91gt All piers, moorages, floats, or other such structures shall notfloat at
all times on the surface of the water, or shall be of open pile--oonstructiaR;
provided no portion of the structure shaU,.l during the .course of the normal
fluctuations of the elevation of the water body, protrude more than five feet above
the surface of the water.
h~. -PResidential piers, docks, floats. mooraqe or launchinq facitilies must
be desiqned to meet' permit standards required by the US Army Corps of
EnQineers and Washinqton State Department of Fish and Wildlife.
, {Bi2} Residential piers, docks.. floats. moorage, or launching facilitieSi'
aGGe8sory . to resiGeRtiaJ. developmem. DPiers, docks. moorages, floats, or
launching facilities may be permitted accessory to. a single-family residence,
multifamily development, or as common use facilities assoCiated with a
subdivision, or short subdivision, in accordance with this chapter and the
following limitations:
fBa. Private, single-residence ~docks for the sole use of the property
owner shall not necessarilv be permitted outright on city of Federal VVay
shorelines.
~b. A f}ief-dock may be allowed when the applicant has demonstrated a
need for moorage and has demonstrated that the following alternatives have
been investigated and are not available or feasible:
31, Commorcial or marin;) moorage.
.g1~. Floating moorage buoys.
Page 15 of 47
I
City of Federal Way SMP - Article III. Shoreline Management - Draft Regtilations
G2J. Joint use moorage dock pfef.
No more than one dockpfef for each residence is permitted. On lots with
less than 50 feet of waterfront, only joint use .dockpfefs shall be permitted except
when abuttinq owners are not aqreeable or when both lots abutting the subject
. lot have legally established piers then the .Iot with less than 50 feet of waterfront
may be permitted an individual pier.
~c. New Mmultiple-family developments residenoe piers and piers
associated with ~ subdivisions or short subdivisions shall be permitted one
shared dock. as a common use facility shall not exceed the follOwing:
a1. No mere than one pier for ea6Jl-4QG-feet of shoreline assoGfated with
tRe-ml::ltHfamily develG~ent, subdivision, or short subdivision is permitted.
g 1.2. The total number of moorage spaces shall be limited to one
moorage space for every two dwelling units in the multi,family development,
subdivision, or short subdivision.
~d. Dock dimensionsPier rind moorage size.
AL The maximum waterward intrusion of any portion of any dockf}ief
shall be 36 feet, or the point where the water depth is 13 feet below the ordinary
high water mark, whichever is reached first., provided:
1 L If a pier i ..
to ei
e of piers, moorages, floats, and/or launching
facilities, or any combination ereof, associated with a single-family residence
shall not exceed 5.100 square feet.
_e~No pier, including finger pier, moorage, float, or over water structure
or device, sh~1I be '1.'ider than 25 percent of the lot 'Nith which it is associated.
~~Mobrage piles. Moorage piles not constructed in conjunction with a
pier are limited by the following conditions:
aLAII piles shall be placed so as to not constitute a hazard. to
navigation.
bL.No pile shall be placed more than 80 feet waterward of the ordinary
high water mark.
6~AII moorage piles shall be placed in a water depth not to exceed 13
feet below the ordinary high watermark.
. €l1:...No more than two moorage piles per residence are permitted.
(6)Launching ramps ~nd lift st~tions require ~ shomline conditional use
permit arid are limited by the following conditions:
a No portion of a launching ramp or lift station shall be placed more than
60 feet waterward of the ordinary high water mark.
b-AU-pertions of a launching r~mp or lift station sh~II be placed ~t a
depth not to exceed eightfeot belm".' the ordinary high water m~rk. ,
c L~unching rails or r~mps sh~1I be anchomd to the ground through the
use of tie type construction. ^sph~lt, concrete, or other ramps 'Nhich solidly cover
the '/Vator body bottom ~re prohibited.
. d No more than' one I~unching rail per single family residenco is
permitted, and no more than two common use launching ramps for oach 100 foet
Page 16 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
of shoreline associ3ted 'Nith 3 multif3mily development, short subdivision,. or
subdivision.
f71t Floats are limited under the following conditions:
a,L One float per single-family residence, multifamily development, short
subdivision, or subdivision is permitted.
B2. No portion of a float shall be placed more than 36 feet waterward of
the ordinary nigh water mark.
G3. Retrieval lines shall not float at or near the surface of the water.
€14. No float shall have more than 100 square feet of surface area.
@Launching Ramps and Lift Stations. Launching ramps and lift
stations require a shoreline conditional use permit and are limited by the
following conditions: [EXISTING TEXT MOVED FROM ENVIRONMENT
DESIGNATIONS SECTION BELOW]
{1} No portion of a launching ramp or lift station shall be placed more than 60
feet waterward of the ordinary high water mark.
{2} All portions of a launching ramp or lift station shall be placed at a depth
not to exceed eight feet below the ordinary high water mark.
{3} L:aunching rails or ramps shall be ancho · the ground through the use
of tie-type construction. Asphalt, concrete 0 ramps which solidly cover the
water body bottom are prohibited.
{4} No more than one laun
, and no more than onetwa co
subdivision is permitted.
ngl -family residence is permitted,
ing ramps for each new 100 feet of
development, short subdivision, or
(d) Breakwaters and Jetties. Jetties 3nd bBreakwaters and jetties are
not permitted within any shoreline of the City. [EXISTING TEXT MOVED'
FROM ENVIRONMENT DESIGNATIONS SECTION BELOW]
(e) Dredainq and Fillina.
(1) Dredqing:
a. Dredging activities in shoreline residential or urban conservancy
environments require a Conditional Use Permit and must comply with all federal
. and state requlations. Dredging is not permitted in the Natural environment.
b. Dredging activities are allowed in the shoreline residential and urban
conservancy shoreline environments only where necessary to protect public
safety or for shoreline restoration activities.
d. Drodqing of bottom materi31s for the sinqlc purpose of obt3ininq fill
matorial is prohibited. '
ec. Dredqinq and excavation in critical salmonid habitatsafeaS is
prohibited. except when required for shoreline restoration activities.
fd. Where allowed. dredqingoperations must be scheduled so as to not
damaqe shoreline ecoloqical functions or processes.
Qe. When dredqe spoils have suitable organic and physical properties,
dredqinq operators shall recycle dredqed material into areas of the City suitable
for those materials.
Page 17 of47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
f. Unavoidable impacts of dredqing shall be mitiqated as required bv this
chapter.
(2) Fillinq:
a. Fill activities shall onlv be allowed in association with allowed
(permitted) water dependent' use developments. Fill associated with non-water
dependent uses shall be prohibited. '
184i4-166 Environmental designations.
(a) Purpose and establishment of desi~nations.
!1l The purpose of these designations is to differentiate between areas whose
geographical, hydrological, topographical, or other features imply differing
objectives regarding the use and future development of the shorelines of the city.
Each environment designation represents a particular emphasis in the type of
uses and the extent of development that should occur within it. The
environmental designation. system is designed to encourage uses. in each
environment that enhance or are compatible with the character of the
environment, while at the same time requiring reasonable standards and
Page 18 of 47
I
.,
City of Federal Way SMP - Article III. Shoreline Management- Draft Regulations
. restrictions on development so that the character of the environment is not
adversely impacted. '
(9,2) Names of environment designations. In order to accomplish the purpose
of this title, environmental designations have been established to be knovm as
follows:
fBa. N3tur31 onvironmentShoreline Residential.
~b. Conservancy.residential environmentUrban Conservancy.
~c. Rural environmentNatural.
('1) Urban environment.
(G~) Limits of environment designations. Each environment designation shall
consist of:
fBa. The entire water body from its centerline or point, including all water
below the surface,' the land below the water body, the space above the water
body, and the shorelands associated with the water body.
~b. The shoreline areas within 200 feet of the OHWM. and additional
upland areas where associated severe biophysic31 constr3ints such aswetlands
and floodplains, steep slopes, slide h3z3rd areas, and wetl3nds extend beyond
200 feet from the OHWM. do not cover tho entire 3ssociated shorel3nd.
,
(EJ1) Establishment of desi
fBa. The written des
environment designations as
'dop3rtment shall constitute t~
those environment designations.
~b. The official maps prepared by the city pursuant to Chapters 173 16
ami 173-26 WAC in tho possossion of the department shall constitute the official
'descriptions of the limits of all shorelands in the city of Federal Way as' defined
by RCW 90.58.030 and FWCC 18-163.
~c. The department may, from time to time as new or improved
information becomes available, modify the official maps described in subsection
fill(€J1){2jb. of this section consistent with state guidelines to more accurately
represent, clarify, or interpret the true limits of the shorelines defined herein.
(e~) Location of boundaries.
(-1ia. Boundaries indicated as following streets, highways, roads, and
bridges shall be deemed to follow the centerline of. such facilities unless
otherwise specified.
~b. Boundaries indicated as following railroad lines and. transmission
lines shall be deemed to follow the centerline of such rights-of-way or easements .
unless otherwise specified.
~c. Where different environmental designations have been given to a
tributary and the main stream at the point of confluence,. the environmental
designation given to the main stream shall extend for a distance of 200 feet up
the tributary.
t4}d. In case of uncertainty as to a wetland or environment boundary, the
director of community development services shall determine its exact location
pursuant to the criteria of WAC 173-22-05a40 and RCW 90.58.030, and the
provisions of this chapter. (Ord. No. 98-323, S 3, 12-1-98; Ord. No. 99-355, S 3,
11-16-99 )
e boundaries of the shoreline
y ordinance in the possession. of the
. Icial legal descriptions of the boundaries of
Page 19 of 47
City of Federal Way SMP - Article III. Shoreline Man.agement - Draft Regulations
18-167 NEW SECTION Permitted Use Table
$hol'ieli~Modmcation
Shoreline Stabilization I
Protection 1
Piers. Docks. MooraQe. and
Floats2. 3
Launchinq Ramp I Lift Station
Breakwaters and Jetties
DredqinQ and FillinQ
Shoreline U.se
Office and Commercial
Development
Recreational Development
Residential Development
Accessorv Structures
Utilities5
Transportation I ParkinQ
Facilities6 .
Aquaculture
Community Boatinq Facilities7
P = Allowed as exempt from permittinq or permitted with Substantial Development Permit
C = Mav be allowed with Shoreline Conditional Use Permit
X = Prohibited
1, Includes bulkheads. bio-enqineered erosion control proiects. qroins and other shoreline
stabilization activities, Groins may onlv be permitted as part of a public beach manaqement
prOQram,
2. Code provisions address these modiffcations as accessory to residential uses.
3. Residential piers and docks are prohibited on Puqet Sound shorelines.
4. Would be permitted with Substantial Development Permit in parks and public access areas;
would be permitted with Shoreline Conditional Use permit elsewhere in Urban Conservancy
Environment
5. Solid waste transfer stations are not allowed
6. ParkinQ as a primary use is prohibited in all environments. but allowed if servin!:! an allowed
shoreline use
7, Allowed in association with recreational development
Page 20 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
18-1-65168 Urban environment Shoreline Residential.
(a) Purpose. The purpose of the "shoreline residential" environment is to
accommodate residential development and appurtenant structures that are
consistent with this chapter. An additional purpose is to provide appropriate public
access and recreational uses.
The purpose of designating the urban environment is to ensure optimum utilization
of the shorelines of the state within urbonized oreas by permitting intensivo use
and by manoging development so thot it enhonces and maintains the shorelines of
the stote f-or 0 multiplicity of urban uses. The urbon en'/ironment is designed to
.reflect a policy of increasing utilization and officiency of urban are3s, to promote a
more intense level of use through redevelopment of areas now underutilized, and
to encourage multiple use of the shorelines of the city if the major use is 'I/ater
dependent or water related, 'Nhile ot the some time safeguarding the quality of the
environment.
(b) Designation criteria. Designation criteria for the ~shoreline residential
environment are provided in the City's shoreline master proqram. FWCC Chapter
xx. shall be:
(1) Shorelines
~
ultifamily residential
entia I purposes ond
environment shall not have-ffide.A.sive-l::>>ef)hysical limitations to development such
as floodplains, steep slopos, sliee hazard areos, and wetlan4&
(c) General requirements.
(1) Development waterward of the ordinary high water mark is prohibited
except water dependent recreational uses and public utilities.
(2) No structure shall exceed a height of 35 feet above average grade level.
This requirement may be modified if the view of any neighboring residences will
, not be obstructed, if permitted outright by the applicable provisions of the
underlying zoning,. and if the proposed development is. water-related or water-
dependent.
(3) All development shall be required to provide adequate surface water
retention, erosion control. and sedimentation facilities during the construction
period.
(4) Setbacks. Development shall maintain the first 50 feet of property obutting
. shoreline landward from the ordinary hiqh water mark as a required minimum
setback andveqetation conservation area, subiect to provisions referenced in
subsection (e). a naturol environment os required open space.
(5). Veaetation Conservation Area. Within the Veqetation Conservation Area required
shoreline setbock area. no more than 50 percent of the area with native shoreline
veqetation shall be cleared. and a minimum of 60 percent of existinq native trees shall be
retained. At least 80 percent of native trees in the shoreliRe setback area Veqetation
Conservation Area over 20 inches in diameter at breast heiqht shall be retained. Trees
determined by the city to be hazardous or diseased may be removed. Additionally. the
Director may allow removal of veqetation exceedinq that described above where an
Page 21 of 47
CitvofFederal Way SMP - A11ic1e III. Shoreline Management - Draft Regulations
applicant aqrees to replacement plantinqs that are demonstrated to provide qreater
benefit to shoreline ecoloqical processes than would be provided by strict application of
th is section.
(5) Parking facilities, except parking bcilities associ3ted with detached single
family development, shall conform to the following minimum conditions:
a. Parking facilities serving individual buildings on the shoreline shall be
located landward from the principal building being served, except when the parking
facility is within or beneath the structure and adequately screened, of--in cases
when an alternate location' would have less environmental impact on the shoreline.
1. b. Any outdoor parking area perimeter, excluding entrances and exits, must
be maintained as a planting area with a minimum width of five feet.
c. Parking as a primary use .shall be prohibited.
d. Parking in shorelino jurisdiction shall directly serve a permitted shoreline
HS&:
(em In addition to any req mposed by Chapter 21 FWCC, collection
facilities to control and separa taminants shall be required where stormwater
runoff from impervious surfaces would degrade or add to the pollution of recipient
waters of adjacent properties.
(1-Z) The regulations of this chapter have been categorized in a number of
sections, regardless of the categorization of the various regulations, aAII
development in the Shoreline Residential area must comply with aU-applicable
regulations identified within the fGeneral Development Standardsl, rShoreline
Modificationsl, and all other applicable sections of this chapter.
(d) Shoreline Modifications
[TEXT RE-ARRANGED FROM EXISTING TEXT, SHOWN DELETED
BELOW]. .
(1) Allowed modifications to the shoreline within Shoreline Residential. desiqnated
areas include the followinq:
a. Shoreline Stabilization and Sooreline Protectioo. Allowed within Shoreline
Residential desiqnated areas under. the requirements' imposed by fNEW SECTION
Shoreline Modificationsl division (a).
b, Piers. Docks, Moorage, and Floats. Allowed within Shoreline Residential
desiqnated areas under the requirements imposed by [NEW SECTION Shoreline
Modificationsl division (b). '
c. Launchinq Ramp I Lift Station. Allowed within Shoreline Residential desiqnated
areas with a Shoreline Conditional Use Permit under the requirements imposed by fNEW
SECTION Shoreline Modificatibnsl division (c).
d. DredQinQ and Filling. Allowed within Shoreline Residential desiQnated areas with
, a Shoreline Conditional Use Permit under the requirements imposed by fNEW SECTiON
Shoreline Modificationsl division (e).
Page 22 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(2) Prohibited modifications to the shoreline within Shoreline Residential desiqnated.
areas include the followinq:
a. a-,-Breakwaters and Jetties.
(e) Shoreline Uses.
(1) Allowed uses within Shoreline Residential desiqnated areas include the following:
a. Residential Development. Sinqle-family and multiple-family residential
development may be permitted in the Shoreline .Residential environment subiect to the
qeneral requirements of Chapter. 22 FWCC. Article XI. Divisions 3 and 4, and the
following:
1. Sinqle-family or multiple-family, residential development is permitted in the
underlyina zone classification.
2. Residential development is prohibited waterward of the ordinary hiqh water
mark.
bb. If the property is developed with a sinqle f3mily home beyond the
strinqline setback or within 50 feet of the ordinary high 'N3ter mark if there 3re no 3diacent
residences. then the residence can onlv be added to if the addition "viii not make the
structure any more nonconforminq as to its setback and the heiqht of the addition within
the setback aroa is not increased, or the applicant may request a shoreline variance and
conditional use permit.
GG aa. If sinale-family residential development is proposed on a lot where
properties on at least one adiacent to both sides of the lot are developed in sinqle-family
residences located less than 50 feet from the OHWM. then the proposed residential
development may be located the same distance from the OHWM as the adiacent
residences (usinq strinqline method) 9f-but shall in no case be closer than 30 feet from
the OHWM. ~ . ,
dd. If the residential development is proposed on shorelines that include'
one or more sensitive areas, as defined in Chapter 22 FVVCC, such development shall
maintain setbacks in accordance with the roqulations and procedures set forth in Ch3pter
22 F'NCC, Article XIV. .
iL Multifamily residential development shall maintain a minimum setback
behind the strinqline setback.. or of 75 feet from the OHWM as a veqetation conservation
area, ',Nhichever is greater. except in the followinq cases:
. aa. If the' property is undevoloped 3nd reasonable use of the property
cannot occur without further encroachment of the setback due to phvsical constr3ints of
the lot. then the setback can be reduced to the minimum necessary in order to build 3
sinqlo family home, but in no case less than 30 feet of the ordin3rv hiqh ':.'ater mark.
beaa~ If multi-family residential development is proposed on a lot where
properties at least one aGiaGent to GsU:r-sities- side of the lot are developed in multi-family
Page 23 of 47
City of Federal Way SMP - Article III. ShoreJine Management - Draft Regulations
residential use located less than 75 feet from the OHWM, then the proposed residential
development may be located the same distance from the OHWM as the adiacent
residential uses BaS (usinq strinqline method) but shall be no closer than 50 feet from the
OHWM. If the property is developed with 3 sinqlo or multibmily structure beyond the
strinqline setb3ck or within 75 feet of tho ordin31)' hiqh 'N3ter m3rk if there are no 3diacent
sinqle or multifamilv structures, then tho structure C3n only be added to if tho addition will
not m3ke the structure any more nonconforminq 3S to its sotback and tho height of the
addition within the structure is not increased or the 3pplic3nt may request 3 shoreline
v3ri3nceand conditional use permit.
cc. If the 'residential development is proposed on shorelines th3t include one
or more sensitive areas, as defined in Ch3pter 22 FVVCC, such development ch311
m3intain setb3cks in accordance with requl3tions and procedures set forth in Chapter 22
F\^.lCC, Article XIV.
b. -Accessory Structures. Rresidential accessory structures may be placed
within the required shoreline setback, provided:
1. No more than one accessory structure. except sv.'imming pools, shall cover
more than 150 s uare feet or to a maximum of 300 s uare feet of accesso structure
area.,:,
is
c. Recreational Oevel nt. Recreational develo ment ma be ermitted in the
Shoreline Residential environment subiect to the qeneral requirements of this chapter,
provided: '
1. The recreational development is permitted in the underlyinQ zone.
2. Swimminq areas shall be separated from boat launch areas.
3. The development of undervl3ter sites for sport divinQ shall not:
i. T 3ke pl3ce at depths of qreater than 80 foet.
ii. Constitute a navif.ptional hazmd.
. Hi. Be located in 3reas whore the normal waterborne traffic 'Nould constitute
a h3z3rd to those people who m3V use such 3 site.
43. The construction of swimming facilities, piers, moorages, floats, and
launching facilities below the ordinary hiQh water mark shall be Qoverned by the qeneral
requirements of this chapter.i.
5. Public boat launchin!:! facilities may be developed, provided:
i. The parkin!:! and traffic Qenerated by such a facility can be safely and
conveniently handled by the streets and areas servinq the proposed facility.
ii. The facility will not be located on a class I beach area or cause net loss in
shoreline function.
,. 6. Upland facilities constructed in coniunction with a recreational development
shall be set back and/or sited to avoid cont3mination adverse impacts to the functions of
the shorelines of the city.
7. Public pedestrian and bicycle pathways shall be permitted adiacent to water
bodies. Such trails and pathways must be made of pervious materials, if feasible.
8. Public contact with unique and fraQile areas shall be permitted where it is
possible without destroyinQ the natural character of the area.
Page 24 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
9. Water viewinq, nature study, recordinq, and viewinq shall be accommodated
by space, platforms, benches, or shelter consistent with public safety and security.
d. Community BoatinQ Facilities. Allowed in association with recreational
development. as requlated under the requirements imposed by (e) Shoreline Uses,
subsection 1.
resources.
ii. Minimize scarrinq of the landscape.
iii. Minimize siltation and erosion,
iv. Protect trees, shrubs, qrasses, natural features, and topsoil from
drainaqe.
V. Avoid disruption of critical aquatic and wildlife staqes.
45. Rehabilitation of areas disturbed by the construction and/or maintenance of
utility facilities shall:
i. Be accomplished as rapidly as possible to minimize soil erosion and to
maintain plant and wildlife habitats. .
ii. Utilize plantinas--ooFAi*ltibJe-with-the-native trees and shrubs. vef,letaOOR7
56. Solid waste transfer stations shall not be permitted within the shorelines of
the state.
f. ParkinQ facilities.. Parkinq, except parkinq facilities associated with detached
sinqle-family development, shall conform to the followinq minimum requirements
conditions:
1. Parkinq facilities servinq individual buildinqs on the shoreline shall be located
landward from the principal buildinq beinq served, except when the parkinq facility is
within or beneath the structure and adequately screened. or in cases when an alternate
location would have less environmental impact on the shoreline.
Page 25 of 47
City of Federal Way SMP - Article III. Shoreline Marlagement - Draft Regulations
2. Any new development or expansion of existinq development creatinq qreater
than 6 total parkinq stalls must meet the water Quality standards required by the Kinq
County Surface Water Manual for "hiqh use" sites and "resource stream protection" (See
Sections 1.3.4 Special requirement oil control. 6.1.5 HiQh use menu, and Resource
stream protection of Kinq County's Surface Water Desiqn Manual).
23. OAnvoutdoor parkinq areas shall provide landscapinq pursuant to FWCC
Chapter 22. perimeter. excludinq entrances ~:md exits, must be maintained as a pla~
area with a minimum width oHive feet.
i. One live tree 'Nith a minimum heiqht of four foet shall be required f{)r each
JO linear feet of plantinQ area.
iLOne live shrub of one qallon container size, or larqor, for each 60 linear
inchos of plantinq area shall be required. ,
iii. /\dditional perimeter and interior landscaping of parking areas may be
required, at the discretion of the director, '....hen it is necessary to screen parkinq areas or
whon large parking areas are proposed. .
J4. Parkinq as a primary use in shoreline iurisdiCtion shall be prohibited.
45. Parkinq in the shoreline iurisdiction shall directlv serve a permitted shoreline
use.
