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15-104794DEPARTMENT OF COMMUNITY DEVELOPMENT 33325 8'h Avenue South CITY OF Federal Way, WA 98003-6325 253-835-2607:Fax 253-835-2609 FederalWay www.ciwoffcderalway.com APPLICATION CRITICAL AREA DIRECT SERVICES PROGRAM Project Name: Gethsemane Cemetery Phased Master Plan Project Description: The Archdiocese of Seattle is undertaking a long range planning effort for Gethsemane Cemetery in Federal Way, WA with the goal of achieving long-term development approval from the City of Federal Way through its Use Process IV/Hearing Examiner application. We seek to contract with a Critical Area Specialist to fulfill requirements of the application: • wetland delineation • stream delineation ■ wetland assessment and categorization • stream categorization Please submit a proposal for all wetlands and streams on the site. Divide your proposal into a base service (working from the center line of Hylebos Creek to the west property boundary) and an optional service (from the center line of Hylebos Creek to the east property boundary). We've attached a site map that highlights the expected critical areas as well as a draft scope. Project Address: 37600 Pac Hwy S, Federal Way 98003 Parcel#: 322104-9025, -9020, -4560, -4365, -4281 Contact Name: Mr. Richard Peterson, Director of Cemeteries, Archdiocese of Seattle Phone: (206) 522-0996 Email: richp@mycatholiccemetery.org Mailing Address: n/a (same as above) I am the owner of the above referenced property and I authorize the city to obtain an estimate of project cost. I recognize the Direct Services Program is optional and that I may choose to utilize any qualified consultant of my choosing. I agree to indemnify and rjdeasehe city m all liability associated with the program or the work/reports of the consultant. Signature: Date: 404", C Consultant Name: Date Sent to Consultant: Materials Sent to Consultant: ❑ Site Plan ❑ Special Study(s) ❑ Other: City Use Only ❑ Landscape Plan ❑ Other: Folder # Fee Estimate: ❑ Construction Drawings Bulletin #078 — June 1, 2014 Page 1 of 1 k:\Handouts\Critical Areas Optional Direct Services Application Z o W U) 5� L 0 W U) ^_ I..L 1 W W 2 W CU W Z W U) E— /W Q J LU Cl) I Z LU Lli LLJ NQ 0^ CL LLI J 0 LU LL LL O U �1 ddV-3Nd lVM IVaACEI , s ONISVHd H11M _ =Comm g NVId 631SVW 3ONVb ONOI _ J AH313HAO 3NVVGSH130 H3AOO NVId 31lS - e ai33fo8d 3UII � w zo 00 �3 =� �Noo 0 p y o p o W <N ❑�_� LL w3�u a f c o y "a' z o o_ o o a _ Z - ri a H i i w ° �QII F 3NgF Z a� z G o�i avi a i oozS� U z' Lu LU I I I II W coi3o m z Wu C in asaaa o J J I I I j I O o _ a�wg - - < o Nw$¢ FU zw owo co yw oo �a<rc u w- °m 3z uN�sizia o - zo - a o a - _w 00 LU o - - o ,<e w M° a� z� ° a Er ddV'� lVM 1V2i343d I)NISVHd H11M NVId 831SVW DON" ONO-1 AIAM AO 3NVW3SH13EJ 103ro8d g_ 49 NVId 311S :31111 o J 1 the •�fy �S� 3¢ln i •\ fV Fo�`o:ILLoaiow o_-< o�zo� aw y V U UV oF� �m iOtFoo� �amo�z �o mu-zpmzm S 33 aM .. oaa' o>o > w " o3N�ra i am�w�e �m m o� mar oHo • i w- .EW o9T� �u 3aai�LLm�m Nmm=a �aww> _ om ATTACHMENT C PROPOSED SCOPE OF SERVICES WETLAND DETERMINATION DRAFT SCOPE PROJECT STATUS AND UNDERSTANDING The Archdiocese of Seattle is undertaking a long range planning effort for Gethsemane Cemetery in Federal Way, Washington with the goal of achieving long-term master plan development approval from the City of Federal Way through its Process IV land use application. The Cemetery Master Plan is intended to guide cemetery development in several phases over the next 50 years, and is focused on planning the area of the property to the west of Hylebos Creek. The phased construction approach is necessitated by numerous practical, local, functional and ethical considerations. Planning a cemetery through phases, as is being done here, allows the cemetery to focus its development efforts and funds efficiently and effectively over the long term lifespan of the cemetery. See Attachment D. PROJECT STATUS AND UNDERSTANDING Two reviews of wetland boundaries have been performed at the Gethsemane Cemetery property to date: 1) Wetlands in the North Arm were delineated in 2005 by Anchor Environmental. The City of Federal Way concurred with their findings. 2) Wetlands in the adjacent northeast property were enhanced and delineated by Sound Transit in 2003. Because the recent wetland delineations occurred more than 10 years ago, all reports and boundaries may need to be updated for this application process. PROPOSED SCOPE OF SERVICES Task 1: Review Background Information Task 1 includes a review of existing documentation for the property. The review will include the following: ■ King County Soils Maps; • Previous wetland determinations and site investigations; • Site specific hydrologic monitoring data; and • Federal, State, and local permitting requirements. Task 2: Wetland Determination Site Investigation After reviewing existing documents, CONSULTANT will conduct one site visit for the purpose of conducting wetland delineation in accordance with City of Federal Way and US Army Corps of