2 Prohibited
include:
a. a-Office and Comme .
b. Aquaculture. '
Residential desi nated areas
Page 26 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(d) Residenti31 developmeHt [REARRANGED WITHIN SHORELINE USES
SECTION ABOVEl . Single family and multiple family residenti31 development
m3Y be permitted in the urb3n environment subject to the gener31 requirements of
Chapter 22 FWCC, Article XI, Divisions 3 and -1, 3nd the following:
(1) Single family or multiple bmily residential development is permitted in the
underlying zone c13ssific3tion.
(2) Residenti31 develepment is prohibited w3terward of the ordin3ry high water
~.
(3) Setbacks.
a. Single family residenti31 developmentsh311 m3int3in 3 minimum setb3ck
behind the stringline setb3ck, or 50 f.eet from the ordin3ry high water mark,
whichever is greater, except in the f{)lIov.'ing coses:
1. If the property is undeveloped 3nd reasonable use of the property
C3nnot occur '.vithout further encro3chment of the setb3ck due to physical.
constr3ints of the lot, then the director of community dovelopment services can
reduce tho setb3ck to the minimum necess3ry in order to build a single bmily
home, but in no C3se less than 30 feet from the ordinary high water m3rk. For the
~ . u.' .
the addition 'Nithin the setbacK area is not increased, or the applic3nt may request
a shoreline v3riance and conditional use permit.
3. If single family residential development is proposed on 3 lot \"o'here
properties adjacent to both sides of the lot 3re developed in single bmily
residences located less than 50 feet from the ordin3ry high water mark, then the
proposed residential development may be loc3ted the S3me dist3nce from the
ordinary high water mark 3S the adjacent residences (using stringline method) or
30 feet from the ordinary high V.'3tor mark, whichever is greater.
, :1. If the residential development is proposed on shorelines that include
one or more sensitive are3S, 3S defined in Chapter 22 F\^jcc, such development
Sh311 m3intain setbacks in accord3nce with the regul3tionsand procedures sot
forth in Chapter 22 F'lVCC, Articlo XIV.
b. Multifamily residential development shall m3int3in 3 setb3ck behind the
stringline setb3ck, or 75 feet from the ordinary high w3ter m3rk, whichever is
gre3ter, except in the following cases:
'1. If the property is undeveloped 3nd reasonable use of the property
cannot, occur without further encro3chment of the setb3ck due to physical
constraints of the lot, then the setb3ck C3n be reducod to the minimum necessary
in order to build a single bmily homo, but in no case less than 30 f.oet of the
ordin3ry high water mark.
2. If the property is developed with 3 single or multifamily structure
beyond the ctringline setb3ck or within 75 foet of the ordin3ry high wator mark if
there are no adjacent single or multifamily structures, then the structure can only
be added to if the addition will jqot m3ke tho structure any more nonconforming as
Page 27 of 47
~8.9f-A
\
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
8butting tho subject lot havo logally established piors then tho lot 'Nith less th8n 50
feet of waterfront may bo permitted 8n individual pier.
(3) Multij:>le f-amily residence piers and piers 8ssocbted with 8 subdivision as a
common use facility shall not exceed the follmving: ,
8. No more than one pier for o3ch 100 feet of shoreline 8ssociated with the
multifamily development, subdivision, or short subdivision is permitted.
b. The tOt8/ numbor of moor3go sp3ces sh311 be Iimitod to one moor8go
sp3ce for every DNO dwelling units in the multifamily development, subdivision, or
short subdivision.
(-1) Pier 3nd moor8ge size.
a. The i'T13ximum w3terward intrusion of 3ny portion of 3ny pier Sh311 be 36
feet, or the point where the water depth is 13 feet bolow the ordin3ry high w3ter
mark, whichever is reached first, provided:
1. If 3 pier is 8 common use pior 3ssoci3tod with 8 multiple family
development or subdivision, this intrusion m8Y be incro8sed four feet for each
3dditional moorage sp3ce over six moor8ge sp3ces to a m8ximum of 76 foet.
b. The maximum width of each pior sh311 bo eight foot.
c. No float sh311 have more than 100 square feot of surf3ce area.
,
sh311 not exceed 500 SqU3ro foet.
. . . .
a. All piles shall be placed so 8S to not constitute 8 h3zard to n8vigation.
b. No pile sh311 bo pl8cod morc th8n 80 f.eet waterw8rd of the ordin8ry high
w3tor mark.
c. /\11 moorage piles shall be placed in 3 '113ter depth not to exceed 13 feet
belo'!: tho ordin31)' high '/later m3rk.
d. No more than two moor3ge piles per residence 8re pormittod.
(6) L3unching r8mps 8nd lift st8tions require 3 shorelino condition31 use pormit
and are limited by tho following conditions:
a. No portion of a 13unching ramp or lift station shall bo placed moro th8n 60
feet wateIV/8rd of the ordinary high water mark.
b. /\11 portions of a 13unching ramp or lift st8tion sh811 be pl8cod 3t 8 depth
not to excood eight feot bolm~J the ordinary high '....ater mark.
c. L3unchingr8ils or r3mps shall be 8nchored to the ground through tho use
of tie type construction. Asph3lt, concrete, or other r8mps which solidly covor the
w3ter body bottom 8re prohibitod. '
d. No more th3n one launching rail por single family residence is permittod,
and no more than two common use launching r3mps for e3ch 100 feet of shoreline
8ssociated 'Nith 8 multif-amily dovelopment, short subdivision, or subdivision.
(7) Fl03ts 3re limited under the follO\Ning conditions: .
a. Ono fl08t per single family residenco, multif8mily development, short
subdivision, or subdivision is permitted.
b. No portion of 3 fJ08tSh811 be placed more than 36 feot v.'8ter#3rd of the
ordinary high water mark. ,
c. Retriev31lines sh811 not float 8t or near th.e surface of tho w3ter.
~eat-sh311 h8ve more th3n 1 OCk€iuare feet of surface are3.
Page 29 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Jg) Utilities[REARRANGED WITHIN SHORELINE USES SECTION ABOVEh
Utility faffiJ.H:ies may be permitted in the urban environment subject to the
requirements of this chapter, provided:
(1) Utility and transmission f::.lcilities shall:
a. Avoid disturb::.lrice of unique and fragile are::.ls.
b. Avoid disturbance of wildlife spawning, nesting, and rearing areas. .
G. Overhead utility facilities shall not be permitted in public p::.lrks,
monuments, scenic, recreation, or historic areas.
(2) Utility distribution and transmission facilities shall be designed so as to:
a. Minimize visual impact.
b. Harmonize 'Nith or enhance the surroundings.
c. Not create a need for shoreline protection.
d. Utilize to the greatest extent possible natural screening.
(3) The construction and maintenance of utility bcilities sh::.lll be done in such a
W::.ly so ::.lS to:
::.l. Maximize the preservation of natur::.ll be::.luty and the conservation of
resources.
b. Minimize scarring of the landscape.
c. Minimize siltation ::.lnd erosion.
drain::.lge.
utility facilities shall:
maintain plant and wildlife habitats.
b.Utilize pkmtings compatible with the native veget::.ltion.
(5) Solid waste transfer stations ch::.lll not be permitted 'v"..ithin the shorelines of
the state..
(h) Office and commercial development [REARRANGED WITHIN SHORELINE
USES SECTION ABOVE]. Office development may be allowed in the urban
environment subject to the requirements of this chapter, provided:
(1) The office or commercial use or activity is permitted in the underlying zoning
classification.
(2) Office and commercial development shall maintain a setb::.lck behin€J-tt::le
stringline setb::.lck, or 75 feet from the ordinary high 'I.'::.lter mark, whichever is
greater, except in tho following cases:
a. If the property is developed with a structure vl.'ithin 75 f.oet of the ordinary
high water mark, then the structure C::.ln only be added to if the addition will not
m::.lke the structure any more nonconforming as to its setback.
b. If a development is proposed on shorelines that include one or more
sensitive areas, 3S defined in Chapter ~ FVVCC, such development sh311 m3int3in
sefuacks in accordance with regulations and procedures set forth in Chapter ~
F'NCC, Article XIV.
(3) Piers, moorages, floats, jnd l::.lunching facilities v.'i11 not be permitted in
conjunction 'Nith office or commerci~1 development; unless they are developed as
part of on sito public 3ccess to the shoreline. '
. Ji) Shoreline protection. Shoreline protection may be permitted in the urban
environment, provided:
Page 30 of 47
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_~ REARRANGEO WllH'N sHoREuNE USESSEC110N
ABOVE1' . ~"-~ -..,"" .
~~~_u. ,W""-Q;
~31..Qi 4'
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City of Fede.ral Way SMP - Article III. Shoreline Marlagement - Draft Regulations
(1) The recre8tional development is permitted in the underlying zone.
(2) Swimmin~eas shall be separ3ted from boat launch areas.
~) The development of under\\'ater sites for sport diving shall not:
a. Take place at depths of greater than 80 feet.
b. Constitute 8 navigational h8zard.
c. Be located in areas where the normal 'Naterborne traffic would constitLJte
a hazard to those poople 'Nho m8Y use such a site.
("1) The construction of s'Nimming facilities, piers, moorages, floats, and
launching facilities below the ordinary high w8ter mark shall be governed by the
regulations of subsections (e) and (f) of this section.
(5) Public boat bunching facilities may be developed, provided:
3. The traffic generated by such 8 facility'can be safely and conveniently
handled by the streets serving the proposed facility. .
, b. The faciiity will not be loc3ted on a cbss I beach.
(6) Upland facilities constructed in conjunction with a recredtional development
shall be set back 3nd/or sited to 3void contamination of the shorelines of the city.
(7) Public pedestrian and bicycle pathways shall be permitted adjacent to water
bodies.
shall 3110w the upstream migration of adult.fish. Fish bypass facilities shall prevent
fry and juveniles migr3ting do'tlnstream from being trapped or harmed.
(2) Landfills shall not intrude into salmon and steelhead h8bitats, except as
provided in subsection (k)(3) of this section.
(3) Landfills m3Y intrude into salt w3ter are3s used by s81mon and steelhe3d for
migr3tion corridors, rearing, feeding 3nd refuge only where the proponent obtains'
a conditional use permit (CUP) and demonstrates all of the follmNing conditions are
meF.
a. The bndfill is for w3ter dependent or 'N3ter related use;
b. /\n.alternative alignment or location is not fe3sible;
c. The project is designed to minimize its impacts on the environment;
d. The facility is in the public interest; and
e. If the project will create significant unavoidable 8dverse impacts, the
impacts are mitigated by cre8ting in kind replacemont habitat ne3r the project.
V\!here in kind repl8cemont mitigation is not feasible, rehabilitating' degraded
h3bitat may be required asa substitute.
(4) Unless the 3pplicant demonstrates that bioengineering techniques 'Nill not
be successful, bulkheads and other shoreline protection structures 3re prohibited
in salmon and steelhead habitat. .
(5) Where bulkheads 3nd other shoreline protection structures are allowed, the
toe of the bulkhead or structure shall be located landward of the ordinary high
water mark except as providod in subsection (k)(6) of this section. Where an
existing bulkhead or structure cannot be removed because of environmental,
saf.ety, or geel~~I-ooA€erns, tho least eAVifenmentally impacting alternative shaU
Page 32 of 47
City of Federal Way SMP - A11icle III. Shoreline Management - Draft Regulations
be usod. Any rep/::lcomont bulkheGd or shoreline protection structure shall be ::lS
etase to the existing structure as possible:
(6) Bulkhe::lds, breakwaters, jotties, groins ::lnd othor shoreline protection
structures m::lY intrudo into salmon and stoelhoGd h::lbitats only 'Nhero the
proponont domonstratos all of the fn/lowing conditions aro met:
a. An ::llternativo alignment or location is not feasible;
b. Tho projoct is dosignod to minimize itsimp::lcts on the environment;
c. Tho facility is in the public intorest; ::lnd
d. If the projoct will creGte significant unavoidable adverse impacts" the
imp~cts are mitigated by creating in kind replacement habitat nO::lr the proje6t-:
Whore in kind replacemont mitigation is not fOGsible, rehGbilit::lting dogradod
habit::lt m::lY bo requirod as a substitute.
(7) Docks, piers, pilings and flo::lts m::lY bo loc::lted in 'Nater ::lreas used by
salmon and steolhoad for migration corridors, re::lring, feeding and refuge,
provided tho bcilitios use open piling construction. Appro::lch fills sh::lll be loc::lted
l::lndward of the ordinary high 'Nator mark. Docks, piers, pilings and flo::lts sh::lll not
be loc::ltod in other salmon ::lnd stool head . habitats. The project shall be dosigned
to minimizo its impacts on the environment.
, . .
Tho proj
> ,(9) Bridgos ~md in w::ltor utility corridors may bo 10cGted in salmon and
stoelhead habitat provided the proponent showsth::lt all of the following conditions
are met:
a. An ::llternative ::llignmont is not feasiblo;
b. The projoct is locatodand designod to minimizo its impacts on the
environment;
c. Any alternativo impacts are mitigated; and
d. Any landfill is located landward of the ordinary high water mark. Opon
piling and piors required to construct tho bridgo m::lY bo placed wator\vard of tho
ordinary high wator mark, if no altornativo mothod is feasible. '
Notwithstanding subsoction (k)( '1) of this section, when installing in water
utilities, the installer may placo native material on tho bed ~md banks of the '.vater
body or 'Notland to re ostablish the preconstruction olovation and contour of tho
bod. The project shall be designod to minimizo its impacts on the onvironmont.
(10) Dredging which 'Nill damago sh::lllo'.... W::lter habitat used by s::llmon ::lnd
steelhoad for migration corridors, re::lring, foedingand refuge shall not bo allowed
unless the proponont demonstrates all of the following conditions ::lre met:
a. The dredging is for::l 'Nator dependont or wator rolatod use; .
b. An alternativo alignmont or loc::ltion is not foasiblo;
c, The project is designed to minimize its impacts on the environment;
d. The facility is in the public intorost; ::lnd
e. If tho projoct v.'ill cre::lto significant un::lvoidable adverse impacts,. th.e
imp::lcts are mitigated by creating in kind replacoment habitat noar the project.
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
VVhero in kind rop/8cement mitigation is not fe8sible, rehabilitating dogradod
habitat may bo required as a substitute.
(11) Dredging and the removal of bed materials beloV': the w8ter line is
prohibited v:ithin s81mon and steelhe8d spavming aroas.
(12) In wator dredge spoil oisposal sitos shall not bo locatod in salmon and
steolhead habitats.
(13) Landfilling, dredging, ch8nnoliz8tion 81")d othor 8ctivities which nog8tivoly
impact h8bitat valuos are prohibited in wetlands, ponds, and side ch8nnols 'I/hich
provide refuge or other h8bit8t for s8/mon or stoolh08d.
(11) \^!ithin salmon and steel head habit8ts, permanent channel changos and
realignmonts are prohibited.
(15) /\qu8culture uses shall not be ostablishod in s81mon 8nd steelhoad habit8t,
excopt for areas that are only usod for migration corridors. This regulation only
applios to in '/later aquaculture usos, not upl3ndaquaculture usos.
(16) Tho removal of 8quatic 8nd ripari8n vegotation. within or 8dj8cont to
salmon 8nd stoelhoad habit8ts sh811 be minimizod. Treos which shade sido
ch8nnols, stroams, rivers, ponds 8nd 'Netlands usod by s81mon and steolhoad
shall bo maintainod. I'.reas 'of disturbed earth sh811 be roveget8tod.
. .
Page .34 of 47
City of Federal Way SMP - A11icle III. Shoreline Management - Draft Regulations
18466169 Rural Urban Conservancy environment.
(a) Purpose. The purpose of the "urban conservancy" environment is to protect
and restore ecological functions of open space, flood plain and other sensitive
lands where they exist in urban and developed settinqs. while allowinq a variety of
compatible uses. The purpose of designating the rural ,environment is to restrict
intensive development, function as ~ buffer between urb~n areas, and maintain
open sp~oes and opportunities for rocre~tion uses within tho ecological c~rrying
cap~city of the land and water resource. New developments in ~ rural environment
should reflect the character of the surrounding 3rea by limiting intensity, providing
porm~nent open space, ~nd maintaining adequ~te building setb~cks from the
wjter to prevent shoreline resources from being destroyed for other rur~1 types of
~
(b) Desianation criteria. Desiqnation criteria for the Urban Conservancy
environment are provided in the City's shoreline master proqram. FWCC Chapter
xx shall bo:
are3s, and/or wetlands.
(c) General requirements.
rural environment shall be tho S3me ~s those for tho urb~n environment, FVVCC
18 165(c). ,
(1) Development waterward of the ordinary hiqh water mark is prohibited
except water dependent recreational uses and public utilities.
(2) No structure shall exceed a heiqht of 35 feet above averaqe grade level.
This requirement may be modified if the view of any neighborinq residences will
not be obstructed. if permitted outriqht by the applicable, provisions of the
underlyinq zoninq, and if the proposed development is water-related or water-
dependent.
(3) All development' shall be required to provide adequate surface water
retention and sedimentation facilities durinq the construction period.
(4) Developmont shall maintain tho first 50 feot of property ~buttinq ~ n~tural
environment 3S required open sp30e. Setbacks. Development shall maintain the
first 50 feet of property- landward from the ordinary hiqh water mark as a required
setback and veqetation conservation area, or development shall maintain 25 feet
from the top of bluffs in the shoreline iurisdiction. whichever is the qreater setback.
Setback shall be subiect to provisions referenced in subsection (e),
5). Veaetation Conservation in Setback. The required setback area shall be
considered a Veqetation conservation area. Within the required shoreline setback
aVegetation Conservation Area, no more than 30 percent of the area with native
shoreline vegetation shall be cleared. and a minimum of 70 percent of existing native
trees shall be retained. At least 80 percent of the native trees in the Veqetation
Conservation Area chorelino setback ~rea over 20 inches in diameter at breast heiqht
Page 35 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
shall be retained. Trees determined by the city to be hazardous or diseased may be
removed. 'Additionally, the Director may allow removal of veqetation exceedinq that
described above where an applicant aqrees to replacement plantinQs that are
demonstrated to provide qreater benefit to shoreline ecoloqical processes than would be
provided by strict application of this section.
(d) Shoreline Modifications. ,
(1) Allowed modifications to the shoreline within Urban Conservancy desiqnated areas
include the followinq:
a. Shoreline Stabilization ~md Shoreline Protectioo. Allowed within Urban
Conservancy desiqnated areas under the requirements imposed by rNEW SECTION
Shoreline Modificationsl division (a).'
b. Piers, Mooraqe, and Floats.. Allowed within, Urban Conservancy desianated
areas under the requirements imposed by rNEW SECTION Shoreline Modificationsl
division (b). '
c. Launchinq Ramp I Lift Station. Allowed within Urban Conservancy desiqnated
areas with a Shoreline Conditional Use ermit under the re uirements im osed b' NEW
SECTION Shoreline Modifications division c t under the followin condition:
1. Permitted with Substantial Dev t Permit in arks and ublic access
areas' within the Urban Conservanc
d.Ored in and Fillin .
a Shoreline Conditional Use Rr
Shoreline Modifications divisi,...
2 Prohibited modificatio
areas include the followinq:
a. Breakwaters and Jetties.
, (e) Shoreline Uses.
(1) Allowed uses within Urban Conservancy desiqnated areas include the followinq: .
a. Residential Development. Allowed within Urban Conservancy desiqnated
areas under the requirements imposed within rNEW SECTIONl Shoreline Residential,
division (e), (1), b, with the followinq additional restrictions:
1. Setbacks. Residential development shall maintain a minimum setback of 50
feet from the ordinary high water mark, or 25 feet from the top of bluffs. whichever is
greater., Exceptions to minimum setback requirements included in rNEW S'ECTIONl
Shoreline Residential. division (e), (1), b, for both sinqle-family and multi-family
development. where in no case shall a setback less than 30 feet from OHWM for sinqle-
family or 50 feet from OHWM for multi-family. or 25 feet from top of bluffs be ailowed.
b. Accessory Structures. Allowed within Urban Conservancy desiqnated areas
under the requirements imposed within rNEW SECTIONl Shoreline Residential. division
(e), (1), c.
c. Recreational Development. Allowed within Urban Conservancy desiqnated
areas under the requirements imposed within rNEW SECTIONl Shoreline Residential.
division (e), (1), a. '
d. Community BoatinQ Facilities. Allowed in association with recreational
development, as requlated under the requirements imposed within rNEW SECTIONl
Shoreline Residential, division (e), (1), b. .
e. Utilities. Allowed within Urban Conservancy desiqnated areas under the
requirements imposed within rNEW SECTIONl Shoreline Residential. division (e). (1), d.
nated areas'with
NEW SECTION
Page 36 of 47
City of Federal Way SMP - Aliicle III. Shoreline Management - Draft Regulatio{ls
f. Transportation I Parking Facilities. Allowed within Urban Conservancy
desiqnated areas under the requirements imposed within [NEW SECTIONl Shoreline
Residential. division (e). (1), e.
q. Office and Commercial Development. Office development may be allowed
with Conditional Use approval in the Urban Conservancy environment subiect to the
requirements of this chapter. provided: .
1. The office or commercial use or activity is permitted in the underlvinq zoninq
classification.
2. Office and commercial development shall maintain a setback behind the
strinqline setback. or of 75 feet from the ordinary hiqh water mark, or 25 feet from the top
of bluffs. whichever is qreater. whichever is lessUsinq the strinqline setback. the
minimum buffer shall be bHt-in no case less than 50 feet from OHWM or 25 feet from the
top of bluffs.qreater. except in the followinq cases:
, i. If the propertv is developedi.vith <3 structure within 75 feet of the ordinary
high water mark, then the structure can only be added to if the addition will not make the
structure any more nonconforminq as to its setback.i. Structures shall be setback the
Article XIV.
3. Piers moora es
con'unction with office or com
on-site ublic access to the sh
4. Additional water quality standard must be met as per Shoreline Residential.
section 18-167 (f)(2 )..,-
(2) Prohibited uses within Urban Conservancy designated areas include:
a. Aquaculture.
(d) Residential devolopment. Single family residential development may be
permitted in the rural environment subject to the general requirements of the
residential pro'.'isions of FVVCC 18 165(d) of the urban environment.
(0) Residential piers, moorage, or launching facilities. Piers, moorages, floats,
or launching facilities may be permitted accessory to n single family residence in
accordance with FVVCC 18 165(0) and (f) of the urban environment.
(f) Subdivisions. The lot standards enumerated in this section apply to any lot
that has buildable area \"lithin the shorelines of the city. Buildable .area menns that
nreo of the lot, exclusive of any required open space, yards, or setbacks upon
which n structure may be constructed.
(1) The minimum required area of a lot in the rural environment shall be five
acres; provided. however:
o. The minimum lot area may be reduced to 15,000 square foot whon:
1. All lots are part of nn approved subdivision or short subdivision.
2. 1\lIlot6 are served by public 'Nater.
3. I\II1ot5 are served by an apf)ffiveEl-sewage disposal-system.
Page 37 of 47
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Ci{y of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
1846+170 Conservancy rosidontialNatural environment.
(a) Purpose. The purpose of the "natural" environment is to protect those
. shoreline areas that are relativelv free of human influence or that include intact or
minimallv deqraded shoreline functions intolerant of human use. These systems
require that only very low intensity uses be allowed in order to maintain the
ecoloqical functions and ecosystem-wide processes. Consistent with the policies of
the desiqnation. local qovernment should include planninq for restoration of
deqraded shorelines within this environment. Conserv~ncy residenti~1 areas ~re
intended to maintain their existing ch~racter. This designation is designed to
protect, conserve, and m~n~go existing natural features and resources. The
preferred uses ~re those nonconsumptive of tho physical ~nd biologic~1 resources
of the ~roa.
(b) Designation criteria. Desiqnation criteria for the Natural environment are
provided in the City's shoreline master proqram, FWCC Chapter xx.Design~tion
criteria for the consorvancy N~tur~1 environment shall be:
(1) Shoreline ~re~s, reg~rdless of the underlying zoning, . which h~ve
environment~lIy sensitivo ~re~s as ~quifor' recharge are~s., fish and wildlife habitat,
siqnificant ~dverse . imp~cts to ocoloqical functions or risk to human
s~fetV.Shorelino are~s 'Nhich arc free from extensive devolopment.
(1) Shoreline ~reas of high scenic value.
(1)/\ shoreline are~ that provides food. water. or cover and protection f.or ~nv
r~re. endanqered. or diminishinqthreatoned species. rTEXT. MOVED FROM
NATURAL BElO\^J1
(5) l\ seasonal h~ven for concentr~tions of native animals. fish, or fO'.'V1. such as
~ miqr~tion route. breedinq site. or spa'Nninq site. rTEXT MOVED FROM
NATURAL BElO'.^Jl
(6) Shoreline ~roas with established histories of scientific resoarch.
(7) Those shoreline are~s h=:lving ~n outsbndinq or unique scenio feature in
their natural state. rTEXT MOVED FROM NATURAL BELO'Nl
(8) In addition to the above criteria, the followinq should bo considered when
desiqnatinq natural environments: rTEXT MOVED FROM NATURAL BELO'.^Jl
~. Areas 'Nhere human influence and development are minimal.
b. Areas capable of o~silv beinq restored to a n~tur~1 conditions.
c. S~ltvJ~ter wotlands.
d. Class I be~ches.
(c) General requirements.
(1) Development waterward of the ordinary hiqh water mark is prohibited
except water dependent recreational uses and public utilities.
(2) No structure shall exceed a heiqht of 35 feet above averaqe qrade level.
This requirement may be modified if the view of any neiqhborinq residences will
not be obstructed. if permitted outriqht by the applicable provisions of the
Page 39 of 47
City of Federal Way SMP - Article III. Shorehne Management - Draft Regulations
underlvinq zoning. and if. the proposed development is water-related or water-
dependent.
(3) All development shall be required to provide adequate surface water
retention and sedimentation facilities durinq the construction period.
('1) Development sh311 maintain the first 100 feet of property abuttinq 3 n3tural
environment as required opon sp3ce.
(4) Setbacks. Development shall maintain the first 100 feet of property
landward from the ordinary hiqh water mark as a required setback and veqetation
conservation area, or development shall maintain 50 feetfrom the top of bluffs in
the shoreline iurisdiction. whichever is the qreater setback. Setback shall be
subiect to modifications referenced in Section xx.
(d) Shoreline Modifications. The followinqshoreline modifications are
prohibited within Natural desiqnated shoreline areas:
(1) Shoreline Stabilization-and Protection;
(2) Piers. Docks. Moorages. and Floats;
(3) Launchinq Ramp I Lift Station;
(4) Breakwaters and Jetties; and
(5) Dredginq and Filling..
(e) Shoreline Uses.
(1) Allowed uses within Naturaldesiqnated areas include:
a. Residential Development Sinqle-family residential development may be
permitted in the Natural environment with a Shoreline Conditional Use Permit subject to
the qeneral requirements of Chapter 22 FWCC. Article XI, Divisions 3 and 4. and the
following:
1. Single.familY-Gr multiple family residential development is permitted in the
underlyinq zone classification.
2. Sinqle-family rResidential development is prohibited waterward of the ordinary
high water mark.
3. Setbacks.
i. Sinqle-familv residential development shall maintain a minimum setback behind
the strinqline sotback, orof 100 feet from the ordinary hiqh water mark as a veqetation
conservation area. or 50 feet from the top of a bluff. whichever is qreater.v.'hichever is
lessqreater. except in the follO'.vinq cases:
Page 40 of 47
,
(d) Residential devolopment. Single family residential development may be
permitted in the conservancy environment subject to the gener31 requirements of
Chapter ~ F'NCC, I\rticle XI, 3nd the residential provisions of FVVCC 18 165(d} of
the urban environment; provided single family residential development shall
maintain 3 minimum setback of 50 feet from the ordin3ry high water mark, except
tRaE
(1) If the development is proposed on shorelines including one or more
sensitive areaS,3S defined in Chapter ~ FVVCC, Article XIV, such development
shall be done in accordance with that 3rticle.
(2) /\ny pier, moorage, f183t, or 13unching facility permitted accessory to single
family development, or a common use facility accessory to a subdivision or short
subdivision, shall be subject to the pier, moor3ge, f103t, and 13unching facility
provisions of FVVCC 18 165(f} of the urban environment; provided no such
authorized structure shall be located within .200 feet of any other structure.
(e) Subdivisions. The lot st3ndards enumerated in this section apply to any lot
that has buildable area 'Nithin the shorelines of the city. Buildable area means that
area of the lot exclusive of any required open sp3ce, yards, or setbacks upon
which a structure may be construGte€k
(1) The minimum required ::Iroa of a lot in the conservancy environment shall be
five ::Icres, provided, hm"levor:
::I. The minimum lot are3 may be reduced to 35,000 square feet 'Nhen:
1. ,~lIlots ::Ire p3rt of 3n approved subdivision or short subdivision.
2. All lots are served by public water.
3. ^lIlots are served by an approved sewage dispOS31 system.. '
1. Nllots are sefVed by paved streeHr.-
Page 41 of 47
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(1) If development is proposed on shorelines including one or mora sensitive
areas, as defined in C~ter ~ FV'lCC, l\rticle XIV, such development shall be
tiooe in accord~nce with reguJ.aHeAs and pffi6edures set forth in that article.
(d) Residenti31 piers, moorage, or bunching bcilities. Piers, moorages, floats,
or launching are prohibited in a natural environment.
(e) Subdivisions.
(1) The minimum required area in the natural environment shall be five acres.
(2) The minimum required lot width in the natural environment shall be 330 f.eet.
(3) ,A,ny lot located \\'holly or partially '....ithin the shorelines of the city shall be
considered 3 leg31 building site; provided, that such lot sh311 be subject to tho
substand3rd lot provisions of Chapter ~ FWCC, Article IV.
(4) Submerged land within the bound3ries of any waterfront parcel sh311 not be
used to compute lot are3, lot dimensions, Y3rds, open space, or other required
conditions of land subdivision or development.
(f)Shoreline protection. Shoreline protection is prohibited in the natural
environment.
(g) Recreation. Recreational development m3Y be permitted in the natural
environment subject to tho general requirements of this ch~pter, provided:
. ...
,
or other similar over water peoestrian structures facilitating access to observation
, points or viewing aroas may be permitted.
(h) Salmon and steelhead h3bitat. S31mon and steelhead habitat shall be
protected under FVVCC 18 165(k)(1) through (k)(18). (Ord. No. 98 323, ~ 3,12 1
98; Ord. No. 99 355, 3 3, 11 1699)
Page 43 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Division 3. Administrative Procedures
18469171 Application and public noticeShoreline Manaqement Permit and
Enforcement Procedures, Adoption bv Reference.
The city of Federal Way hereby adopts by reference the followinq sections or
subsections of Chapter 173-27. as amended. of the Washinqton Administrative
Code ("WAC") entitled Shoreiine Manaqement Permit and Enforcement
Procedures.
WAC:
(1) 173-27-020 Purpose
(2) , 173-27-030 Definitions
(3) 173-27 -040-Developments exempt from substantial development permit
requirement
(4) 173-27 -050 Letter of exemption
(5) 173-27-060 Applicability of Chapter 90.58 RCW to federal land and aqencies
(6) 173-27 -090 Time requirements of permit'
(7) 173-27 -100 Revisions to permits
8 173-27 -120 S ecial rocedure for Ii
9 173-27 -130 Filin with de artme
10 173-27 -140 Review crite ill
11 173-27-150 Review c ermits."
12 173-27 -160 Review c
13 173-27 -170 Review c
(14) 173-27-180 Applicati development. conditional
use or variance permit
(15), 173-27-190 Permits for substantial development. conditional use or variance
(16) 173-27-210 Minimum standards for conditional use and variance permits
(17) 173-27-240 Authority and purpose
(18) 173-27-250 Definitions
(19) 173-27-260 Policy
(20) 173-27-270 Order to cease and desist
(21) 173-27-280 civil penalty
(22) 173-27-290 Appeal of civil penalty
(23 )173-27 -300 Criminal penalty
(24) 173-27-310 Oil or natural qas exploration
18469-172 Permit S\lb-processing and public notice.
(a) Permit Submittal. An application fora substantial development permit shall
be made to the department of community development on forms prescribed by the
department. Upon submittal of a complete application, and required fees, the
department shall instruct the applicant to publish notices of the application at least
once a week on the same day of the week for two consecutive weeks in a
newspaper of general circulation within the city. The applicant shall also provide
additional public notice as prescribed in process IliV, FWCC 22-431 et seq. (Ord.
No. 90-38, 9 1(24.40),2-27-90; Ord. No. 97-291, 9 3, 4-1-97; Ord. No. 98-323, 93,
12-1-98; Ord. No. 99-355, 9 3, 11-16-99)
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
18 170 Procedure for review.
(b) Procedure for review. The substantial development permit shall be reviewed
under the provisions of process III, FWCC 22-386.et seq., and the WAC 173-27
procedures adopted by reference in FWCC 18-169. Tthe director of community
development services shall be the final approval authority for the permit. (Ord. No.
90-38, ~ 1(24.50),2-27-90; Ord. No. 97-291, ~ 3,4-1-97; Ord. No. 98-323, ~ 3,12-
1-98; Ord. No. 99-355, ~ 3,11-16-99)
1-8-173 Shoreline Exemption.
(a) The purpose of a shoreline exemption is to provide an approval process for
uses and activities which do not triqqer the need for a substantial development
permit. but require compliance with the shoreline quidelines and the provisions of
the City's SMP. .
(b) If the use, activity or development meets the requirements for an exemption
as per WAC 173-27-040, the applicant may submit an authorized statement of
exem tion to the director of communit develo m services for review and
approval. E
184+4-174 Shorelinevariarice.
(a) The purpose of a shore' ,:,91 .' ,0 grant relief to specific bulk, .
. dimens'ional or performance s r~~ 6rth in the shoreline master program,
and where there is an extraor ~unique circumstance relating to the property.
such that the strict implement i n of the shoreline master program would impose
unnecessary hardship on the applicant or thwart the policies of the Shoreline
Management Act.
(b),~hen a variance is requested, the substantial development permit and the
variance shall be reviewed under the provisions of process IV, FWCC 22-431 et
seq., and the hearing examiner shall be the final approval authority for the City of
Federal Way. The Department of Ecoloqy shall be the final approval authority
under WAC 173-27-200.
(c) A variqnce from the standards of the master program may be granted only
when the applicant can demonstrate that all the following conditions will apply:
(1) That the strict requirements. of the bulk, dimensional or performance
standards set forth in the master program precludes or significantly interferes with
a reasonable use of the property not otherwise prohibited by the master program;
. (2) That the hardship described above is specifically related to the property,
and is the result of unique conditions such as irregular lot shape, size, or natural
features, location of oxistinq improvements and the application of the master
program, and not for example, from deed restriction or the applicant's own actions;
(3) That the design of the project will be compatible with other permitted
activities in the area and will not cause adverse effects to adjacent properties or
the shoreline environment;
(4) That the variance authorized does not constitute a grant of special privilege
not enjoyed by other properties, and will be the minimum necessary to afford relief;
(5) That the public interest will suffer no substantial detrimental effect;
(6) That the public rights of navigation and use of the shorelines Will not be
adversely affected by the granting of the variance when the proposal is for
Page 45 of 47
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
development located waterward of the ordinary high water mark, or within
wetlands, estuaries, marshes, bogs or swamps; and
(7) That constderation has been given to the cumulative effect of like actions in
an area where similar circumstances exist, and whether this cumulative effect
would be consistent with shoreline policies or would have substantial adverse,
effects on the shoreline.
(d) Shoreline variances may not be used to permit a Use that is specifically
prohibited in an environment, or to vary uses permitted within an environmental
designation. (Ord. No. 90-38, 9 1(24.60.10 - 24.60.40),2-27-90; Ord. No. 97-291,
93,4-1-97; Ord. No. 98-323, 93,12-1-98; Ord. No. 99-355, 93,11-16-99)
18-1-72-175 Conditional uses.
(a) Conditional use permits are allowed to provide greater flexibility in varying
the application of the use regulations of the shoreline master program in a manner
which will be consistent with the policies of Chapter 90.28 RCW, particularly where
denial of the application would thwart the policies of the Shoreline Management
Act.
(b) When a conditional use is requested, the substantial development permit
and the cOhditional use shall be revi~wed un~er .~rovisions. of process IV,
FWCC 22-431 et seq., and the heanng exa~all be the final approval
. authority for the Cit of Federal Wa. hint of Ecolo . shall be the final
a roval authorit under WAC 1
(c) Conditional uses have i,~ a. ,al characteristics which require a,
special degree of control to m s compatible w.ith other existing or
permitted uses in the same enent, and to assure that the use is in the public
interest. In authorizing a condi onal use permit, special conditions may be
attached to the permit by the hearing examiner to prevent undesirable effects or
mitigate environmental impacts ofthe proposed use.
(d) Conditional use permits shall' be authorized only when they are consistent
with the following criteria:
(1) The proposed use is consistent with the policies of RCW 90.58.020 and the
policies of the master program;
(2) The use will not interfere with normal public use of surf3CO 'A'3terspublic
shorelines;
(3) The use will cause no unreasonable adverse effects on the shoreline or
surrounding properties or uses, and is compatible with other permitted uses in the
area;
(4) The public interest will suffer no substantial detrimental effect;
(5) Consideration has been given to cumulative impact of additional request~
for like actions in the area. .
(e) Other uses not set forth in the shoreline master program may be authorized
through a .conditional use permit if the applicant can demonstrate that other uses
are consistent with the purpose of the shoreline environmental desiqnation and
compatible with existinq shoreline improvements or that extraordinary
circumstances preclude reasonable use of the property; however, uses specifically
prohibited by the master program may not be authorized. (Ord. No. 90-38, 9
1(24.70.10 - 24.70.50), 2-27-90;Ord. No. 98-323, 9 3, 12~1-98; Ord. No. 99-355, 9
3, 11-16-99; Ord. No. 00-375, 92, 10-3-00)
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
1841J--176 Final approval of shoreline permits. '
(a) The director of community development shall notify the following agencies
or persons within five days of the final approval of a shoreline permit and any
variances or conditional uses granted:
(1) The applicant;
(2) The State Department of Ecology;
(4~) Any person who has submitted written comments on the application;
(~) Any person who has requested notification in writing prior to final approval
of the permit.
. (b) No work may commence on a site requiring a shoreline permit until 21 days
following the date of filing of the shoreline permit by the State Department of
Ecology, and written notification has been received from the Department of
Ecology that the appeal period 'has been initiated. (Ord. No. 90-38, 9 1 (24.80.1 0,
24.80.20),2-27-90; Ord. No. 98-323, 9 3, 12-1-98; Ord. No. 99-355, 9 3, 11-16-99)
184+4-177 Combined hearing authority.
In those cases when development propo
public hearing under the authority of othe h
be combined. (Ord. No. 90-38, 1 (.
Ord. No. 99-355, 9 3, 11-16-9
18415-:178 Alteration or rec Ion of nonconforming use or
development.
(a) Applications for substantial development or building permits to modify a
nonconforming use or development may be approved only if:
(1) rhe modifications will make the useor develop'ment less nonconforming; or
(2) The modifications will not make the use or development more
nonconforming.
, (b) A use or development, not conforming to existing regulations, which is
destroyed, deteriorated, or damaged more than 75 percent of its fair market value
may be reconstructed only consistent with regulations set forth in this article. (Ord.
No. 90-:38, 91(24.100),2-27-90; Ord. No. 98-323, 9 3,12-1-98; Ord. No. 99-355,9
3, 11-16-99)
I'] e shorelines may require a
r of this Code, the hearings may
-9 Ord. No. 98-323, 9 3~ 12-1-98;
18476--179 Shoreline environment redesignation.
Shoreline environments designated by the master program may be
redesignated by the city council upon finding that such redesignation will be
consistent with:
(1) The policies of Section 2 of the Shoreline Management Act of 1971.
(2) The goals, objectives and policies of the master program.
(3) The designation criteria of the shoreline environment designation requested.
(Ord. No. 98-323, 93,12-1-98; Ord. No. 99-355,93,11-16-99)
Page 47 of 47
City bfFederal Way SMP - Artic1e)II. Shoreline Management - Draft Regulations
CtFAN
VE~/ON
4.1 Article III
SHORELINE MANAGEMENT
Sections:
Division 1. Generally
18-161 Purpose and authority.
18-162 Jurisdiction.
1'8-163 Additional definitions.
Division 2. Shoreiine Regulation
18-164 General development standards.
18-165 Shoreline modifications.
18-166 Environment designations.
18-167 Permitted use .table.
18-168 Shoreline residential env'
18-169 Urban conservancy en
18-170 Natural environment.
f1
Division 3. It. ministrative Procedures
18-171 Shoreline management permit and enforcement procedures,
adoption by reference
18-172 Permit processing and public notice
18-173 Shoreline exemption
18- 173 Shoreline variance18-174 Conditi,onal uses
18-175 Final apporval of shoreline permits
18-176 Combined hearing authority
18-177 Alteration or reconstruction of nonconforming use or development
18-178 Shoreline environment redesignations
Division 1. Generally
18-161 Purpose and authority.
The city adopts these regulations under the authority of the Shoreline
Management Act of 1971, Chapter 90.58 RCW, as amended, and the
Shoreline Management Guidelines, Chapter 173-26 WAC. (Ord. No. 90-
38,91(24.10),2-27-90; Ord. No. 98-323, 9 3,12-1-98; Ord. No. 99-355, 9
3,11-16-99).
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City of Eederal Way SMP - Article III. Shoreline Management - Draft Regulations
18-162 Jurisdiction.
(a) The provisions of this article shall, apply tq all develop-me,:nt
proposed within the areas defined as "shorelines" in RCW ;
90.58.030(2)(d), and "shorelines of state-wide significance" in RCW
90.58.030(2)(e). The approximate location of these shorelines shall be
designated on maps maintained by the department of community
development; however, the property owner or applicant shall be
responsible for determining the exact location of the shoreline when a
permit is filed.
(b) No development shall be undertaken by any person on the
shorelines of.the state without obtaining a shoreline permit from the
department of community development, or an authorized statement of
exemption per WAC 173-27-040 and for developments exempted by RCW
90.58.140(9) and (10). (Ord. No. 90-38, 9 1 (24.30.1 0,24.30.20), 2-27-90;
Ord. No. 98-323, 93,12-1-98; Ord. No. 99-355, 9 3,11-16-99)
18-163 Additional definitions.
Unless otherwise defin, ed in this chapter, tf..,','.'.'........, nitions contained in
this chapter, Chapter 22 FWCC, Cha r '. ",) , and Chapter 173-26
WAC shall apply. . " .' ',.
Act: means the Washingto ," e Management Act,
Chapter 90.58 RCW.
Amendment means a revision, update, addition, deletion, and/or
reenactment to the Federal Way SMP.
Approval means an official action by the City of Federal Way agreeing
to submit a proposed SMP or amendments to the Department of Ecology
for review and official action pursuant to the SMA. '
Backshore means a berm, together with associated marshes or
meadows, on marine shores landward of the ordinary high water mark
which is normal above high tide level and has been gradually built up by
accretion.
Bank means a steep rise or slope at the edge of a body of water or
water course.
Beach nourishment means the artificial replenishing of a beach by
delivery of materials dredged or excavated elsewhere.
Berm means a ledge or shoulder consisting of mounded earth or rock.
Breakwater means an off-shore structure, either floating or not, which
mayor may not be connected to the shore, such structure being designed
to absorb and/or reflect back into the water body the energy of the waves.
Bulkhead means a wall, seawall, embankment or other structure
erected parallel to the shoreline that retains or prevents sliding or erosion
of land or protects land from wave action.
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City of Federal Way SMP - Article III. Shoreline Management -Draft Regulations
Bluff means a steep slope which abuts and rises from Puget Sound.
Bluffs contain slopes predominantly in excess of 40 percent, although
portions may be less than 40 percent. The toe of the bluff is the beach of
Puget Sound. The top of a bluff is typically a distinct line where the slope
abruptlY.levels out. Where there is no distinct break in slope, the slope is
either the line of vegetation separating the unvegetated slope from the
vegetated uplands plateau or, when the bluff is vegetated, the point where
the bluff slope diminishes to less than 15 percent.
Conditional use means a use, development, or substantial
development which is classified as a shoreline conditional use or is not
classified within the SMP.
Critical saltwater and freshwater habitats (critical salmonid habitats)
mean habitats that are used by Pacific salmonid species that migrate
between fresh water and salt water during their life cycle. These habitats
include:
1. Gravel bottomed streams used for spawning;
2. Streams, lakes, and wetlands used for re' feeding, and cover
and refuge from predators and high waters'
3. Streams and salt water ,bodies tion corridors;
4. Shallow areas of salt W8 . for aring, feeding, as well
as cover and refuge from pred' ts, including, but not limited
to, forage fish habitats such a ches and eelgrass beds; and
5. Pocket estuaries includ ams mouths and deltas where
freshwater mixes with salt water and provides rearing habitat for
juvenile salmonids.
Dredging means the removal of earth from the bottom of a stream, bay
or other water body for the purposes of deepening and/or maintaining a
navigational channel.
Drift cell (Also referred to as "drift sector," or "littoral cell") means a
particular reach of marine shore in which littoral drift' may occur without
significant interruption and which contains any natural sources of such drift
and also accretion shore forms created by such drift.
Ecological functions means the work performed or role played by the
physical, chemical, and biological processes in the shoreline that
contribute to the maintenance of the aquatic and terrestrial environments
that constitute the shoreline's natural ecosystem.
Ecosystem-wide processes means the suite of naturally occurring
physical and geologic processes of erosion, transport, and deposition; and
specific chemical processes that shape landforms within a specific
shoreline ecosystem and determine both the types of habitat and the
associated ecological functions.
Shoreline environment designation means the categories of shorelines
of the state established by the city of Federal Way shoreline management
master program to differentiate between areas whose features imply
differing objectives regarding their use and future development.
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Exemptions means those, development activities set forth in Chapter
XX of the Federal Way SMP which are not required to obtain a Substantial
Development Permit but which must obtain an authorized statement of
exemption and which mus otherwise comply with applicable provisions of
the Act and the City's SMP.