Engineers (USACE) regulatory requirements. CONSULTANT will conduct the wetland delineation using the Routine Determination Method described in the Corps of Engineers Wetland Delineation Manual and Washington State Wetlands Identification and Delineation Manual. Proposal to Prepare Wetland Determination Report Page 1 of 3 ATTACHMENT C During the site investigation, CONSULTANT will collect data at data plot locations that are representative of the on -site wetlands and uplands. CONSULTANT will flag the data plot locations and the on -site wetlands at approximately 50-foot intervals (depending on the complexity of the wetland and stream and degree of detail required). The flags will be numbered consecutively. CONSULTANT will complete a sketch map showing the approximate location of each flag for use by land surveyors. Please note: This proposal assumes that the Client will provide all survey services for the wetland determination map. Task 3: Prepare Wetland Determination Report The information collected during Tasks 1 and 2 will be documented in a wetland report. The report will include: • Brief description of on -site wetlands; • Wetland classification per new WDOE guidelines and category; • Brief functional assessment • Wetland boundary map (survey of wetland boundary to be provided by the Client); • Potential mitigation opportunities on -site; • Regulatory requirements and permitting implications; • Site photographs; and • Data sheets. CONSULTANT will submit the report to the Client for use in implementing the new Master Plan for the park and to include in permit application packages. Task 4: Client and Agency Coordination Task 4 includes coordination with the Client throughout completion of the project. One on -site meeting is included in this task to meet with the Client and/or project engineer to present the results of the wetland determination. If requested by the Client, the CONSULTANT will also attend any additional meetings to discuss the Gethsemane Cemetery Master Plan in relation to any identified wetland areas and the stream corridor. Task 5: Project Management Task 5 entails administrative tasks such as contracting and invoicing for the project through closure of the project. Expenses Expenses include reproduction of project documents, postage, mileage, and similar project associated expenses. FEES AND SCHEDULE Project cost and schedule are a concern for the Client. We can work together to establish a proposal that is better tailored to your situation, as needed. Proposal to Prepare Wetland Determination Report Page 2 of 3 ATTACHMENT C ESTIMATE SCHEDULE FOR SCOPE OF SERVICES Task Task 1. Review Background Information October 2015 Task 2. Wetland Site Investigation October 2015 Task 3. Wetland and Stream Determination Report October 2015 Task 4. Client and Agency Coordination On -going Task 5. Project Management On -going Proposal to Prepare Wetland Determination Report Page 3 of 3 ATTACHMENT D GETHSEMANE CEMETERY PHASED MASTER PLAN JUSTIFICATION FOR LONG TERM VESTING Gethsemane Catholic Cemetery, opened in 1975, continues the Catholic Church's multi -millennia ministry of burial of the dead, prayer for the dead, and consolation of the grieving, three of the six Corporal Works of Mercy practiced by the Roman Catholic Church and its members. The Catholic cemetery is one of the oldest publicly recognized ministries of the Church dating back to Fossores (a clerical role) of Rome who were responsible for burying the dead and building and maintaining the catacombs in which the early Christians were buried.' The Canon Law of the Catholic Church states that there are two sacred places, the church building specifically designated for divine worship and the Catholic cemetery. "Sacred places are those which are designated for divine worship or for the burial of the faithful by a dedication or a blessing which the liturgical books prescribe for this purpose."2 The Catholic Cemetery provides a place of burial and dignified memorialization of the deceased in keeping with the documents of the Catholic Church.3 In a broader sense, the Catholic cemetery witnesses the Gospel, provides a place of prayer, catechizes the Catholic belief in resurrection, affirms the dignity of human life, assists the poor, and brings together a number of.elements of the Catholic Church's pastoral mission. Fundamentally, Gethsemane Cemetery exists to affirm this mission today and for future generations yet unborn. In order for Gethsemane Cemetery to continue to serve its sacred mission through this century and beyond, the 50 year phased development articulated in the Cemetery Master Plan is essential to the development of the cemetery given funding constraints under which cemeteries must operate due to their long-term legal, financial and ethical obligations to their patrons and the community as a whole. The long-term phased construction approach in the Gethsemane Master Plan, typical of cemeteries, reflects the relationship between limited available funding and the need for not only