Fill means the addition of soil, sand, rock, gravel, sediment, earth
retaining structure, or other material to an area waterward of the OHWM,
in wetlands, or on shorelands in a manner that raises the el~vation or
creates dry land.
Float means a structure or device which is not a breakwater and which
is moored, anchored, or otherwise secured in the waters of Federal Way,
and which is not connected to the shoreline.
Grading means the movement or redistribution of the soil, sand, rock,
gravel, sediment, or other material on a site in a manner that alters the
natural contour of the land.
Groin means a barrier type structure extending from the backshore into
the water across the beach. The purpose of a groin is to interrupt
sediment movement along the shore. .
Jetty means a,n artificial barri.e.,..,r" u.s....e..d to cp.a....,.,....n,. '~".',.,"..>'.,.; natural littoral drift
to protect inlet entrances from 'clogging b~ I ~sediment.
Landslide means an episodic dow I f, '. e.; ent of a mass of soil or
rock that includes but is not Iim;~.. ~,:, I, sill" ps, mudflows, and
earthflows. " .' , "'..
Littoral drift means the nat .If, ~e ent of sediment along marine or
lake shorelines by waveaction \0" ei/,onse to prevailing winds.
Marine means pertaining to tidally influenced waters, including Puget
Sound and the bays, estuaries and inlets associated therewith.
Nearshore means either nearshore environment or nearshore habitat
and refer generally to an a'rea along the Puget Sound shoreline that
extends from the top of bluffs or upland area immediately adjacent to the
beach to the point where sunlight penetrates marine waters to a depth
where aquatic plant life is supported.
Nonconforming use or development means a shoreline use or
development which.was lawfully constructed or established prior to the
effective date of the Act or the applicable SMP, or amendments thereto,
but which does not conform to present regulations or standards of the
SMP. "
Non-water-oriented uses means those uses which have little or no
relationship to the shoreline and are not considered priority uses under the
. SMA. Examples include professional offices, automobile sales or repair
shops, mini-storage facilities, multifamily residential development,
department stores, and gas stations.
Ordinary High Water Mark (OHWM) means the mark on all tidal waters
and streams that will be found by examining the beds and banks and
ascertaining where the presence and action of waters are so common and
usual and so long continued in all ordinary years as to mark upon the soil
a character distinct from that of the abutting upland, in respect to
vegetation, as that condition existed on June 1, 1971, as it may naturally
Page 4 of 29
City of Federal Way SMP," Article III. Shoreline Management - Draft Regulations
change thereafter, oras it may change thereafter in accordance with
permits issued by a local government or the Department of Ecology. In
any area where the ordinary high water mark cannot be found, the
ordinary high water mark adjoining saltwater shall be the Iineof mean.
higher high tide.
Public Access means the public's ability to get to and use the State's
public waters, the water/land interface and associated public shoreline
area.
Restoration means in the context of "ecological restoration," the
reestablishment or upgrading of impaired ecological shoreline processes
or functions. This may be accomplished through measures including, but
not limited to, revegetation, removal of intrusive shoreline structures and
removal or treatment of toxic materials. Restoration does not imply a
requirement for returning the shoreline area to aboriginal or pre-European
settlement conditions:
Riprap means a layer, facing or protective mound of angular stones
randomly placed to prevent erosion, scour or sloughing of a structure or
. embankment; also, the stone so used.
Shore/an ds, also referred to as "shorel,a,.""n d...~,."a.,~ i.f.'..,...".,.....',.,..... means those lands
. extending landward for two hundred feet i a 1~tff! ions as measured on
a horizontal plane from the ordinary ..,.. ",'. t..~,' ; floodways and
contiguous floodplain areas Ian .. b:~re eet from such .
floodways; and all wetlands a ' . 'ssociated with the streams,
lakes, and tidal waters which, j , 0 the provisions of this chapter;
the same to be designated as. ation by the Department of Ecology.
Shoreline administrator means the administrator shall be the Planning
Director or his or her designee and is responsible for administering the
Federal Way SMP.
Shoreline jurisdiction means all "shorelines of the state" and
"shorelands" as defined in the Federal Way SMP and RCW 90.58.030.
, Shoreline Master Program (SMP) means the comprehensive use plan
for a described area, and the use regulations together with maps,
diagrams, charts, or other descriptive material and text, a statement of
desired goals, and standards developed in accordance with the policies
enunciated in RCW 90.58.020.
Shoreline modifications means those actions that modify the physical
configuration or qualities of the shoreline area, usually through the
construction of a physical element such as a dike, breakwater, pier, weir,
dredged basin, fill, bulkhead, or other shoreline structure. They can
include other actions, such as clearing and grading.
Shoreline stabilization means actions taken to address erosion
impacts to property, dwellings, businesses, or structures caused by
natural shoreline processes such as currents, floods, tides, wind or wave
action.
Shorelines means all of the water areas of the state, including
reservoirs, and their associated shorelahds, together with the lands
underlying them; except (i) shorelines of statewide significance; (ii)
shorelines on segments of streams upstream of a point where the mean
annual flow is twenty cubic feet per second or less and the wetlands
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
associated with such upstream segments; and (iii) shorelines on lakes
less than twenty acres in size and wetlands associated with such small
lakes.
Shorelines of Statewide Significance means those areas of Puget
Sound in the City of Federal Way lying seaward from the line of extreme
low tide. .
Shorelines of the state means the total of all "shorelines" and
"shorelines of statewide significance" within the City of Federal Way.
, Soft-shore bank stabilization means the use of bioengineering or
biotechnical bank stabilization measures where vegetation, logs, rock and
beach nourishment are used to address erosion control and slope stability.
SMP means the Shoreline Master Program.
SMA means the Shoreline Management Act.
Stringline setback means a straight line drawn between the points on
the primary buildings having the greatest projection waterward on the two
adjacent properties. If one of the adjacent properties is unimproved the,
line shall be drawn to the point of the standard shoreline setback at the
side property line of the unimproved lot. .
Water-dependent means a use or portion e which cannot exist
in any other location and is depende t by reason of the
intrinsic nature of its operation~ dependent uses may
include ship cargo terminal 101' rru ~ and passenger terminals,
barge loading facilities, ship b I d~ dry docking, marinas,
aquaculture, float plane faciliti s sewer outfalls.
Water-enjoyment, means a recreational use, or other use facilitating
public access to the shoreline as a primary characteristic of the use; or a
use that provides for recreational use or aesthetic enjoyment of the
shoreline for a substantial number of people as a general characteristic of
the use and which through the location, design and operation assures the
public's ability to enjoy the physical and aesthetic qualities of the
shoreline. In order to qualify as a water-enjoyment use, the use must be
open to the general public and the shoreline oriented space within the
. project must be devoted to the specific aspects of the use that fosters
shoreline enjoyment. Primary water-enjoyment uses may include, but are
not limited to, parks, piers and other improvements facilitating public
access to shorelines of the state; and general water-enjoyment uses may
include, but are not limited to, restaurants, museums, aquariums,
scientific/ecological reserves, resorts and mixed-use commercial;
provided, that such uses conform to the above water-enjoyment
specifications and the provisions of the master program.
Water-oriented means any combination of water-dependent, water-
related, and/or water-enjoyment uses and serves as an all-encompassing
definition for priority uses under the SMA.
Water-related means a use or portion of a use' which is not intrinsically
dependent on a waterfront location but whose economic vitality is
dependent upon a waterfront location because: , .
(1) Of a functional requirement for a waterfront location such as the
arrival or shipment of materials by water or the need for large quantities of
water; or
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(2) The use provides a necessary service ,supportive of the water-
dependent commercial ' activities and the proximity of the use to its
customers makes its services less expensive and/or more convenient.
Examples include professional services serving primarily water-dependent
activities and storage of water-transported foods. (Ord. No. 98-323, 9 3,
12-1-98; Ord. No. 99-355, 93,11-16-99)
@
f1
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City of Federal Way SMP - Article III. Shoreline Managemc<nt - Draft Regulations
Division 2. Shoreline Regulation
18-164 General development standards.
The following general development standards apply to allu'ses and
activites in all shoreline environments: .
(a) Impact mitigation.
(1) To the extent Washington's State Environmental Policy Act of 1971 (SEPA),
chapter 43.21 C RCW, is applicable, the analysis of environmental impacts from
proposed shoreline uses or developments shall be conducted consistent with the
rules implementing SEPA (FWCC XX and WAC 197-11). Mitigation for adverse
impacts to shoreline functions will be triggered during the SEPA review or
shoreline land use permit process.
(2) Where required, mitigation measures shall be applied in the following
sequence of steps listed in order of priority.
a. Av~iding the impact altogether by not ~", , certain action or parts of an
action; ,
b. Minimizing impacts by Iii ifn ' e 0 agnitude of the action and
its implementation by u ' Ii' ti}l technology or by taking affirmative
steps to avoid or reduc '-
c. Rectifying the impact b.,..' pairing, rehabilitating, or restoring the affected
environment;
d. Reducing or eliminating the impact over time by preservation and
maintenance operations;
e. Compensating for the impact by replacing, enhancing, or providing
substitute resources or environments; and
f. Monitoring the impact and the compensation projects and taking
appropriate corrective measures.
(3) In determining appropriate mitigation measures applicable to shoreline
development, lower priority measures shall be applied only where higher priority
measures are determined to be infeasible or inapplicable.
(4) Required mitigation shall not be in excess of that necessary to assure that
proposed uses or development will result in no net loss of shoreline ecological
functions.
(5) Mitigation actions shall not have a significant adverse impact on other
shoreline functions fostered by the policy of the Shoreline Management Act.
(6) When compensatory measures are appropriate pursuant to the mitigation
priority sequence above. preferential consideration shall be given to measures
that replace the impacted functions directly and are located in the immediate
vicinity of the impact. However, alternative compensatory mitigation may be '
authorized if said mitigation occurs within the watershed and addresses limiting
factors or identified critical needs for shoreline conservation based on watershed
or comprehensive management plans. Authorization of compensatory mitigation
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
measures may require appropriate safeguards, terms or conditions as necessary
to ensure no net loss of ecological functions.
(b) Vegetation conservation. Existing native shoreline vegetation
shall be preserved to the maximum extent feasible within the shoreline
setback consistent with safe construction practices, and other provisions
of this chapter. Specifically'native trees and shrubs shall be preserved to
provide habitat, shade and slope stabilization functions to maintain
ecological processes in the City's shoreline.
(c) Water quality I stormwater. All activities and development within
the shoreline jurisdiction shall be in compliance with the requirements and
restrictions of FWCC Chapter 21: Surface and Stormwater Management.
(d) Critical areas. Activities and development in critical areas found
within shoreline jurisdiction are required to comply with the following
development standards. ~
(1) Geologic Hazard Areas. RegUlated~"C~I.l ,aOi'lgiically hazardous areas (as
defined in FWCC Ch.apter 22) locate., .".n 1.)~r,~ e jurisdi~tion include seismic'
hazard areas, landslide hazard, op .' and erosion hazard areas. If
a geologic hazardous area is I ~,: ,..."~ i '. shoreline jurisdiction, all activities
on the, site shall be in com ,f'l \'l the requirements and restrictions of
FWCC Chapter 22, Article XIV ISlon 4: Critical Areas.
(2) Streams and Wetland. If a stream or wetland (as defined in FWCC
Chapter 22) is located within the shoreline jurisdiction, all activities within the
shoreline jurisdiction shall be in compliance with the requirements and
restrictions of FWCC Chapter 22, Article XIV, Divisions 5 & 6: Critical Areas.,
(3) Flood Hazard Reduction. If an area of special flood hazard is located on
or adjacent to a development site within shoreline jurisdiction, all activities on the
site shall be in compliance with the requirements and restriction of FWMC
Chapter 18, Article II, Division 6: Critical Areas.
(e) Critical salmonid habitats. Activities and development in critical
salmonid habitats found within the shoreline jurisdiction are required to comply
with the following additional development standards:
(1) Structures which prevent the migration of salmon and steelhead are
prohibited in the portions of the water bodies used by fish. Fish bypass facilities
shall allow the upstream migration of adult fish. Fish bypass facilities shall
prevent fry and juveniles migrating downstream from being trapped or harmed. '
(2) Fills shall not intrude into critical salmonid habitats, except as provided
in subsection (d)(3)of this section.
(3)Fills may intrude into critical salmonid habitats only where the
proponent obtains a conditional use permit (CUP) and demonstrates all of the
following conditions are met:
a. An alternative alignment or location is not feasible;
Page 90f 29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
b. The project is designed to minimize its impacts on the environment;
c. The project is in the public interest; and
d. If the project will create significant unavoidable adverse impacts, the
impacts are mitigated by creating in-kind replacement habitat near the project.
Where in-kind replacement mitigation is not feasible, rehabilitating degraded
habitat may be required as a substitute.
(4) Bulkheads, breakwaters, jetties, groins and other shoreline protection
structures may intrude into critical salmoriid habitats only where the proponent
demonstrates all of the following conditions are met:
a. An alternative alignment or location is not feasible;
b. The project is designed to minimize its impacts on the environment;
. c. The project is in the public interest; and
d. I,f the project will create unavoidable adverse impacts, the impacts are
mitigated by creating in-kind replacement habitat near the project. Where in-kind
replacement mitigation is not feasible, rehabilitating degraded habitat may be
, required as a substitute. .
(5) Pilings and floatsmay be located in water areas used by salmon and
steelhead for migration corridors, rearing, fe' and refuge, provided the
facilities use open piling construction and i j.'..'..... are avoided to the maximum
extent possible. Approach. fills shal ".. ndward of the ordinary high
,water mark. (6) Open pile bri f'ed water crossing structures
over critical salmonid' habitat not feasible, one of the following
water crossing structures m oved if the impacts can be mitigated:
temporary culverts, bottomle chculverts, elliptical culverts or other fish-
passable round culverts. These structures are listed in priority order, with the first
having the highest. preference and the last the lowest preference. In order for a
lower priority structure to be permitted, the applicant must show the higher
priority structures are not feasible. The,project shall be designed to minimize its
impacts on the environment.
(7) Bridges and in-water utility corridors may be located in critical habitats
provided the proponent shows that all of the following conditions are met:
a. An alternative alignment is not feasible;
b. The project is located and designed to minimize its impacts on the
environment;
c. Any alternative impacts are mitigated; and
d. Any landfill is located landward of the ordinary high water mark.
Open piling and piers required to construct the bridge may be placed
waterward of the ordinary high water mark, if no alternative method is feasible.
When installing in-water utilities, the installer may place native material on
the bed and banks of the water body or wetland to re-establish the
preconstruction elevation and contour of the bed. The project shall be designed
to avoid and minimize its impacts on the environment.
(8) Dredging which will damage shallow water habitat used by salmon and
, steelhead for migration corridors, rearing, feeding and refuge shall not be allowed
unless the proponent demonstrates all of the following conditions are met:
a. The dredging is for a water-dependent or water-related use;
b. An alternative alignment or location is not feasible;
3. The project is designed to minimize its impacts on the environment;
d. The project is in the public interest; and
Page 10 of29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
e.lf the project will create significant unavoidable adverse impacts, the
impacts are mitigated by creating in-kind replacement habitat near the project.
Where in-kind replacement mitigation is not feasible, rehabilitating degraded
habitat may be required as a substitute.
(9) In-water dredge spoil disposal sites shall not be located in critical.
salmonid habitats.
(10) Filling, dredging, channelization and other activities which negatively
impact habitat values are prohibited in wetlands, ponds, and side channels which
are associated with critical salmonid habitats.
(11) Within critical habitats, permanent channel changes and realignments
are prohibited.
(12) The removal of aquatic and riparian vegetation within or adjacent to
critical salmonid habitats shall be minimized. Trees which shade side channels,
streams, estuaries, ponds and wetlands associated with critical salmonid habitats
shall be maintained. Areas of disturbed earth shall be revegetated.
(13) Unless removal is needed to prevent hazards to life and property or to
enhance critical salmonid habitats, large woody debris below the ordinary high.
water mark shall be left in the waterway to provide salmon and steel head
habitat.(Ord. No. 98-323,93,12-1-98; O'd: ~5' 93,11-16-99)
18.165 [NEW SECTION] Sho J ~~ a Ions
(a) Shoreline stabilizatio 'l~tabilization may be permitted
in the shoreline residential an n conservancy environments,
provided:
(1) Shoreline stabilization, including bulkheads shall not be considered
an outright permitted use on the city's shorelines. In order for shoreline
. stabilization to be permitted the City must find that:
a. Erosion from waves or currents presents a clear and imminent
threat to a legally established primary structure, one or more substantial
accessory structures, or public improvements. The applicant shall provide
a geotechnical report, prepared by a qualified professional, that estimates
the rate of erosion and evaluates alternative solutions;
b. Nonstructural alternatives such as slope drainage systems,
vegetative growth stabilization, gravel berms, and beach nourishment
shall be prioritized over structural options such as bulkheads and riprap.
The "softest" effective alternative shall be utilized; and;
c. The proposed shoreline stabilization is located landward of the
ordinary high water mark; and
d. The proposed shoreline protection is the minimum size
necessary to protect existing improvements; and
e. The applicant shall demonstrate that impacts to sediment
transport are minimized to the greatest extent possible; and
. f. Shoreline stabilization shall not have an adverse impact on the
property of others and shall be designed so as not to create the need for
shoreline protection elsewhere; and
g. Shoreline stabilization shall not significantly interfere with normal
surface and/or subsurface drainage into the water body and shall be
constructed using an approved filter cloth or other suitable means to allow
Page 11 of 29
City of Federal Way SMP -:- Article III. Shoreline Management - Draft Regulations
passage of surface and groundwater without internal erosion of fine
material; and
h. Shoreline stabilization shall not be used to create new lands.
(2) When a bulkhead is permitted subject to subsection (1), above, the
following standards shall apply:
a. The maximum height of the proposed bulkhead is no more than
one foot above the elevation of extreme high water on tidal waters, or one
foot in height above the elevation of ordinary high water mark on lakes,
measured from grade on the waterward side of the bulkhead; and
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City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
b. A dock may be allowed when the applicant has demonstrated a need
for moorage and has demonstrated that the following alternatives have been
investigated and are not available or feasible:
1. Floating moorage buoys.
2. Joint use moorage dock.
No more than one dock for each residence is permitted. On lots with less
than 50 feet of waterfront, only joint use dock shall be perm.tted except when
abutting owners are not agreeable or when both lots abutting the subject lot have .
legally established piers then the lot with less than 50 feet of waterfront may be
permitted an individual pier.
c. New multiple-family developments subdivisions or short subdivisions
shall be permitted one shared dock.
1. The total number of moorage spaces shall be limited to one moorage
space for every two dwelling units in the multifamily development, subdivision, or
short subdivision.
d. Dock dimensions.
1. The maximum waterward intrusion of any portion of any dock shall be
36 feet, or the point where the water depth is 13 feet beloW the ordinary high
water mark, whichever is reached first.
2. The maximum width of each d c
wide on joint use docks where additi I
3. The total surface
facilities, or any combination
shall not exceed 400 square f < ," ,
e. Moorage piles. Moo~iles not constructed in conjunction with a pier
are limited by the following conditions:
1. All piles shall be placed so as to not constitute a hazard to navigation.
2. No pile shall be placed more than 80 feet waterward of the ordinary
'high water mark.
3. All moorage piles shall be placed in a, water depth not to exceed 13
feet below the ordinary high water mark.
., 4. No more than two moorage piles per residence are permitted.
be six feet, or up to eight feet
o s provided.
00 ges, floats, and/or launching
ted with a single-family residence
f. Floats are limited under the following conditions:
1. One float per single-family residence, multifamily development, short
subdivision, or subdivision is permitted. ..
2. No portion of a float shall be placed more than 36 feet waterward of
the ordinary high water mark.
3. Retrieval lines shall not float at or near the surface of the water.
4. No float shall have more than 100 square feet of surface area.
. (c) Launching Ramps and Lift Stations. Launching ramps and lift
stations require a shoreline conditional use permit and are limited by the
following conditions:
(1) No portion of a launching ramp or lift station shall be placed more than 60
feet waterward of the ordinary high water mark.
(2) All portions of a launching ramp or lift station shall be placed at a depth
not to exceed eight feet below the ordinary high water mark.
Page 13 of29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(3) Launching rails or ramps shall be anchored to the ground through the use
of tie-type construction. Asphalt, concrete, or other ramps which solidly cover the
water body bottom are prohibited.
(4) No more than one launching rail per single-family residence is permitted,
and rio more than one common use launching ramp for each new multifamily
development, short subdivision, or subdivision is permitted.
(d) Breakwaters and Jetties. Breakwaters and jetties are not
permitted within any shoreline of the City.
(e) Dredging and Filling.
(1) Dredging:
a. Dredging activities in shoreline residential or urban conservancy
environments require a Conditi'onal Use Permit and must comply with all federal
and state regulations. Dredging is not permitted in the Natural environment.
. b. Dredging activities are allowed in the shoreline residential and urban
conse, rvancy shor~line envir~nmen~s. ?nlY, wh l' "!}' ecessary to protect public
safety or for shoreline restoration activities ';
. .
. . ,.,'., .
. . '.
c. Dredging and exca :j.,' , I salmonid habitats is prohibited,
except when required for shor . ation activities.
d. Where allowed, dre I'" operations must be scheduled so as to not
damage shoreline ecological f~nctions or processes.
e. When dredge spoils have suitable' organic and physical properties,
dredging operators shall recycle dredged material into areas of the City suitable
for those materials. "
f. Unavoidable impacts of dredging shall be mitigated as required by this
chapter.
(2) Filling:
. a. Fill activities shall only be allowed in association with allowed
(permitted) water dependent use developments. Fill associated with non-water
dependent u~es shall be prohibited.
b. Fill needed to support the following water dependent uses may be
allowed in all shoreline environments through a Shoreline Conditional Use
Permit:
1 Public access;
2 Expansion, alteration, or repair of transportation facilities currently
located with in the shoreline;
3 Mitigation actions;
4 Environmental, ecological, or watershed restoration projects;
5 Beach nourishment or enhancement projects; and
6 Soft shore bank stabilization projects.
d. Permitted fill activities must comply with the following standards:
1. Demonstration that alternatives to fill are not feasible; ,
Page 14 of29
City of Federal Way SMP - Article III. Shoreline Management - Drafi Regulations
2. Demonstration that fill shall be deposited so as to minimize disruption
of normal surface and ground water passage;
3. Demonstration that fill materials shall be of s.uch quality that it will not
adversely affect water quality;
4. Demonstration that fill shall allow surface water penetration into the
ground water supply, where such conditions existed prior to the fill; and
5. Demonstration that landfill timing will minimize damage to water
quality and aquatic life.
e. Fill, except for beach nourishment, shall be prohibited in areas of high
shoreline erosion potential. '
f. Fill located waterward of the ordinary high water mark that results in a
net loss of shoreline function is prohibited.
g. Fill within the one hundred-year (tOO-year) flood plain requires
demonstration that fill will not reduce the flood plain water storage capacity or in
any way increase flood hazard so as to endanger public safety.
18-166 Environmental designations.
(a) Purpose and establishment of deSig~a i,~. '
(1) The purpose of the designations is tG,....",', ",'" ~,J3,r, ,.,en ntiate between areas whose
geographical, hydrological, topogra i i,; ;ther features imply differing
objectives regarding the use an u ,pm .', t of the shorelines of the city.
Each environment designa ", particular emphasis in the type of "
uses and the extent of t that should occur within it.' The
environmental designation s is designed to encourage uses in each
environment that enhance or' are compatible with the character of the
"environment, while at the' same time requiring reasonable standards and
restrictions on development so that the character of the environment is not
adversely impacted.
(2) Names of environment designations. In order to accomplish the purpose
of this title, environmental designations have been established as follows:
a. Shoreline Residential.
b. Urban Conservancy.
c. Natural.
(3) Limits of environment designations. Each environment designation shall
consist of: '
a. The entire water body from its centerline or point, including all water
below the surface, the land below the water body, the space above the water
body, and the shorelands associated with the water body.
b. The shoreline areas within 200 feet of the OHWM, and additional
upland areas where associated wetlands and floodplains extend beyond 200 feet
from the OHWM.
(4) Establishment of designations.
a. The written descriptions of the boundaries of the shoreline environment
designations as adopted by ordinance shall constitute the official legal
descriptions of the boundaries of those environment designations.
b. The official maps prepared by the city pursuant to Chapter 173-26 WAC
shall constitute the official descriptions of the limits of all shorelands in the city of
Federal Way as defined by RCW 90.58.030 and FWCC 18-163.
Page 15 of29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
c. The department may, from time to time as new or improved information
becomes available, modify the official maps described in subsection (a)(4 )b. of
this section consistent with state guidelines to more accurately represent, clarify,
or interpret the true limits of the shorelines defined herein.
(5) Location of boundaries.
a. Boundaries indicated as following streets, highways, roads, and bridges
shall be deemed to follow the centerline of such facilities unless otherwise
specified.
b. Boundaries indicated as following railroad lines and transmission lines
shall' be deemed to follow the centerline of such rights-of-way or easements
unless otherwise specified.
c. Where different environmental designations have been given to a
tributary and the main stream at the point of confluence, the environmental
designation given to the mainstream shall extend for a distance of 200 feet up
the tributary.
d. In case of uncertainty as to.a wetland or environment boundary, the
director of community development services shall determine its exact location
pursuant to the criteria of WAC 173-22-040, and RCW 90.58.030, and the
provisions of this chapter. (Ord. No. 98-323, S 1-98; Ord. No. 99-355, S 3,
11-16-99) ,
..~
Page 16 of29
City of Federal Way SMP - Article IlL Shoreline Management - Draft Regulations
18-167 NEW SECTION Permitted Use Table
Sh.or:eline Modification
Shoreline Stabilization I
Protection 1
Piers, Docks, Moorage, and
Floats2. 3 .
LaLinching Ramp I Lift Station
Breakwaters and Jetties
Dredging and Filling
Shoreline Use
Office and Commercial
Development
Recreational Development
Residential Development
Accessory Structures
Utilities5
Transportation I Parking' .
Facilities6
Aquaculture
Community Boating Facilities7
P = Allowed as exempt from permitting or permitted with Substantial Development Permit
C = May be allowed with Shoreline Conditional Use Permit
X = Prohibited
1. Includes bulkheads, bio-engineered erosion control projects, groins and other shoreline
stabilization activities. Groins may only be permitted as part of a public beach management
program.
2. Code provisions address these modifications as accessory to residential uses.
3. Residential piers and docks are prohibited on Puget Sound shorelines.
4. Would be permitted with Substantial Development Permit in parks and public access areas;
would be permitted with Shoreline Conditional Use permit elsewhere in Urban Conservancy
Environment.
5. Solid waste transfer stations are not allowed
6. Parking as a primary use is prohibited in all environments, but allowed if serving an allowed
shoreline use
7. Allowed in association with recreational development
Page 170[29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
18-168 Shoreline Residential.
(a) Purpose. The purpose of the "shoreline residential" environment is to
accommodate residential development and appurtenant structures that are
consistent with this chapter. An additional purpose is to provide appropriate public
access and recreational uses. .
(b) Designation criteria. Designation criteria for the shoreline residential
environment are provided in the City's shoreline master program, FWCC Chapter
xx.
(c)General requirements.
(1) Development waterward of the ordinary high. water mark is prohibited
except water dependent recreational uses and public utilities.
(2) No structure shall exceed a height of 35 feet above average grade level.
This requirement may be modified if the view of any neighboring residences will
not be obstructed, if permitted outright by the applicable provisions of the
underlying zoning, and if the proposed development is water-related or water-
dependent.
(3~ All dev~lopment shall be re.quired .to Rr~~~e ade~uate surface wa.ter
ret~n, tlon, erosion control, and. sedlmentat If),,'[' IlItles dUring the construction
~rI~. .
(4) Setbacks. Development e '. st 50 feet of property landward,
from the ordinary high water ' :ed minimum setback and vegetation
conservation area, subject to eferenced in subsection (e). .
(5). Vegetation Conservati , a. Within the Vegetation Conservation Area, no more
than 50 percent of the area wit'tl native shoreline vegetation shall be cleared, and a
minimum of 60 percent of existing native trees shall be, retained. At least 80 percent of
native trees in the Vegetation Conservation Area over 20 inches in diameter at breast
height shall be retained. Trees determined by the city to be hazardous or diseased may
be removed. Additionally, the Director may allow removal of vegetation exceeding that
described above where an applicant agrees to replacement plantings that are
demonstrated to provide greater benefit to shoreline ecological processes than would be
provided by strict application of this section.
(6) In addition to any requirements imposed by Chapter 21 FWCC, collection
facilities to control and separate contaminants shall be required where stormwater
runoff from impervious surfaces would degrade or add to the pollution of recipient
waters of adjacent properties.
(7) All development in the Shoreline Residential area must comply with
applicable regulations identified within the [General Development Standards],
[Shoreline Modifications], and all other applicable sections of this chapter.
(d) Shoreline Modifications
(1) Allowed modifications to the, shoreline within Shoreline Residential designated
areas include the following: .
a. Shoreline Stabilization. Allowed within Shoreline Residential designated areas
under the requirements imposed by [NEW SECTION Shoreline Modifications] division (a).
Page 18 of29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
b. Piers, Docks, Moorage, and Floats. Allowed within Shoreline Residential
designated areas under the requirements imposed by [NEW SECTION Shoreline
Modifications] division (b).
c. Launching Ramp / Lift Station. Allowed within Shoreline Residential designated
areas with a Shoreline Conditional Use Permit under the requirements imposed by [NEW
SECTION Shoreline Modifications] division (c).
d. Dredging and Filling. Allowed within Shoreline Residential designated areas with
a Shoreline Conditional Use Permit under the requirements imposed by [NEW SECTION
Shoreline Modifications] division (e).
(2) Prohibited modifications to the shoreline within Shoreline Residential designated
areas include the following:
a. Breakwaters and Jetties.
(e) Shoreline Uses.
(1) Allowed uses within Shoreline Residential designated areas include the following:
a. Residential Development. Single-family and multiple-family residential
development may be permitted in the Shoreline Residential environment subject to the
general requirements of Chapter 22 FWCC, 'I Ie XI, Divisions 3 and 4, and the
following: ,
1. Single-family or multiple- d tial development is permitted in the
underlying zone classification.
". ' 2. Residential ,devel ited waterward of the ordinary high water
mark.
3. Setbacks.
i. Single-family residential development shall maintain a minimum shoreline
setback of 50 feet from the Ordinary High Water Mark (OHWM) as a vegetation
conservation area, except in the following case:
aa. If single-family residential development is proposed on a lot where
properties on at least one side of the lot are developed in single-family residences located
less than 50 feet from the OHWM, then the proposed residential development may be
located the same distance from the OHWM as the adjacent residences (using stringline
method) but shall in no case be closer than 30 feet from the OHWM.
ii. Multifamily residential development shall maintain a minimum setback of
75 feet from the OHWM as a vegetation conservation area, except in the following case:
aa If multi-family residential development is proposed on a lot where
properties at least one side of the lot are developed in multi-family residential use located
less than 75 feet from the OHWM, then the proposed residential development may be
located the same distance from the OHWM as the adjacent residential uses (using
stringline method) but shall be no closer than 50 feet from the OHWM.
b. Accessory Structures. Rresidential accessory structures may be placed within
the required shoreline setback, provided:
1. No more than one accessory structure shall cover more than 150 square feet,
or to a maximum of 300 square feet of accessory structure area.
2. No accessory structure shall exceed eight feet in height.
3. Existing native shoreline vegetation within the shoreline setback is conserved
to the maximum extent possible as per general requirements (c)(4).
Page 19 of29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
c. Recreational Development. Recreational development may be permitted in the
Shoreline Residential environment subject to the general requirements of this chapter,
provided:
1. Th~ recreational development is permitted in the. underlying zone.
2. Swimming areas shall be separated from boat launch areas.
3. The construction of swimming facilities, piers, moorages, floats, and launching
facilities below the ordinary high water mark shall be governed by the general
requirements of this chapter.l.
5. Public boat launching facilities may be developed, provided:
i. The parking and traffic generated by such a facility can be safely and
conveniently handled by the' streets and areas serving the proposed facility.
ii. The facility will not be located on a beach area or cause net loss in
shoreline function.
6. Upland facilities constructed hl conjunction with a recreational development
shall be set back and/or sited to avoid adverse impacts to the functions of the shorelines
of the city.
7. Public pedestrian and bicycle pathways shall be permitted adjacent to water
bodies. Such trails and pathways must be mad · ervious materials, if feasible.
. 8. Public contact with unique a areas shall be permitted where it is
possible without destroying the natur c,FI' a he area.
9. Water viewing, natu:E, . in , and viewing shall be accommodated.
by space, platforms, benches, te'nt with public safety and security.
d. Community Boati, V cilities. Allowed in association with recreational.
development, as regulated under the requirements imposed by (e) Shoreline Uses,
subsection 1.
e. Utilities. Utility facilities may be permitted in the Shoreline Residential
environment subject to the requirements of this chapter, provided:
1. No other practicable alternative with less impact to the environment is
available for the facility.
2. Utility and transmission facilities shall:
i. Avoid disturbance of unique and fragile areas.
ii. Avoid disturbance of wildlife spawning, nesting, and rearing areas.
iii. Conserve native shoreline vegetation, particularly forested areas, to the
maximum extent possible.
iv. Overhead utility facilities shall not be permitted in public parks,
monuments, scenic, recreation, or historic areas.
3. Utility distribution and transmission facilities shall be designed so as to:
i. Minimize visual impact.
ii. Harmonize with or enhance the surroundings.
iii. Not create a need for shoreline protection.
iv. Conserve native shoreline vegetation, particularly forested areas, to the
maximum extent possible.
v. Utilize to the greatest extent possible natural screening.
4. The construction and maintenance of utility facilities shall be done in such a
way so as to:
i. Maximize the preservation of natural beauty and the conservation of
resources.
, Page 20 of29
City of Federal Way SMP ~ Article III. Shoreline Management - Draft Regulations'
ii. Minimize scarring of the landscape.
iii. Minimize siltation and erosion.
iv. Protect trees, shrubs, grasses, natural. features, and topsoil from
drainage.
v. Avoid disruption of critical aquatic and wildlife stages.
5. Rehabilitation of areas disturbed by the construction and/or maintenance of
utility facilities shall:
i. Be accomplished as rapidly as possible to minimize soil erosion and to
maintain plant and wildlife habitats. .
ii. Utilize native trees and shrubs.
6. Solid waste transfer stations shall not be permitted within the shorelines of the
state.
f. Parking facilities.. Parking, except parking facilities associated with detached.
single-family development, shall conform to the following minimum requirements:
1. Parking facilities serVing individual buildings on the shoreline shall be located
landward from the principal building being served, except when the parking facility is
within or beneath the structure and adequately screened, or in cases when an alternate'
location would have less environmental impact ~i; shoreline.
2. Any new development 0 x,~ ~existing development creating greater
than 6 total parking stalls mus,', er ' ality standards required by the King
County Surface Water Manua ,0',',.. I ites and "resource stream protection" (See
Sections 1.3.4 Special requiJl'll control, 6.1.5 High use menu, 'and Resource
stream protection of King Cou ..~ urface Water Design Manual).
3. Outdoor parking, areas shall provide landscaping pursuant to FWCC
Chapter 22.
4. Parking as a primary use in shoreline jurisdiction shall be prohibited.
5. Parking in the shoreline jurisdiction shall directly serve a permitted shoreline
use.
(2) Prohibited uses to the shoreline within Shoreline Residential designated areas
include:
a. Office and Commercial Development.
b. Aquaculture.
Page 21 of29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
18-169 Urban Conservancy environment.
(a) Purpose. The purpose of the "urban conservancy" environment is to protect
and restore ecological functions of open space, flood plain and other sensitive
lands where they exist in urban and developed settings, while allowing a variety of
compatible uses. '
(b) Designation criteria. Designation criteria for the Urban Conservancy
environment are provided in the City's shoreline master program, FWCC Chapter
xx (c) General requirements.
(1) Development waterward of the ordinary high water mark is prohibited
except water dependent recreational uses and public utilities. .
(2) No structure shall exceed a height of 35 feet above average grade level.
This requirement may be modified if the view of any neighboring residences will
not be obstructed, if permitted outright by the applicable provisions of the
underlying zoning, and if the proposed development is water-related or water-
dependent. '
(3) All development shall be required to provide adequate surface water
retention and sedimentation facilities during the ruction period.
(4) Setbacks. Development shall maintai st 50 feet of property landward
from the ordinary high water mark as r ack and vegetation
conservation area, or develop It feet from the top of bluffs in
the shoreline jurisdiction, whic , ter,setback. Setback shall be
subject to provisions referenc 'i tion (e),
5). Vegetation Conservatio in Setback. The required setback area shall be
considered a Vegetation conservation area. Within the Vegetation Conservation Area, no
more than 30 percent of the area with native shoreline vegetation shall be cleared, and a
minimum of 70 percent of existing native trees shall be retained. At least 80 percent of
the native trees in the Vegetation Conservation Area over 20 inches in diameter at breast
height shall be retained. Trees determined by the city to be hazardous or diseased may
be removed. Additionally, the Director may allow removal of vegetation exceeding that
described above where an applicant agrees to replacement plantings that are
demonstrated to provide greater benefit to shoreline ecological processes than would be
provided by strict application of this section.
(d) Shoreline Modifications.
(1) Allowed modifications to the shoreline within Urban Conservancy designated areas
include the following:
a. Shoreline Stabilization. Allowed within Urban Conservancy designated areas
under the requirements imposed by [NEW SECTION Shoreline Modifications] division (a).
b. Piers, Moorage, and Floats. Allowed within Urban Conservancy designated
areas under the requirements imposed by [NEW SECTION Shoreline Modifications]
division (b).
c. Launching Ramp I Lift Station. Allowed within Urban Conservancy designated
areas with a Shoreline Conditional Use permit under the requirements imposed by [NEW
SECTION Shoreline Modifications] division (c), except under the following condition:
1. Permitted with Substantial Development Permit in parks and public access
areas withih the Urban Conservancy environment.
Page 22 of 29
City of Federal Way SMP - Article III. ShQreline Management - Draft Regulations
d. Dredging and Filling. Allowed within Urban Conservancy designated areas with
a Shoreline Conditional Use Permit under the requirements imposed by [NEW SECTION
Shoreline Modifications] division (e).
(2) 'Prohibited modifications to the shoreline within Urban Conservancy designated
areas include the following:
a. Breakwaters and Jetties.
(e) Shoreline Uses~
(1) Allowed uses within Urban Conservancy designated areas include the following:
a. Residential Development. Allowed within Urban Conservancy designated
areas under the requirements imposed within [NEW SECTION] Shoreline Residential,
division (e), (1), b, with the following additional restrictions: .
1. Setbacks. Resioential development shall maintain a minimum setback of 50
feet from the ordinary high water mark, or 25 feet from the top of bluffs, whichever is
greater. Exceptions to minimum setback requirements included in [NEW SECTION]
Shoreline Residential, division (e), (.1), b, for both single-family and multi-family
development, where in no case shall a setback less. than 30 feet from OHWM for single-
family or 50 feet from OHWM for multi-family, or 25 feet from top of bluffs be allowed.
b. Accessory Structures. Allowed within Urban Conservancy designated. areas
under the requirements imposed within [NEW ION] Shoreline Residential, division
(e), (1), c.
c. Recreational Developme
areas under the requirements .
division (e), (1), a.
d. Community Boati, Allowed in association with recreational
development, as regulated u." r he requirements imposed within [NEW SECTION]
Shoreline Residential, division (e), (1), b.
e. Utilities. Allowed within Urban Conservancy designated areas under the
requirements imposed within [NEW SECTION] Shoreline Residential, division (e), (1), d.
f. Transportation I Parking Facilities. Allowed within Urban Conservancy
designated areas under the requirements imposed within [NEW SECTION] Shoreline
Residential, division (e), (1), e.
thin Urban Conservancy designated
W SECTION] Shoreline Residential,
g. Office and Commercial Development. Office development may be allowed
with Conditional Use approval in the Urban Conservancy environment subject to the
requirements of this chapter, provided:,
1. The office or commercial use or activity is permitted in the underlying zoning
classification.
2. Office and commercial development shall maintain a setback of 75 feet from
the ordinary high water mark, or 25 feet from the top of bluffs, whichever is greater.
Using the stringline setback, the minimum buffer shall be in no case less than 50 feet
from OHWM or 25 feet from the top of bluffs.
3. Piers, moorages, floats, and launching facilities will not be permitted in
conjunction with office or commercial development; unless they are developed as part of
on-site public acce,ss to the shoreline.
4. Additional water quality standard must be met as per Shoreline Residential,
section 18-167(f)(2).
(2) Prohibited uses within Urban Conservancy designated areas include:
Page 23 of29
City of Federal W.ay SMP - Article III. Shoreline Management - Draft Regulations
a. Aquaculture.
18-170 Natural environment.
(~) Purpose. The purpose of the "natural" environment is to, protect those
shoreline areas that are relatively free of human influence or that include intact or
minimally degraded shoreline functions intolerant of human use. These systems
require that only very low intensity uses be allowed in order to maintain the
ecological functions and ecosystem-wide processes. Consistent with the policies of
the designation, local government should include planning for restoration of
degraded shorelines within this environment. (b) Designation criteria.
Designation criteria for the Natural environment are provided in the City's shoreline
master program, FWCC Chapter xx.:
(c) General requirements.
(1) Development waterward of the ordina h water mark is prohibited
except water dependent recreational uses an. I c utilities.
. (2) No ,structure shall exceed a i 021;,. et above average grade level.
This requirement may be modi' , of ny neighboring residences will
not be obstructed, if permi the applicable provisions of the
underlying zoning, and if th development is water-related or water-
dependent. .
(3) All development shall e required to. provide adequate surface water
retention and sedimentation facilities during the construction period.
(4) Setbacks. Development shall maintain the first 100 feet of property
landward from the ordinary high water mark as a required setback and vegetation
conservation area, or development shall maintain 50 feet from the top of bluffs in
the shoreline jurisdiction, whichever is the greater setback. Setback shall be
subject to modifications referenced in Section xx,
(5) Vegetation Conservation in Setback. The required setback area shall be
considered a Vegetation Conservation Area. Within the Vegetation Conservation area,
no more than 15 percent of the area with native shoreline vegetation shall be cleared, and
a minimum of 75 percent of existing native trees shall be retained. All native trees in the
Vegetation Conservation Area over 20 inches in diameter at breast height shall be
retained. Trees determined by the city to be hazardous or diseased may be removed.
Additionally, the Director may allow removal of vegetation exceeding that described
above where an applicant agrees to replacement plantings that are demonstrated to
provide greater benefit to shoreline ecological processes than would be provided by strict
application of this section.
(d) Shoreline Modifications. The following shoreline modifications are
prohibited within Natural designated shoreline areas:
Page 24 of 29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(1) Shoreline Stabilization;
(2) Piers, Docks, Moorages, and Floats;
(3) Launching Ramp I Lift Station;
(4) Breakwaters and Jetties; and
(5) Dredging and Filling.
(e) Shoreline Uses.
(1) Allowed uses within Natural designated areas include:
a. Residential Development. Single-family residential development may be
. permitted in the Natural environment with a Shoreline Conditional Use Permit subject to
the general requirements of Chapter 22 FWCC, Article xi', Divisions 3 and 4, and the
following:
1. Single-family residential development is permitted in the underlying zone
classification. .
2. Single-family residential development, is prohibited waterward of the ordinary
high water mark.
3. Setbacks.
i. Single-family residential development shall maintain a minimum setback of 100
feet from the ordinary high water mark as a veg n conservation area, or 50 feet from
the top of a bluff, whichever is greater."
b. Recreational Developmen
, requirements imposed within [
c. Utilities. Allowed with
Permit 'under the requiremen ~
division (e), (1), d.
(2) Prohibited uses within Natural designated areas include:
a. Office and Commercial Development;
b. Transportation I Parking Facilities that are not associated with single family
residential structures;
c. Community boating facilities; and
d. Aquaculture.
it n Natural designated areas under the
Sh eline Residential, division (e), (1), a.
t!'~ t1esignated areas with Shoreline Conditional Use
osed within [NEW SECTION] Shoreline Residential,
Page 25 of 29
City of Federal Way SMP - Article III. Shoreline Management -Draft Regulations
Division 3. Administrative Procedures
18-171 Shoreline Management Permit and Enforcement Procedures,
Adoption by Reference.
The city of Federal Way hereby adopts by reference the following sections or
subsections of Chapter 173-27, as amended, of the Washington Administrative
Code ("WAC") entitled Shoreline Management Permit and Enforcement
Procedures.
WAC:
(1) 173-27 -020 Purpose
(2) 173-27 -030 Definitions
(3) 173-27 -040Developments exempt from substantial development permit
requirement
(4) 173-27 -050 Letter of exemption
(5) 173-27-060 Applicability of Chapter 90.58 RCW to federal land and agencies
(6) 173-27 -090 Time requirements of permit
(7) 173-27 -100 Revisions to permits
(8) 173-27-120 Special procedure for Ii
(9) 173-27 -130 Filing with departme
00) 173-27-140 Review crite i
(11) 173-27-150 Review c
(12) 173-27-160 Review c
(13) 173-27-170 Review c
(14) 173-27-180 Applicati
use or variance permit
(15) 173-27-190 Permits for substantial development, conditional use or variance
(16) 173-27-210 Minimum standards for conditional use and variance permits
(17) 173-27-240 Authority and purpose
(18) 173-27-250 Definitions
(19) 173-27-260 Policy
(20) 173-27-270 Order to cease and desist
(21) 173-27-280 civil penalty
(22) 173-27-290 Appeal of civil penalty
(23) 173-27-300 Criminal penalty
(24) 173-27-310 Oil or natural gas exploration
Ility extensions and bulkheads
lo~ j ent
tiql deyelopment permits
naitional use permits
or variance permits
requirements for substantial development,
conditional
18-172 Permit processing and public notice.
(a) Permit Submittal. An application for a substantial development permit shall be
made to the department of community development on forms prescribed by the
department. Upon submittal of a complete application, and required fees, the
department shall instruct the applicant to publish notices of the application at least
once a week on the same day of the week for two consecutive weeks in a .
newspaper of general circulation within the city. The applicant shall also provide
additional public notice as prescribed in process III, FWCC 22-431 et seq. (Ord. No.
Page 26 of 29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
90-38, ~ 1 (24.40), 2-27-90; Ord. No. 97-291, ~ 3, 4-1-97; Ord. No. 98-323, ~ 3, 12-1-98;
Ord. No. 99-355, ~ 3, 11-16-99) ,
(b) Procedure f6r review. The substantial development permit shall be reviewed
under the provisions of process III, FWCC 22-386 et seq., and the WAC 173-27
procedures adopted by reference in FWCC 18-169. The director of community
development services shall be the final approval authority for the permit. (Ord. No.
90-38,91(24.50),2-27-90; Ord. No. 97-291, ~ 3, 4-1-97; Ord. No. 98-323, 9 3,12-
1-98; Ord. No. 99-355, 9 3, 11-16-99) .
18-173 Shoreline Exemption.
.'
(a) The purpose of a shoreline exemption is to provide an approval process for
uses and activities which do not trigger the need for a substantial development
permit, but require compliance with the shoreline guidelines and the provisions of
the City's SMP.
(b) If the use, activity or development meets the requirements for an exemption
as per"'!AC 173-2:-040, the applica~t may subm' '" ~f1 aut.horized sta~ement of
exemption to the director of commumty deve .. (services for review and
approval. '
18-174 Shoreline variance.
(a) The purpose of a shore e 's to grant relief to specific bulk,
dimensional or performance s >, i set forth in the shoreline master program,
and where there is an extraorclft ry.or unique circumstance relating to the property
such that the strict implementation of the shoreline master program would impose
unnecessary hardship on the applicant or thwart the policies of the Shoreline
Management Act.
(b) When a variance is requested, the substantial development'permit and the
variance shall be reviewed under the provisions of process IV, FWCC 22-431 et
seq., and the hearing examiner shall be the final approval authority for the City of
Federal Way. The Department of Ecology shall be the final approval authority
under WAC 173-27-200.
, ,
(c) A variance from the standards of the master program may be granted only
when the applicant can demonstrate that all the following conditions will apply:
(1) That the strict requirements 'of the bulk, dimensional or performance
standards set forth in the master program precludes or significantly interferes with
a reasonc;lble use of the property not otherwise prohibited by the master program;
(2) That the hardship described above is specifically related to the property,
and is the result of unique conditions such as irregular lot shape, size, or natural
features, and the application .of the master program, and. not for example, from
deed r~striction or the applicant's own actions;
(3) That the design of' the project will be compatible with other permitted
activities in the area and will not cause adverse effects to adjacent properties or
the shoreline environment;
(4) That the variance authorized does not constitute a grant of special privilege
not enjoyed by other properties, and will be the minimum necessary to afford relief;
(5) That the public interest will suffer no substantial detrimental effect;
Page 27 of 29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
(6) That the public rights of navigation and use of the shorelines will not be
adversely affected by the granting of the variance when the proposal is for
development located. waterward of the ordinary high water mark, or within
wetlands, estuaries, marshes, bogs or swamps; and
(7) That consideration has been given to the cumulative effect of like actions in
an area where similar circumstances exist, and whether this cumulative effect
would be consistent with shoreline policies or would havesub~tantial adverse
effects on the shoreline.
(d) Shoreline varianc'es may not be used to permit a use that is specifically
prohibited in an environment, or to vary uses permitted within an environmental
designation. (Ord. No. 90-38, 91(24.60.10-24.60.40), 2-27-90; Ord. No. 97-291,
93,4-1-97; Ord. No..98-323, 93, 12-1-98; Ord. No. 99-355,93, 11-16-99)
18-175 Conditional uses.
(a) Conditional use permits are allowed to provide greater flexibility in varying
the application of the use regulations of the shoreline master program in a manner
which will be consistent with the policies of Chapter 90.28 RCW, particularly where
denial of the application would thwart the policies of the Shoreline Management
Act.
(b) When a conditional use is requested,
.and the conditional use shall be revie e II
FWCC 22-431 et seq., and the
authority for the City of Feder
approval authority under WAC
(c) Conditional uses have 'r] and special characteristics which require a
special degree of control to m e the uses com'patible with other existing or
permitted uses in the same environment, and to assure that the use is in the public
interest. In authorizing a conditional use permit, special conditions may be
attached to the permit by the hearing examiner to prevent undesirable effects or
mitigate environmental impacts of the proposed use.
(d) Conditional use permits shall be authorized only when they are consistent
with the following criteria:
(1) The proposed use is consistent with the policies of RCW 90.58.020 and the
policies of the master program;
(2) The use will not interfere with normal use of public shorelines;
(3) The use will cause no unreasonable adverse effects on the shoreline. or
surrounding properties or uses, and is compatible with other permitted uses in the
area;
(4) The public interest will suffer no substantial detrimental effect;
(5) Consideration has been given to cumulative impact of additional requests
for like actions in the area.
(e) Other uses not set forth in the shoreline master program may be authorized
through a conditional use permit if the applicant can demonstrate that other uses
are consistent with the purpose of the shoreline environmental designation and
compatible with existing shoreline improvements or that extraordinary
, circumstances preclude reasonable use of the property; however, uses specifically
prohibited by the master program may not be authorized. (Ord. No. 90-38, 9
1 (24.70.10 - 24.70.50),2-27-90; Ord. No. 98-323, 9 3, 12-1-98; Ord. No. 99-355, 9
3,11-16-99; Ord. No. 00-375, 92,10-3-00)
, stantial development permit
tH provisions of process IV"
r , all be the final approval,
artment of Ecology shall be the final
Page 28 of 29
City of Federal Way SMP - Article III. Shoreline Management - Draft Regulations
Page 29 of 29
5309 Shilshole Avenue NW
Suite 200
Seattle, WA 98107
206,789,9658 phone
206,789,9684 fax
www.adoltson.com
memorandum
date January 15, 2006
to Isaac Conlen, Senior Planner.
from Teresa Vanderburg and Kent Hale
subject Federal Way Shoreline Master Program (SMP) Update -
Cumulative Impacts Analysis
The guidelines state t
functions and/or uses,
adverse cumulative i
development opportu
The purpose of this memo is to assess the cumulative impacts
development in the shoreline that would result from develo~
proposed City of Federal Way SMP, Under the shoreline
evaluate and consider cumulative impacts of reasonabl
shorelines of the state (WAC 17-26-186(8)( d)). Cu rent
and beneficial effects of other established regul pr
on Iy foreseeable future
nd a,' tivities over time under the
~~';V;~~
~P' e' al jurisdictions are required to
filE U. ure development in the
.r\ eeable future development,
ified and must be discussed.
Puget Sound shoreline in the
y limits and the City's potential
ulative impacts is to insure
d regulations will achieve no
line conditions are identified
of
ntalnpolicies, programs, and regulations that address
he burden of addressing cumulative Impacts among
cumulative impacts should consider:
· Current circu
· Reasonably fo
· Beneficial effe
laws."1
he shorelines and relevant natural processes;
re development and use of the shoreline; and
y established regulatory programs under other local, state, and federal
1 WAC 173-26-186(8)(d)
EXHIBIT ---1::L-
(?)AGE OF
....
City of Federal Way SMP
Cumulative Impacts Analysis
This cumulative impacts assessment uses these three considerations as a framework for evaluating the
potential long-term impacts on shoreline ecological functions and processes that may result from
development or activities under the proposed SMP over time.
Current Shoreline Condition
As part of the City's SMP update process, a shoreline inventory and map tJ.I,io was prepared in the
spring and summer of 2006. The Shoreline Inventory and Characteriza' identifies existing conditions
and evaluates the ecological functions and processes in the City's s jurisdiction. The inventory
included all shoreli,ne areas within the City of Federal Way, as we'""." .. .J~ found in the Potential
Annexation Area (PAA), east of the city limits. r! '
The City has two main types of water bodies that are re l!J~~ t e City's SMP: marine coastal
shorelines of Puget Sound and freshwater lakes over 2 ac[es)~ siz " he Puget Sound marine
coastal shoreline is designated a "shoreline of statewid si,gnfficanc "J he freshwater lakes under
SMA regulation within the, city are Steel Lake, N La d the n estern shore of Lake Killarney.
Further, the City of Federal Way has identified,: lea I ,I~. the t of the City and east of the
Interstate 5 corridor for future annexation. Thi 1 is to a Potential Annexation Area
(PAA). Lakes subject to SMA regulatio cat in 11M s P clude Star Lake, Lake Dolloff,
Lake Geneva, Five Mile Lake and th ini ' e KiI ey. The freshwater lakes are
all designated as "shorelines of t ak thereof n e PAA are currently regulated
under the King County SMP. Th in Fed ,;'~t Way or its PAA that meet the
definition of shorelines of th stat '
ne area, including those areas within the
ated along the Puget Sound marine
long freshwater lakes. Key findings of the
The City of Federal W
PAA. Of this total, an
coastline. The, remai
inventory and charact
Watershed Context
The City of Federal
- the Duwamis]1-Gree
areas of Pugef Sound
PAA are addressed a
and to Mill Creek and
the northern portions
The majority of the Fe ral Way area lies within WRIA 10 and drains to either the White River or to
Hylebos Creek. North Lake, Lake Geneva, Lake Killarney and Five Mile Lake are located within this
watershed. These lands drain to the south. The White River flows to the Puyallup River before entering
Puget Sound at Commencement Bay. The Hylebos flows to the south into Tacoma and enters the
Hylebos Waterway at Commencement Bay. '
Physical and Biological
Bluffs, beaches, bays, and the mouths of several freshwater streams characterize the City's 'coastal I
nearshore shoreline. Approximately 40 percent of the City's coastal shoreline has been modified with
riprap, concrete or wooden bulkheads. Structures in the shoreline can limit the amount of sediment
Page 2 of 10
""~..,, ....,. t. i ,rf
~ 'H 1 . ), ,'''~
~ '.t"~ 'io~\:.tt
....' ,.... , :'Jl'+d ( ,
"'tV, ~,)"q!),
<\,.,....'!-' ~.;.I~.Id.. . <r.-Ilfto>~,~""""",}- ~~..~ ~.' ..
city of Federal Way SMP
Cumulative Impacts Analysis
transported from upland areas to the beach, and are known to cause erosion and loss of some habitats
such as sand and fine gravel beaches. Currents naturally move sediments across the beach. and .
alongshore in continual cycles, but these structures interrupt the natural supply and distribution of
sediments, causing a change in sediment composition within the nearshore area. However, coastal
. shoreline in Dumas Bay and Dash Point State Park are in a more natural condition I and coastal
processes are less altered. Fish and wildlife that utilize the shoreline depend on these nearshore
processes to maintain their habitats and ultimately their populations. Important feeder bluffs have been
identified both north and south of Dumas Bay.
The freshwater lakes in the City are located on a broad plateau in th rn half of the City and in the
PAA. The plateau developed from glacial recessional deposits an~:, the glaciers melted, lakes
fO,rmed in the scour areas. Lakes in the City drain to five main" a1r'f,;,n"",~,.""g, ',.e,;',',>,/,','.~ ins including 1) the Puget
Sound, 2) the Green River, 3) Mill Creek, 4) the White River '~~9J~.IJ~~~lebos. Lake shorelines have
been modified with bulkheads and other bank protection, al~Jti ~~;significant areas of natural
shoreline conditions. On Steel Lake, Star Lake and Five L~k,' " oximately 20 to 50 percent of
the shoreline has been modified with bulkheads. Shore 6dific s are less frequently occurring
on the remaining lakes. In general, shorelines wi the are mo ighly altered in comparison to
those within the PAA.
b,..~ety 0 ,~, uatic and terrestrial species
n (~ride vari~1Jof invertebrates. Of special
cies an 'pecies of local importance
,Chinoo salmon (threatened), coho
such as surf smelt and sand lance (prey for
present along the City's coastal/nearshore
,rthern end of Dumas Bay and northward.
stuary with regional importance within the
The freshwater shorel
salmon ids or habitat ~
waterfowl, trout, and
residents. Also, good
habitat in streams suc
nd its PAA do not provide habitat for anadromous
s. However, these lakes do provide general habitat for
ec e Important to the character of Federal Way and the lakeshore
, the freshwater lakes is important for downstream salmonid
reek, Joe's Creek, Mill Creek, Lakota Creek, and the Green River.
Land Use and PubIiOJ"~,C ss .
The major land uses ~~~ the Federal Way coastal/nearshore shoreline are single-family homes,
parks, and public facilities. The City's most common shoreline use is single-family residential, which
occupies 55 percent of the coastal shoreline. Parks and public recreational facilities occupy 18 percent
of the shoreline. These uses include Dash Point State Park, Dumas Bay Park, Dumas Bay Centre,
and Poverty Bay Park. Parks provide opportunities for beach access, fishing, hiking and recreation.
Land uses along the City's freshwater lakes are primarily single-family residential and public parks.
Single-family residential use occupies between 55 and 80 percent of the shoreline on most lakes, with
the exception of North Lake (35 percent) and Five Mile Lake (32 percent). Parks, boat ramps, and
pub.lic facilities occupy 9 to 39 percent of the lake shorelines. Public access to the lakes occurs via
Page 3 of 10
City of Federal Way SMP
Cumulative Impacts Analysis
parks including Steel Lake Park, Lake Geneva Park, Lake Killarney Park and Five Mile LakePark, as
well as several boat ramps owned by'Washington Department of Fish and Wildlife.
Reasonably Foreseeable Future Development and Use
The City of Federal Way has an established land use pattern in the shoreline jurisdiction that predates
the current regulatory regime. The pattern generally includes public wat ~font parks and single-family
residential development within the City's shorelines. Since 1999, at t ,existing SMP regulations
were adopted, the City has received an average of 2 building per' y, ar for residential
construction within the shoreline. A total of 11 building permits in the shoreline jurisdiction
since 1999. In addition, there are only two residential piers Sound coastal shoreline and
no public marina within the City. '
Currently, the Puget Sound shoreline within the City is J
parcels along the City's Puget Sound shoreline, f
these are located in areas of residential zoning.
parcels are found along the freshwater lake sh
the City's PM. However, critical areas and th
parcels within the freshwat~r lake sho s (
be developable except through the e v
of the undeveloped parcel along ~g,~~1 ne
encumbered by critical areas. Crili~l; . in
buffers, and steep slopes r 4i~, rc
City of Federal Way, th I '. 0
along both the Puget
patterns that are cons
established by the Cit
Number of
Undeveloped
Parcels (%of
total)
Undeveloped
Parcels (%)
considered
developable
Undeveloped
Parcels (%)
encumbered
by Critical
Areas
Portion of Lake Killarne
WlmhiilN f?IAA
Portion of Lake Killarne
220 39 18%
96 93 97%
131 49 37%
5 5 100%
90 56
105 96
60
67
112
52 93%
70 63%
40 78%
47 70%
54 87%
Page 4 of 10
City of Federal Way SMP
Cumulative Impacts Analysis
Based on the nature of the shoreline within the City limits, the lack of extensive vacant developable
land and consistency among land use regulations and long-range plans, reasonable foreseeable
development will likely include redevelopment of property as well as new development, particularly near
the lakes in the PM. Redevelopment and development will not likely result in significant changes in
types of land use (e.g. single-family to multi-family, commercial, or industrial uses).
Within the PM, there is moderate potential for new development along the shorelines of freshwater
lakes. Between 12 and 30 percent of the total lots along these lakes is co sidered developable within
the shoreline jurisdiction. Due to existing land use patterns, King Count ning, and proposed
designation for shoreline areas within the City's Comprehensive Plan evelopment will likely be
single-family residential along the lakes in the PM. Once annexe nallakefront residential.
development is anticipated.
Changes to Shoreline Environment Designations
At the time of incorporation in 1990, the City of Federal
and 1999, the City developed and adopted its ow ocal
policies are contained in the land use element Fe
Section 2.8.5). Shoreline development Jegulati nd
18, Article III, of the Federal Way City Code (F 91
established a system of "sho'reline en . en na
policies and use regulations within . di sh
designations function like zoning Th ey
regulations for density, setbacks, lI:k,he p
regulations for portions of "~, e e j
designations are basef:(;,,~i: ti nn >,0
~~;~~;~;n~~~~~ . ~1 ;; ~\~~S~gh~~~~: ha1~ ~:~:~d;~ ~hO~~~~~~~' 3)
annexation of North L Killarney. These areas were originally designated as
Urban Environment b nd are currently being managed by the City using the
County's SMP provisi nexations, the City's SMP was left with several
inconsistencies. Mos r r sidentiaJ neighborhoods are designated differently (i.e. Jakes
with similar residentia t d differently under the City's SMP versus King County's SMP for
recently annexed are , to, C s shoreline parks are similarly designated differently (Poverty Bay
Park and Dash Point '.Lt,.flitel?' rks are designated Conservancy and Dumas Bay Park is designated
Natural). "
The proposed SMP a resses inconsistencies in the 1999 SMP by providing a new system of
environment designations, in compliance with State guidelines (WAC 173-26-211). The new system
applies designation criteria and management policies consistently across areas with similar current and
planned land uses and resource characteristics. The new shoreline designations also pre-plan for
future annexation areas so that future inconsistencies in shoreline development a're avoided.
Eliminat.ion of these inconsistencies will help the City reduce net loss of ecological function in the
shoreline over time.
The proposed SMP environment designations includes a "Shoreline Residential" environment for areas
of the City that are characterized by single or multi-family reSidences or planned as such; an ,"Urban
Conservancy" environment that includes waterfront park areas and residential areas, and an "Natural"
Page 5 of 10
City of Federal Way SMP
Cumulative Impacts Analysis'
environment which is designated for the purpose of protecting those shoreline areas that are relatively
free of human influence or that include intact or minimally degraded shoreline functions sensitive to
human use. The proposed SMP did not include an "Aquatic" shoreline environment; since all shoreline
uses in the City are paired with an upland use and therefore another shoreline environment. The
proposed environment designations are consistent with both the existing land use pattern and the
Comprehensive Plan future land use designations, .
Changes to Development Standards and Use Regulations
The proposed SMP offers several changes to the development regul~t1,,<,
conservation and prohibit activities that would cause adverse impa J~,sb,
processes. These changes include limiting shoreline modificati
revetments along much of the City's shoreline. These shore!"
the natural net-shore drift direction and the availability an .
Further, the conservation of shoreline vegetation has b
regulations for the City to further stabilize shorelands an
related to development of specific uses in the sho!,.line
ecological functions and processes, while conti .".fn to
allow sensitive development. The proposed ch ',~l(; s a
DEVELOPMENT I
USE
Table 2. Proposed Changes to S
, ShQreJine Modifica,tion
Bulkheads and
shoreline stabilizatio
.>.
j.,' '.
mitted (P) in Shoreline
esidential and Urban
Conservancy, but prohibited in
Natural. Requires applicant to
demonstrate that softshore
armoring techniques do not provide
adequate upland protection.
Bulkheads not permitted unless
necessary to protect primary
structures.
Breakwaters
rohibited in all
environments.
Permitted on freshwater
shorelines, except for in
Natural Environment.
Prohibited in all
environments.
Prohibited (X) in all environments.
Piers and Docks
Permitted on freshwater shorelines,
except for in Natural Environment.
Prohibited (X) in all environments.
Jetties and Groins
,";';~~:E~; .,,,
>:Shoreline Use
Office and
Commercial
Oevelo ment
Permitted in all
environments.
Permitted in Urban Conservancy
environment. Prohibited in all other
environments.
Page 6 of 10
City of Federal Way SMP
Cumulative Impacts Analysis
DEVELOPMENT I
USE
Recreational
Develo ment
Residential'
Development
1999 SMP
REQUIREMENTS
Permitted in all
environments.
Permitted in all
environments.
2007 SMP UPDATE
REQUIREMENTS
Permitted in all environments.
Accessory Structures
Permitted in all
environments.
Permitted in all environments,
except Conditional Use in Natural
Environment.
Permitted in all
except Condi .
Environme
Permitt
exce
E
P
e
E
Changes to the Tre
Much of the develop
adoption of the Washi
in the City's shoreline
"non-conforming" use st
policies and regulatio~t
Utilities
Permitted in all
environments,
Transportation/Parking Permitted in all
Facilities environments.
are, in general, more
II environments, but
d to the Urban Conservancy
larly for shoreline stabilization), .
~I e "soft-shore"erosion control or
ld be re ired to demonstrate why a "soft-
ing developme'nt. Over time these
cological processes as properties are
;~ses and Structures
oreline predates incorporation of the City and or
ent Act in 1971. Several properties and developments
nt zoning or SMP regulations. The 1999 SMP addresses
n t shoreline jurisdiction. However, the proposed SMP includes
ned to increase protection of shoreline resources over time.
Under the proposedw. sir ctures or uses that were legally established, but which now do not
conform to the City's. ode or are non-conforming with regard to the use regulations in the
proposed SMP may c e as long as they do not increase or expand in their non-conformity. The
policies and regulatio related to non-conforming structures and non-conforming uses in the shoreline
are also consistent with the City's zoning code regulations.
Restoration Planning
Consistent with state guidelines (173-26-186), the proposed SMP includes a new section of goals and
policies addressing shoreline restoration within Federal Way. The goals and policies for restoration
have also been modified to acknowledge that the City's intent is to meet the "no net loss" standard, and
result in an overall improvement to the condition of the habitat and resources within the shoreline
jurisdiction of the City. .
Page 7 of1 0
City of Federal Way SMP
Cumulative Impacts Analysis
The draft Restoration Plan dated December 2006 addresses the shoreline restoration element of the
SMP. The proposed SMP identifies restoration opportunities that include programmatic opportunities
(e,g. surface water management; water quality improvement; public education), site-specific
opportunities (e.g. protection of feeder bluffs, restoration of stream mouth deltas and pocket estuaries),
regional plans and policies for Puget Sound restoration, and potential funding and partnership
opportunities. The SMP's restoration planning is focused on areas where shoreline functions have
been degraded by past development activities. These areas with impaired functions were identified in
the City's Shoreline Inventory and Characterization. The implementation 0 these restoration
opportunities will have the effect of improving shoreline ecological functi . within the City over time.
The City's existing Sh
use chapter of the Cit
oriented uses and exi
natural resources (Cit
designations as Natur
intensity of developm
use vision expressed
and policies will be in
Beneficial Effects of Any Established Regul
Local, State, and Federal Laws
grams under Other
The City's SMP is meant to be consistent with and work
federal programs and planning documents to pr t th
and protect the health and safety of City reside The
following:
ith several City, State and
I alues of shoreline resources
lude, but are not limited to, the
r
goals and policies are included as an element in' the land
pr nsive Plan. These goals and policies encourage water-
u es in balance with protection of the Puget Sound shoreline's
y,2002). This document also establishes shoreline environment
rv ncy, Rural, or Urban Environments, depending on the land use and
proposed SMP environmental designations are consistent with the land
Comprehensive Plans. Following adoption, the City's proposed SMP goals
. orated as a chapter of the City's Comprehensive Plan.
Federal Wav City Code Chaoter 22: Zoning - Title 22 of the City's Municipal Code establishes zoning
designations. Zoning implements the Comprehensive Plan's vision for future land use. Zoning
designations near the Puget Sound shoreline include Single Family Residential, and Multifamily
Residential. Zoning designations near the freshwater lake shorelines include Single Family Residential
and Corporate Park. Shoreline zoning is consistent with the designations in the proposed SMP,
Federal Way City Code. Chaoter 22. Article XIV. Critical Areas - Chapter 22 of the FWCC establishes
development standards, buffers and permitted uses in designated critical areas, Critical areas include
geologic hazardous areas, streams, regulated lakes, regulated wetlands, regulated wellheads and
critical aquifer recharge areas and wellhead protection areas. Standards in this chapter are designed
Page 8 of 10
City of Federal Way SMP
Cumulative Impacts Analysis
to protect these areas from adverse impacts. The City updated it Critical Areas code in 1999.
Designated critical areas are found throughout the City's shoreline jurisdiction, particularly streams,
flood hazard areas, and geologic hazard areas. Consistent with state guidelines, development
standards for critical areas that are physically located in the shoreline jurisdiction have been
incorporated into the proposed SMP by reference.
City of Federal Way Surface Water Manaaement Division
The City's Surface Water Mcmagement Utility is guided by the Surface Wa~er Facilities Plan (1994) and
the City's Comprehensive Plan (2002). The Surface Water Manageme } ivision (SWM) is responsible
for the comprehensive management of the City's surface water syste is involves protecting
developed and undeveloped properties from flooding I runoff and ~,~Iity problems I while
continuing to accommodate new development. The SWM Divis' I2fomotes the preservation of
natural drainage systems, protection of fishery resources an itat. The City's Surface Water
Capital Improvement Program identifies I funds, and imple cific projects intended to
provide flood control or alleviation, improve and enhanc t, replace culverts to improve
fish passage, and improve water quality from stormwat rface Water Management
restoration program is currently focused on strea eso d emphasis on restoration of
lakes and marine shorelines.
State and Federal
A number of state an es ay have jurisdiction over land or natural elements in the City's
shoreline jurisdiction. ent proposals most commonly trigger requirements for state or
federal permits when ct etlands or streams; potentially affect fish and wildlife listed under
the federal Endanger ~' es Act (ESA); result in over five acres of clearing and grading; or affect
the floodplain or flood . ' . s with local requirements, state and federal regulations may apply
throughout the City, b J!1,r.gulated resources are common within the City's shoreline jurisdiction. The
state and federal regu 'tions affecting shoreline-related resources include, but are not limited to:
Endanaered Soecies Act
The federal ESA addresses the protection and recovery of federally listed species. The ESA is jointly
administered by the National Oceanic and Atmospheric Administration (NOAA) Fisheries (formerly
referred to as the National Marine Fisheries Service), and the United States Fish and Wildlife Service
(USFWS).
Page 9 of 10
City of Federal Way SMP
Cumulative Impacts Analysis
Clean Water Act rCWA)
The federal CWA requires states to set standards for the protection of water quality for various
parameters, and it regulates excavation and dredging in waters of the U.S., including wetlands. Certain
activities affecting wetlands in the City's shoreline jurisdiction or work in the adjacent rivers may require
a permit from the U,S. Army Corps of Engineers and/or Washington State Department of Ecology under
Section 404 and Section 401 of the CWA, respectively.
es that use, divert, obstruct,
ay affect fish habitat.
ce water from industrial
also required for stormwater
es, and municipal stormwater
ast, is largely developed in residential uses.
coastal shoreline jurisdiction. On the other
ng the freshwater lake shorelines,
-0
, ~..J1 n
~~~/nc
The proposed SMP p ~~.~ a new system of shoreline environment designations that establishes
more uniform manage' ent of the City's shoreline. The updated development standards and regulation
of shoreline modifications provides more protection for shoreline processes. The updated standards
and regulations are more restrictive of activities that would result in adverse impacts to the shoreline
environment. The restoration planning effort outJine,d in the proposed SMP provides the City with
opportunities to improve or restore ecological functions that have been impaired as a result of past
development activities. In addition, the proposed SMP is meant to compliment several City, state and
federal efforts to protect shoreline functions and values. .
Based on assessment of these factors, the cumulative actions taken over time in accordance with the
proposed SMP are not likely to resuJt in a net loss of shorelinE;l ecological functions from existing
baseline conditions.
Page 10 of 10
~.
CITY OF ~
Federal Way
City of Federal Way
,
Shoreline Master Program Update
Citizen Advisory Committee Meeting - July 26, 2006
Meeting Minutes
Attendees:
Peter Townsend
Chris Andersen
Bill Baldwin
Hal Whidden
Linda Ellingson
Isaac Conlen, City of Federal Way
Greg Fewins, City of Federal Way
Teresa Vanderburg, Adolfson
Marlies Weirenga, EnviroVision
1. Introductions
The group introduced themselves and provided individual issues of concern and questions
related to the SMP update process. The issues were:
. What does SMA require?
· Concern about private property takings and too many regulations..
· Desire to have public access to public shorelines.
· Balance property rights and environmental concerns.
· Allow private property owners use and enjoyment of shorelines.
· Consider beach improvements on lakes. .
· Concern with the environmental condition of the Puget Sound and Dumas Bay. Drastic
changes over the past few years.
Public concerns coming out of the June 7th Open House were discussed. These were:
· How shorelines are currently regulated in the PM;
· The value of incorporation into the City and regulatory differences for shorelines in PM,
which are governed by King County, versus future City regulations;
Doc. J.D.
EXHIBIT .~
PAGE OF
· A desire for non-.motorized boat use on certain lakes;
· Water quality concerns in the lakes;
· Flooding concerns related to stormwater;
· Desire to be able to maintain and repair existing docks; and
· Impact of other regulations related to shorelines (Le. Corps, state, local permits)
2. Overview of the SMP update process
Isaac introduced the City's SMP update process and described the requirements of the Ecology
grant funding this process. He described the current SMP program elements and referred to the
packet distributed to the group (Handout 1-Chapter 2, Land Use Element of Comprehensive
Plan; Handout 2 - FW City Code, Article III, Shoreline Management).
Teresa described the SMP update requirements using the new state guidance from 2003
(Handout 4 - Introduction to Washington's Shoreline Management Act, Handout 5 - What is a
Shoreline Master Program? From Ecology web page at
http://www.ecv.wa.Qov/proqrams/sea/SMAlst Quide/SMP/SMPintro.html). Cities in western
Washington must update their SMP by 2009. She described the requirement to evaluate
ecosystem-wide processes and look at "no net loss" of shoreline function. She described the
timing of the work related to the grant. The City would like to complete the SMP update work by
June. 2007 as per grant requirements. A Technical Advisory Committee (TAC) has been formed
. to review the shoreline inventorY report, which is nearly completed. The role of the CAC is to
provide any additional local information into the existing conditions of the shorelines, provide
input into the process, particularly the goals and policies and shoreline environment
designations.
3. Components of the SMP
Teresa described the components of the SMP. She referred to Handout 5 - Book Graphic,
showing how the FW Comprehensive Plan and City Code are integrated into a Shoreline Master.
Plan or Program to cover all the required elements of the SMP. Ecology reviews and approves
. the local program.
4. Proiect Schedule
The overall project schedule was discussed. The packet for the meeting included a general
schedule (Handout 6) that outlined major deliverables and time frames. The inventory report is
almost complete and is due to Ecology as a draft by August 31st. Shoreline goals, policies, and
environment designations will be addressed next, with adoption slated for spring 2007.
5. Issues of Citizen Concern
The July 26th CAC meeting started with the issues of concern as outlined above.
6. Overview of the Draft Shoreline Inventory & Characterization Report
Teresa and Marlies summarized the contents of the draft inventory report for the group. Data
sources were described, and general results. A 3-page summary of findings for the inventory
and characterization was introduced to the group (Handout 7) and discussed. In addition, a
Doc. J.D.
. .~... \ c,~ ~ tl "';;.t ;;:4
. . ~ ~ {..~ ~ ~ l.if.......,.,,-
,.,...'....~....,', . ". ..,.... ..,'~ '.~"".'" ,'.
'''''. _, .~,,_ ':} O,__,_....~".~ .3 DN.'I
subset of maps from the draft map folio were provided to the CAC (Handout 8) including the
following figure examples:
Figure 1 - Shoreline Planning Areas
Figure 2 - Regional Context
Figure 3 - Topography and Hydrology
Figure 4 ~ Geology
Figure ?? - Parks and Open Space
Figure 7 - Nearshore Coastal Processes
Figure ???-B - Current Conditions, Dumas Bay (Reach 1 B) and Puget Sound Ea.st (Reach 1A)
Figure ???-D - Current Conditions, Star Lake (Reach 3)
Figure ???-F - Current Conditions, North Lake (Reach 6) .
Figure ??? - Coastal Restoration Opportunities
Figure ??? - Lake Restoration Opportunities
7. Next Steps
The group discussed the agenda for next time. Isaac said that the draft shoreline inventory
report would be posted on the City's web page for public review on or immediately after August
1, the due date for delivery of the report to Ecology for review. Isaac said that any additional
resources that the group may have or comments to the report could be emailed to him.
Additional references noted were the EIS or other materials related to the Lakehaven
Wastewater Treatment Facility and its outfall, environmental reports related to work at the Des
Moines Marina, and a report prepared by the city in connection with acquisition of Dumas Bay
Park. Isaac and Teresa took notes to follow-up on these references.
Peter Townsend asked what is expected from the CAC before the next meeting. Isaac said that
this is just the introduction to the process and we will be sending out a packet for the next
meeting to begin discussion of the goals, policies and shoreline environment designations. Hal
Whidden asked if he wanted markups to the existing regulations or Land Use element of the
Comp Plan. Isaac said that this would be coming up soon, but that we weren't quite ready for
markups; please keep them for next time.
Isaac said that we are anticipating three more CAC meetings - probably monthly from August
through September. Contact him by email for questions or comments.
Doc. J.D.
~
CITY OF ~
Federal Way
City of Federal Way
Shoreline Master Program Update
Citizen Advisory Committee Meeting - August 30, 2006
Meeting Minutes
Attendees:
Peter Townsend
Chris Anderson
Hal Whidden
Chuck Gibson
Bill Baldwin
Isaac Coolen, City of Federal Way
Greg Fewins, City of Federal Way
Don Robinett, City of Federal Way
Sandra Lange, Washington Department of Ecology
Marlies Weirenga, EnviroVision
Kent Hale, Adolfson
Aaron Booy, Adolfson
1. Introductions
The meeting began at 7:00pm. The group introduced themselves, as there were a number of new faces
since the July 26, 2006 meeting.
2. Review of Julv 26, 2006 CAC meetina minutes
July 26',2006 CAC meeting minutes had been distributed to the CAC for review prior to this meeting. No
. comments or concerns were raised upon review of the minutes.
3. Review of CAC roles and schedule
. .
. .
Isaac reviewed the introductory letter that all CAC members had received, and reiterated the schedule for
the remaining CAC meetings, including the major focus (shoreline designations, polices and regulations,
and restoration opportunities) for each meeting. The CAC is intended to focus on big picture and policy
issues and is not intended to get into code level review of the regulatory component of the SMP.
Concerns were raised regarding the role of the CAC, including:
Doc. J.D.
· With all the 'masters' (e.g., the Planning Commission, City Council, Ecology) in the SMP update
and approval process, concern was raised as to how or whether the input of the CAC would
be integrated; and
· Concern as to whether individuals' specific concerns would have an opportunity to be addressed
within the confines of the CAC process; Isaac indicated individual concerns could be raised,
especially with regard to policy issues. He also indicated he would meet with members on an
individual basis to discuss detailed comments if desired.
· Two members brought written comments on SMP items they had reviewed and submitt~d them to
the City.
4. Overview of the Shoreline Manaaement Act (Sandra Lanae. Department of Ecoloay)
Sandra explained how the Shoreline Management Act (SMA) had stemmed from a citizen movement in
the late 1960s that focused on conserving natural shoreline environments. The state legislature, in
creating the SMA in the early 1970s, attempted to balance resource protection with human use.
Sandra explained Ecology's role in the local Shoreline Master Program (SMP) update process (as in
Federal Way). She stated that the local government is charged with the primary responsibility of
undertaking the planning required by the state guidelines (WAC 173-26). Ecology plays a largely
supportive role in the process, ensuring th1;lt state guidance documents and the SMA are successfully
followed. She explained that Ecology reviews and/or approves shoreline permitting decisions according
to WAC 173-27, the SMA permitting and enforcement procedures. .She stressed that local SMPs cannot
deviate from the permit approval criteria established by WAC 173-27. .
Regarding the SMA overview, CAC questions and comments included:
· Is the Federal Way marine shoreline a Shoreline of Statewide Significance?
(What is the designation?). It was discussed and agreed that Puget Sound in Federal Way is
designated a shoreline of statewide significance waterward of the extreme low tide.
· Use of the term 'natural environment' ~ after more than a century of development (including
logging) can we call anything truly 'natural' anymore?
· Consistencies (and inconsistencies) between the SMA and other City regulations (such as the
critical areas ordinance) - is this accounted for during the SMP process? It was noted that
treatment of critical areas within shoreline jurisdiction is addressed a~ part of the SMP
update, however, the scope does not include updating of the city's critical areas regulations.
A suggestion that consistency between the SMP and other regulations be adopted as a goal
or requirement for the SMP process and there seemed to be agreement this was appropriate.
5. Draft Shoreline Inventory & Characterization Report - Q & A
Kent generally described what is covered within the Draft Inventory & Characterization RepDrt (Draft I&C),
including: identification of critical areas, infrastructure, utilities, environmental conditions, and unique
resources within all shoreline planning areas. Kent asked if there were any questions regarding the Draft
I&C. Questions and concerns included:
· Where does information within the Draft I&C come from? [Response from Kent: Existing surveys
and inventories from the City or other regional organizations such as WRIA 9, existing City
. documents and reports];
· How are changing conditions documented within the SMP process? [Response from Kent: 7 year
review framework, in the interim it is left to the city to document changes];
· A concern that there has been recent (last 3 years) development in areas marked as 'natural' on
Draft I&Cmaps and that 2002 air photos are too dated; .
· A suggestion that 'unknown' information about. lake shoreline modifications could easily be
attained and should be attained; and
· A suggestion that memo structure could be improved, and that a few specific details seemed to
be incorrect - addressed specifically in comments which were provided to the City and
Adolfson;
Doc. J.D.
6. Shoreline Environment DesiQnations - ExistinQ & Proposed
Kent began by describing what Shoreline Environment Designations are and how they function. They
can be considered a zoning or land use overlay, that should be considered in concert with other zoning
designations. Kent highlighted that existing Environment Designations are reflected on handout maps
and that each designation coincides with certain land use restrictions. Proposed new Environment
Designations were introduced (with handout); Kent explained how they had been developed by Ecology
to streamline the designation process and better match Environment Designations with existing shoreline
designations throughout Washington State. Kent highlighted that the primary designations for the City
would likely be Shoreline Residential, Urban Conservancy, and Natural (due to current land use patterns
and natural resources in Federal Way). Comments on this point included:
· Are other Environment Designations (such as 'High Intensity') possible within Federal Way?
[Response from Kent/Isaac: Could be possible if Federal Way planning included a vision of a
high intensity uSe, such as a marina, however, no such plan exists]; .
· Is there a one to one (or other) relationship between the existing and new Environment
Designations? [Response from Kent: Some similarities, but no one to one relationship or
obvious other relationship - new system differs in more ways than it has similarities];
· Under new Environment Designations, what (if any) will be the major differences in policy and
land use regulations? [Isaac suggested that this would be further discussed at future CAC
meetings] ;
· Are the 6 new Environment Designations from Ecology the required choices, or could other
designation options be developed? [Response from Sandra Lange: the new system is pretty
much required to insure consistency statewide. Response from Kent: The guidelines do
allow you to develop new designation options for areas that were truly unique, however the
City's preference is tq first try and utilize the new designations as they appear in the WAC
guidelines};
· Concern raised - why would the CAC want to set Environment Designations in Federal Way
before the restrictions under each designation are understood and agreed upon? [Greg
suggested that the CAC process of setting designations and corresponding regulations would
not be completely linear, that designations might be re-adjusted once corresponding
regulations were further developed and understoodJ.
At this point, discussion began regarding new Environment Designation possibilities within the City of
. Federal Way by looking at the map, which included a preliminary look at where new designations might
be appropriate. Discussion began with the lake shorelines, and included the following points:
· A need to look at the current zoning when deciding what the new designation might be (example:
'Urban Conservancy' designation in an area zoned 'Office Park');
· Importance of looking at future land use mapping as much as current use; and
· Agreement that the preliminary lake reach Environment Designations (a combination of Urban
Conservancy and Shoreline Residential) seemed to be a reasonable starting point, with
understanding that they would be looked at again with policy and regulatory considerations.
Discussion next moved to the marine shoreline planning area. Kent began by noting that on the
preliminary map of new Environmental Designations, residential use shorelines were either designated as
Urban Conservancy or Shoreline Residential. The preliminary mapping had been based on the level of
ecological function existing at a given shoreline segment, with high-bluff areas (no bulkheads) showing a
higher degree of connection with the marine environment than low-bluff areas (with substantial
bulkheads). More intensely developed residential areas were generally proposed as Shoreline
Residential, less intensely developed residential areas were generally proposed as Urban Conservancy
and parks and public open spaces were generally proposed as Urban Conservancy with some
undeveloped portions proposed as Natural. Major topics of discussion included:
· Suggestion that Environment Designations should consider desired (future) ecological connection
in addition to existing ecological connection (Dumas Bay pocket estuary used as an
Doc. J.D.
example). [Kent noted that the comment gets into restoration opp.ortunities and restoration
planning, which would be an area of focus at a later GAG meeting]
· A 'what if' was proposed to the group: What if the entire marine shore.line was designated 'Urban
Conservancy'? Wouldn't it encourage protection and improvement of ecolog.ical connections
while still recognizing the residential land use? Discussion around this point included:
· Certain areas deserved to be highlighted as 'Natural';
· Land use and conditions in some areas would seem to indicate that 'Urban
Conservancy' would not be appropriate; and
· Different designations along the shoreline would perhaps be more useful to
City planners administering the SMP.
· A concern with creating differences in Environment Designation for high-bank and low-bank areas
- wouldn't a lan~owner who owned land up to the shoreline in a high-bank area expect the
same Environment Designation as a landowner who owned land up to the shoreline in a low-
bank area? How much weight should existing land use pattern be given in establishing
designations? Designating some residential areas 'Urban Conservancy' and some 'Shoreline
Residential' raises issues of fairness.
.0 A questioning of whether high-bank areas truly are of higher ecological function than other areas;
and
· A reiteration of the difficulty in agreeing on appropriate Environment Designations to the City's
shorelines without fully understanding the regulatory impacts (Le., what can and cannot be
done in each designation?). .
7. Next Steps
Isaac touched on the major topics highlighted in the Environment Designations discussion. He suggested
that a consensus had been reached regarding the lake shoreline designations (indicated on the map) as
a good starting point to work from in discussing policy and regulatory impacts. Regarding the marine
shoreline, Isaac suggested that two general approaches for Environment Designation were being
considered; one that broke the shoreline into many small designation sections, and one that more broadly
designated the majority of the marine shoreline. With the caveat that policies and regulations under each
designation needed to be understood, the group generally agreed.
Isaac indicated that the coming meeting would occur in late September and touched on what the major
topics of consideratiDn would be at the remaining CAC meetings. . Contact him by email for questions or
comments. The meeting adjourned at 9:4qpm.
Doc. J.D.
CITY OF ,~
Federal Way
City of Federal Way
Shoreline Master Program Update
Citizen Advisory Committee Meeting - October 4, 2006
Meeting Minutes
Attendees:
Chris Andersen
Hal Whidden
Chuck Gibson
Bill Baldwin
Linda EIsington
Gary Hering
Isaac Conlen, City of Federal Way
Greg Fewins, City of Federal Way
Don Robinett, City of Federal Way
Kent Hale, ESA Adolfson
Aaron Booy, ESA Adolfson
1. Introductions
The meeting began at 7:00pm. The group introduced themselves, as there were several new faces since
the August 30, 2006 meeting.
2. Review of AUQust 30. 2006 CAC meetinQ minutes
August 30, 2006 CAC meeting minutes had been distributed to the CAC for review prior to this meeting.
Several minor comments were made, and noted, after review of the minutes.
3. Review of Federal Way Shoreline Environment DesiQnations Memo
Kent gave an overview of the Memo (dated September 27,2006) that had been received by all CAC
participants before the October 4 meeting. Kent highlighted several elements of the Memo, including the
following:
. The inclusion of Ecology's new Management Policies for each shoreline environment designation
under consideration, noting that some of Ecology's Management Policies might not be
applicable to Federal Way;
Doc. J.D.
· The inclusion of Federal Way's existing Management Policies that might be appropriate and
applicable to one or more of the proposed shoreline environment designations; and
· The 'Permitted Uses' table described on Pg. 7 of the Memo and located on Pg. 8, noting that it
indicates what uses and modifications are allowed under existing shoreline environment
designations and what would be allowed under proposed shoreline environment
designations. This table was prepared in response to questions raised by the committee at
the previous meeting.
4. General discussion of Shoreline Environment DesiQnations: both in reQard to ExistinQ &
Proposed DesiQnations and the ManaQement Policies & Uses Memo
Comments and questions focused on the City's marine shoreline included: .
· What did the three colors along Federal Way shorelines indicate on the maps posted at the
beginning of the meeting [Kent described how the colors represented the proposed shoreline
environment designations, and described how - as discussed at the previous CAC - the
alternative designations shown on the two posted maps represented alternative strategies of
designation.] .
· A concern was raised with creating differences in Environment Designation for high-bank and
low-bank areas that are both zoned as residential - wouldn't a landowner who owned land up
to the shoreline in a high-bank area expect the same Environment Designation as a
landowner who owned land up to the shor~line in a low-bank area?
· . Suggestion made that residential development would be allowed under both
Urban Conservancy and Shoreline Residential designations, and that instead of
describing Urban Conservancy as more restrictive to residential development, it
would be better be described as leading to 'more careful review' of development
proposals.
· Another point of view: there are major differences between the proposed
designations that would lead to very different management policies and
allowable uses. Question asked: Why and how does Urban Conservancy fit into
the Puget Sound Shoreline. [Response to this question came in the form of the
following comment, with additional response from Kent after the comment, as .
described below.]
· A comment was made suggesting that in previous conversations about how designations were to
be made for each shoreline reach, it was generally agreed that the decision would be based
off of the existing land use and ecological functions present at the shoreline reach. [Kent
elaborated upon this briefly, and generally agreed with the suggestion] The comment was
then further elaborated to suggest that existing environmental analysis (from WRIA 9) does
exist that highlights certain Puget Sound shoreline areas as having higher ecological function,
and this analysis would support a three-tiered system of shoreline environment designation
(including Natural, Urban Conservancy, and Shoreline Residential).
· A comment was made that what a shoreline homeowner would really be interested in would be
an understanding of what shoreline modifications and uses would be allowed. A bulkhead
was used as an example: Is a new bulkhead allowed? If so, what sort of bulkhead? [Kent
noted that these sorts of decisions are currently made based on regulations within the
Federal Way code, and that these regulations were developed with guidance documentation
from Ecology and other state agencies. He then noted that under all of the proposed
shoreline designations, Federal Way would still use the Federal Way code and refer to the
same guidance documentation in making decisions.]
· The topic was further discussed by the comment that under both Urban
Conservancy and Shoreline Residential designations, bulkheading would (or
could) be allowed - however 'more careful' review could be required under
Urban Conservancy than under Shoreline Residential.
· A comment that there is no one-to-one relationship between the management policies for each
shoreline environment designation. This makes it difficult to make any sort of comparison
between how each might be managed or regulated. Example us~d: Setbacks are addressed
Doc. J.D.
under certain designations, but not under others. Staff agreed and will reformat ma~agement
policies to follow a consistent structure.
· Are different setbacks and use requirements connected to different shoreline environment
designations? [Isaac responded that under current designations, minimum setback
requirements are typically the same, except that setbacks are larger in the 'Natural'
environment designation.
· Is there anyexplicitlanguage in Ecology guidance that says lake shorelines can be treated
"differently than marine shorelines? [Isaac responded that Ecology allows for differences to be
made at local levels in terms of regulations and restrictions.]
· A comment re-iterating that it is very difficult to make 'broad' environment designations when the
restrictions within each environment are unknown.
· Response to comment suggested that it is difficult to address regulatory details
for each designation because environmental review is done on a site-by-site
basiS.
· Isaac responded that there was a hope that some general assumptions could
be made based on the management policies for each shoreline designation -
with the main focus aimed at making shoreline designations both practical and
user friendly.
· A comment that the 'Purpose' statements (as taken from Ecology guidelines) for each shoreline
environment designation do highlight significant differences between each designation,
suggesting that there would also likely,be major differences in how development in each
designation would be restricted and reviewed by City planners.
· A comment suggesting that since the City will review all development, what is the purpose of
placing any sort of more restrictive designation? Wouldn't environmental concerns be
addressed with or without different designations?
· Response suggested that by placing more detaileq designations over the
shorelines, it would provide a filter to assist City planners in their review of
shoreline proposals.
· Greg commented that the designations would also provide a filter (guidance) to
developers when they are considering what could and couldn't be done with a
shoreline area.
· So who draws the lines that determine what areas receive what shoreline environment
designation?
· Response suggested that WRIA 9 environmental analysis could be used to
determine areas with greater ecological function
· . Kent, at this point, reviewed the thinking and criteria that had been used to
determine how to designate areas Shoreline Residential, Urban Conservancy, or
Natural (i.e., by looking at the level of development and the ecological function of
any given shoreline area).
· A comment was made suggesting to consider designating some of the initially proposed Natural
shoreline areas as Urban Conservancy, while still maintaining high value areas, as noted by
WRIA 9, as Natural.
· A comment was made that if distinct designations are to be made in certain areas along the
marine shoreline, then documented scientific findings need to support those distinctions.
· A comment made that it would be useful to see examples of ecologically friendly or 'mimicking'
shoreline protection strategies actually in practice. [Kent and others suggested some
examples, however additional examples with more detail might still be useful.]
· A concern rose that in Urban Conservancy areas, repairs to existing bulkheads might not be
allowed - and that this would create serious concerns with landowners in these areas. [Isaac
responded that repair would likely be allowed, and that only a full. bulkhead replacement
could require the use of a different type of bulkhead. Kent noted that the existing regulations
and policies establish a preference for alternative bulkhead "softshore" designs and that
reviewing a proposal for a full replacement (not a repair) might require that a landowner
consider these designs first and demonstrate .why it would not work.]
Doc. J.D.
At this point, Isaac suggested that the CAC should focus on commen!s and questions applicable to
lake shorelines. Comments and questions focused on the City's lake shorelines included:
· What does 'no net loss of ecological function' really mean? If taken literally, it seems to suggest
that no residential develqpment would be allowed within shoreline areas. If most of the lakes
are designated "Shoreline Residential", then ho'w could you have both? [Staff agreed that the
'no net loss' language contained in the state guidelines raises some questions with regard to
whether this is achievable given that residential and other uses are expected to occur. Kent
described how mitigation is frequently used to compensate for development activities... that
opportunities to mitigate (habitat creation, improvement, and enhancement) are used to
maintain 'no net loss'.}
· A comment suggesting that there is very little natural function provided by the lakes in Federal
Way; they do not provide salmon or native habitat and in reality are largely serving human
purposes.
· A question regarding the flexibility of the management policy language for the Shoreline
Residential designation: the policies do not se~m to be reflective of a balance between
human and natural uses that the City should consider in areas designated Shoreline
Residential. [Kent responded that the language is from Ecology and reflects the criteria they
will use to review the City's SMP, however that there is flexibility in what the City can do.}
There were several general comments asking for clarification on information included in the Management
Policies & Permitted Uses Memo. These comments included the following:
· A comment regarding the difference between impacts to ecological function as stated under the
Natural Environment and Urban Conservancy designation - what are the differences
between 'no significant impact' and 'no net impact'? [Kent suggested that in a Natural
designation, no significant impacts should be allowed, with or without mitigation; while in
other areas with more allowed uses (such as Urban Conservancy) you could have. uses that
may have impacts but they would be mitigate.d and thus have 'no net impact. 1
· A desire for clarification as to why Commercial/Office development would be allowed With Urban
Conservancy areas but not in Shoreline Residential areas. [Kent responded that Shoreline
Residential areas really are limited to residential development, whereas Urban Conservancy
areas allow for a variety of development uses as long as ecohgical function is maintained.}
.. A desire for clarification regarding the difference between a Substantial Development Permit and
a Conditional Use Permit. [Kent and Isaac responded: A Substantial Development Permit is
required when a project reaches a threshold monetary amount (currently $5,000) and
involves City review and approval, whereas a Conditional Use Permit is for large scale
projects that may have significant impacts (ecological, compatibility) and requires review and
approval by both the City and Ecology.} .
· A comment asking for clarification regarding the Aquatic designation. [Isaac described how Kent
and him had discussed this designation and its use, and whether or not it would be applicable
to Federal Way. Isaac indicated that there was still some confusion regarding the Aquatic
designation and further clarification would be sought from Ecology.}
5. Next Steps
Isaac touched on the major topics highlighted in the evening's discussion. He indicated staff would make
the Management Policies structurally uniform across all shoreline environment designations per CAC
request. He indicated that discussion of environment designations had been good. He noted that full
consensus may not be possible, however, and it's important that we move on to our next task at our next
meeting.
Isaac indicated that the coming meeting would occur in late October or early to mid November and
touched on what the major .topics of consideration would be at the two remaining CAC meetings (goals
and policies and restoration planning). Contact him by em ail for questions or comments. The meeting
adjourned at 9:00 PM;
Doc. J.D.
~
CITYOF , ~
Federal Way
City of Federal Way
Shoreline Master Program Update
Citizen Advisory Committee Meeting - November 15, 2006
Meeting Minutes
Attendees:
Chris Andersen
Chuck Gibson
Linda Elsington
Gary Hering
Peggy McKasy
Joleen Latham
Mike McKasy
Isaac Conlen, City of Federal Way
Sandra Lange, Washington Dept. of Ecology
Teresa Vanderburg, ESA Adolfson
Kent Hale, ESA Adolfson
1. Review of October 4th, 2006 CAC meetina minutes
The meeting began at 7:05pm. The group introduced themselves, as there were some new citizens since
the October meeting. Several residents from Dumas Bay area were in attendance at this meeting.
Meeting minutes from the October 4th CAC meeting were distributed in the packet of materials prior to this
meeting. Several minor comments were made, and noted, after review of the minutes.
Sandra Lange asked about the "high bank" versus "low bank!' development requirements - these should
be different. Kent explained that we had discussed the landslide hazard issues in the last meeting.
2. Overview of Shoreline Master Proaram update process ..
Doc. J.D.
Teresa gave an overview of the City's SMP update process and where we are in the process. We
submitted the Draft Shoreline Inventory & Characterization report to Ecology for review on August 1, 2006
but have not received comments to date from Ecology. We did receive comments from our Technical
Advisory Committee (TAC), specifically from our WRIA 9 representative and King County. A citizen
comment was made that the previous inventory done on North Lake in 1998 was badly done. This raised
a lot of discussion among North Lake residents.
The Draft Goals and Policies (including environment designations) and Restoration Plan are due to
Ecology on December 15, 2006. The draft goals and policies, along with environment designations, will
be discussed tonight with the CAC. The Draft restoration plan has been prepared and is in City review.
The next CAC meeting will focus on the restoration plan. Chris asked if the next CAC meeting would be
in early December prior to the Dec. 15th deadline. Isaac said yes he would schedule this soon.
In early 2007, we will be introducing the City Council and LUTC to the components of the SMP update.
To meet our grant deadline, we must have the SMP work completed by June 2007.
3. Review of SMP Update - Goals.& Policies Memorandum
Kent gave an overview of the Goals & Policies Memo (dated October 26, 2006) that had been received by
all CAC participants before the November meeting. Kent walked through the general and specific
recommendations outlined in the memo. In general, we have reorganized chapters in the Goals &
Policies, removed redundancies, and added new policy statements required by the shoreline guidelines.
Kent noted that the big themes to focus on include the following:
1. Shoreline use element: longest section of the Goals & Policies
2. Public access and recreation: combined these because the policies are similar
3. Shoreline environment designations and policies: revised to meet guidelines
Mike asked about shoreline regulations - will these then follow our discussion of goals & policies. Kent
answered yes, but we are already touching on those, for example we have already talked about piers and
requirements for those in general.
4. General discussion of Shoreline Goals & Policies - Existina and Proposed
Comments and questions focused on the City's marine shoreline included:
· A discussion began about the aquatic areas and use of an Aquatic Environment
Designation.
Mike asked specifically about lots that are plotted out to the old government line, well below the OHWM of
Puget Sound. This is for Dumas Bay where the ownership extends up to 600 feet out into the sound.
Kent said, yes, we will be regulatIng those areas to the extent of the City's jurisdiction. Mike said a
neighbor wanted to fence his property even below the tide line, which he could see would be problematic.
Kent assured everyone that the regulations will still.apply waterward of the OHWM and goals & policies
will apply everywhere in the City, even if an Aquatic Environment Designation is not used. . .
A discussion as to the uses for an Aquatic Environment designation occurred. One person asked if there
are uses that would only occur in that environment, waterward of the OHWM. Sandra Lange referred
everyone to the WAC definition for the Aquatic Environment areas.
· Comments on the Proposed Goals & Policy Language- Shoreline Use Element and Public
Access I Recreation
A request for comments from Isaac initiated the group's review of the goals & policies.
Doc. J.D.
On SMP Policy (SMPP) 8, Chris requested that the policy (b) be rephrased to clarify.. A$ iUs now, it is
open to interpretation. Chris's point is that some structures can be safely built in landslide hazard zones,
and if they don't result in a no net loss of shoreline function.
On SMPP 12, Chris as~ed how this policy relates to zoning issue. Shouldn't densities be established
according to zoning requirements? It was confirmed that densities are in fact controlled by the underlying
zoning.
On SMPP30, a discussion of shoreline armoring occurred. Will new hard bulkheads be allowed at all?
Yes, but only after considering other options with less impact like different soft shore alternatives and site
designs. Gary noted that SMPP11 c is similar in intent. .
On Goal SMPG5, a long discussion among th~ citizen occurred regarding the wording of that goal. Mike
noted that the wording almost discourages safe use of a property since shoreline protection must be
limited. Kent explains that the goal for new development is to first look at site configuration. Need to ask
"Can you develop safely without requiring the need for a bulkhead?" Look for alternatives to hard
structures. Mike suggested rewording the Goal to focus on the positive - as in to "encourage soft shore
armoring over hard bulkheads." Mike suggests.that Goal SMPG5 needs to be more flexible and
reworded to accommodate the possible redevelopment of bulkheads. Chris voiced similar concerns with
this language. .
The group asked if it was true that new development could not use hard bulkheads. Isaac said yes, you
must come up with alternative site designs. One possible exception would be for properties that are
constrained to the degree that you cannot develop without a bulkhead.
Mike asked about what actions would be considered "new development". If you removed an existing
house to rebuild? No, that is considered "redevelopment" not new. How does the City's SMP work with
the Hydraulic Project Approval (HPA) requirements from the state Department of Fish and Wildlife? Kent
said that the HPA is primarily fish related, whereas the SMP deals with broader issues.
Sandra reiterated that new development in the shoreline needs to consider construction in a way that
doesn't require hard bulkheads. The new shoreline guidelines require this consideration. Sandra
recommends that property owners consider structure setbacks and structure footprint before hard
bulkheads.
Kent suggests that we will reword. both SMPG5 and SMPP30. Gary wants us to make sure that it follows
the new shoreline guidance. It has to be approved by Ecology, so has to be consistent. Chuck said yes
to revising the goal and policy above, we need to recognize that there are certain situations where new
hard bulkheads may be warranted.
Sandra said the confusion lies in use of "shoreline protection" in the goal. This is a misnomer and should
use "shoreline armoring" instead to be clear. Chuck asks what is soft shore armoring anyway? Kent
explains it is the use of logs, vegetation, natural materials to achieve shoreline protection instead of
concrete bulkheads. Seahurst Park in Des Moines is an example of this. Sandra mentioned that
concrete bulkheads get a "bad rap" because they often stick out too far into the OHWM.
How does the state look at beach nourishment projects? Would these be allowed? Can you add a beach
to your property? Yes, Seahurst Park is an example where beach nourishment was allowed to improve
shoreline functions. .
Kent mentioned that Conservation and Restoration elements of the SMP will be discussed during the
restoration planning meeting. The goals and policies will be included in the Restoration plan.
Dqc. J.D.
· Comments on the Shoreline Environments & ManaQement Policies
Kent introduced the shoreline environments that have been selected by the City and CAC:
· Shoreline Residential
· Urban Conservancy
· Natural
Then he explained that the management policies. are set up with three separate parts: 1) type of use, 2)
development standards and setbacks, and 3) different policies per each shoreline environment type.
Sandra asked on p. 20, under management policies for Shoreline Residential, "why aren't supporting.
uses allowed in the shoreline zone, like commercial development. Why is it limited to only water-oriented
uses?" She asked if this was verbatim from the WAC. .
Chuck asked so this means you can't put a Starbucks in the shoreline jurisdiction in ~horeline Residential
zones. Isaac said very few commercial uses are allowed in shoreline areas due to the primarily
residential zoning associated with these areas, however, we can look at that policy and see if we want to
make a change there to allow non water-oriented uses. It may be too restrictive as it is written,
Chris notes that the management policies point to the standards but don't provide setbacks. Setbacks
may be different in each environment designation, and will be in the shoreline regulations. Kent says yes.
Isaac mentions that the requirement of the shoreline guidelines is for "no net IDSS" so we are striving to
meet this test. A discussion followed of how to meet the no net loss standard. Chuck voiced the concern
that every bit of the shoreline has some type of function. Concern regarding overly discretionary
regulatory language was voiced. Isaac said that when we put together the regulations, we'll make sure
that the language isn't too discretionary. Sandra said that the City needs to rely on its inventory to set the
baseline for shoreline conditions.
5. Shoreline Environment DesiQnations - Summary of Results
Kent refers to a GIS map of the City with the proposed shoreline environment designations displayed,
Based upon feedback from earlier CAC meetings, the environment designations were discussed. The
freshwater lakes are designated either Shoreline Residential (SR) or Urban Conservancy (UC). The
Puget Sound coast is designated Natural, SR and UC. SR is proposed in developed areas with low
banks. UC is proposed in residential areas with high bank coastal bluffs (feeder bluffs) and within Dumas
Bay and generally in more environmentally sensitive areas. Natural areas include portions of Dash Point
State Park and other undeveloped park lands.
Chuck suggested that we might need to consider a Natural designation along part of North Lake. There
are areas along North Lake that are basically undisturbed which meet Natural definition. It was noted that
the Natural designation may not have been considered in this area due to inconsistencies with the
underlying office pa.rk zoning. .
Mike noted that most of Dumas Bay is proposed to be Urban Conservancy. He recognizes this
designation will be more restrictive for development. This will put the focus on restoration in those areas,
while still allowing residential development. Peggy noted that this designation will give Dumas Bay
residents more clout for restoration actions. It was noted that the "no net loss" requirement is applicable
to all three environment designations under consideration.
Residents noted that there is a problem with odor in Dumas Bay from decaying seaweed. They are
. worried that this is impacting bay health, affecting eelgrass habitat. The residents have a meeting set up
on November 2ih with Ecology and other agencies to find a solution to problems in the bay. The odor
Doc. J.D.
was th.e worst this year of the past several years. Could be an issue related to Lakehaven Sewer outfall,
septic tanks, or stormwater runoff. Mike is hoping Ecology will fund a baseline study of the Bay.
6. Next Steps
Isaac touched on the major topics highlighted in the evening's discussion. He said that he will be s~tting
up the next meeting for sometime in early December to discuss restoration planning. Contact him by
email for questions or comments. The meeting adjourned at 9:20 PM.
Doc. J.D. .
.~
CITY OF ~
Federal Way
City of Federal Way
.Shoreline Master Program Update
Citizen Advisory Committee Meeting - December 6, 2006
Meeting Minutes
Attendees:
Chuck Gibson
Gary Hering
Peggy McKasy
Mike McKasy
Joleen Latham
Bill Baldwin .
Isaac Conlen, City of Federal Way
. Greg Fewins, City of Federal Way
Don Robinett, City of Federal Way
Andrea Maclennan, Coastal Geologic Services
Teresa Vanderburg, ESA Adolfson
1. Review of November 15, 2006 CAC meetinQ minutes
Reviewed the November 15 CAC meeting minutes and agreed on content.
2. Draft Shoreline Restoration Plan
Teresa introduced the Restoration Plan and des~ribed the contents. She walked the group through the
elements of the report, and the requirements for restoration planning under the new shqreline guidelines.
CAC members reviewed the Draft Restoration Plan and the GIS drawings for the marine shoreline,
indicating where restoration opportunities exist as identified by the Water Resource Inventory Area
(WRIA) planning efforts.
Mike McKasy asked whether Dumas Bay's seaweed would be considered a noxious weed. If that was
the case, he wondered if Dumas Bay would fall under that portion of the restoration goals and policies
(Dumas Bay Restoration/Enhancement Opportunities - invasive species removal?). Mike also pointed
out that a tidal lands policy goal to restore degraded shorelines is needed. Chuck asked whether this was
something to be pur.sued by the City, or if private property owners should take the lead. The group
Doc. J.D.
discussed the environmental. issues at Dltmas Bay, and since the cause of the odors problems is not yet
clearly identified, we decided it warranted further study. Not likely that the kelp in the Bay would be
considered an invasive species.
Bill asked several general questions on the overall program, wondering whether Federal Way's SMP
development would have to coordinate its actions with regional entities. He wondered what might happen
if the working group, a small part of the big picture, came up with goals that were in conflict with the larger
program. Which would .be a higher priority - Federal Way's alternatives or the larger WRIA group's
alternatives? As an example, Bill pointed to the case of feeder bluffs blocked by bulkheads. In this
situation, the WRIA group deals with conflict such as this. Don suggested that different priorities might
come into play at the local leveL The City wants to contribute to the restoration opportunities identified at
the WRIA leveL .
Don turned discussion to the Lake Management District. Aquatic weed management programs were
established for the specific purpose of aquatic weed management in North Lake and Steel Lake.
Although the restoration plan calls for possible expansion of these programs that would not really be
possible, according to Don, based upon the way they are set up. He suggested the possibility of Council
funding for that purpose, obtained through 1) raising taxes; 2) CIP City donation; and/or 3) raising utility
fees. Isaac proposed looking into grants as a means of funding future restoration programs. Bill, in turn,
asked Isaac if citizens interested in a specific lake restoration project could approach the City, and Isaac
said that yes, they could. Supporting Isaac's point, one citizen pointed out that lakes benefit all the public.
Peggy noted a Site-Specific Restoration Goal on page 18 of the Draft Restoration Plan: the goal seems to
address restoration of tributary mouths only, rather than the entirety of Dumas Bay. Don responded that
most scientists agree the Bay is a pocket estuary, and we are focusing on the bay. Dumas Bay itself is
considered high value habitat. The City has done a lot of past restoration projects on the streams and
stream mouths.
Andrea was asked to describe how Coastal Geologic Services did their evaluation of the marine shoreline
in Federal Way for the WRIA group work. She said that the evaluation was based upon information that's
been collected through walking surveys onshore. Evaluation included looking at geomorphological
processes, sediment sources, sediment transport ZOnes, and modified shorelines (looked at, not
mapped). About 90 percent of our natural sediment sources in marine areas are from eroding bluffs.
These surveys indicate high value conservation bluffs in the area, as they are the .Ieast changed from
historical condition.
The group continued the discussion on Dumas Bay, wondering what impact restoration planning would
have on homeowners. Don pointed out that restoration is opportunity driven, and also that feasibility
studies are needed to verify these restoration projects. Gary proposed that the process of erosion is
normal and that the balance of property owners need it to occur (to maintain beaches, etc.). Sediment
transport also provides support for ecosystems, he said, and people need to walk the beach to discover
that. Adding to the discussion, Mike referred to page 21 of the Draft Restoration Plan and proposed that
property owners at the base of feeder bluffs in Dumas Bay be notified that their homes have been
identified for removaL Isaac and Don both pointed out that none of the restoration projects would be
undertaken without feasibility studies and the permission of landowners. Restoration in this context is
entirely voluntary. There was discussion about the appropriateness of including the restoration projects
calling for removal of homes given the low likelihood of implementation and the political sensitivity.
Bill raised a general question about implementing the Restoration Plan, pointing out that 95% of the Draft
Plan focuses on Puget Sound and Dumas Bay. He was worried that not as much is known about lakes,
and no lake restoration projects have been identified. Bill wanted to go on the record stating that the
group needed more information on lakes. Chuck stated that King County did a survey of all lakes 4 years
ago. Chuck suggested that Department of Ecology Lakes Program funding could be pursued, and
Peggy asked. what the best place to apply that funding might be. Speculating on other funding sources,
Don stated that the Salmon Recovery Funding Board won't fund urban stream restoration and Mike
Doc. J.D.
wondered who is funding the stream restoration on the golf course. The suggestion was made to add
lake restoration projects to the conclusion statement in the Draft Restoration Plan.
Isaac then gave an overview of the SMP timeline. We will start legislative process in February of 2007
with Planning Commission, which is expected to take a month to a month and a half to review the
proposed SMP. LUTC will then review the SMP and make a recommendation in March, and the.
document will go to the full Council in late April. The final SMP will be effective in fall of 2007, subject to
Department of Ecology review. Isaacwill notify the CAC during Planning Commission review.
One member asked whether it was true that they'd be voting on annexation in 2007. It was suggested
that annexation was a long process, but that it was a state goal advocated by the City Council, King
County, and a majority (50%) of voters. Yes, annexation is slated to be discussed this year.
Doc. J.D.