long-term planning to accommodate additional burials, but also for the continued protection and maintenance of current burial sites. Given the long-term presence of the cemetery and its services, the cemetery depends on a long-term care fund to ensure it continues to operate long after it reaches capacity. Long-term care funds are required by legal, sound financial management and ethical considerations. The main source of revenue for the long-term fund is the individual sales of burial plots where a portion of the revenue is deposited into the long-term care fund. Given the limited provisions of this fund and the extensive costs of protecting and maintaining the facility, great care is taken to use the fund in the most efficient manner possible. For this reason, it is essential that Gethsemane develop in phases so that it is not forced to expend its entire care fund to develop its large property all at once, when not all of the grounds would be used for burials or to replenish ' The Catholic Cemetery —A Vision for the Millennium, National Catholic Cemetery Conference, Des Plaines, I1, 1997, p. 15, §12. 2 The Code of Canon Law promulgated at the Vatican for the Universal Catholic Church, § 1205. 3 The Order of Christian Funerals, approved for use by the Vatican and the National Conference of Catholic Bishops, Catholic Book Publishing Corp, NJ, 1989, p. 392, §417. 4 The Catholic Cemetery —A Vision for the Millennium, pp. 12 — 14. Gethsemane Cemetery Phased Master Plan Justification for Long Term Vesting Page 1 of 2 ATTACHMENT D the care fund and properly maintain the facility. The continued operation of the cemetery depends on the thoughtful use of the care fund over time and only as needed. Under these legal, financial and ethical circumstances, the cemetery must have long-term certainty about the regulations that will govern its phased development. Thus, the Master Plan must vest to current regulations for a very long period of time to ensure that the Master Plan and the operation, planning, construction and maintenance are consistent with the legal, financial and ethical considerations detailed above. The 50 year phased development is required and warranted to ensure the cemetery may appropriately plan today for its future development. Authorizing the phased development of this project will enable Gethsemane to build the appropriate infrastructure to accommodate future development. It is essential to large projects of this nature to obtain a high degree of certainty with respect to structural requi>ements that will require connections to future expansions, such as direct physical connections, irrigation systems, drainage systems, drives, etc. For this purpose, there must be great certainty with respect to property constraints and applicable regulations, such as boundaries and buffers of critical areas, limitations on uses of critical areas, as well as engineering requirements such as dimensions and other provisions relating to drives. Cemeteries must be carefully planned in all phases to minimize the "carry distance" and to provide maximum accessibility for families and visitors, especially the older, less mobile who are most typical cemetery visitors. The development of early phases must be based on informed decisions and certainty of regulations so as to best allocate resources and efficiently plan for future development. Any uncertainty in these matters will result in a misuse of very fixed resources and will result in poorly executed development. For all of these reasons, it is imperative that Gethsemane develop pursuant to at least a 50 year phased master plan that is vested to current regulations. Gethsemane Cemetery Phased Master Plan Justification for Long Term Vesting Page 2 of 2 Stacey Welsh From: Sent: To: Cc: Subject: Attachments: Importance: Kevin, John Hempelmann <JHempel man n@Cairncross.com> Tuesday, November 03, 2015 12:21 PM Kevin O'Brien (kevin.obrien@otak.com) Stacey Welsh; Peterson Richard (richp@mycatholiccemetery.org); Jim Brennan Oim@jabrennan.com); Carol Ohlfs (Carol@jabrennan.com); Nicole De Leon; Midori Dillon; Fred Morley (FredM@mycatholiccemetery.org) Contract for Gethsemane Cemetery MX-M 503 N_20151103_111305. pdf High Attached is the Otak Contract signed by the Archdiocese. You are authorized to proceed. Please confirm you will start this week as planned so we can coordinate later this month with the surveyors. John CH& I John Hempelmann Attorney Cairncross & Hempelmann 524 Second Avenue I Suite 500 1 Seattle, WA 98104-2323 d:206-254-4400 I Bio This email message may contain confidential and privileged information. Any unauthorized use is prohibited. If you are not the intended recipient, please contact the sender by reply email and destroy all copies of the original message Please be advised that if you use a public or employer -provided computer or workplace device or system, then there is a risk that your email correspondence may be disclosed to your employer or other third party. 1 CONSULTANT AGREEMENT CORPORATION OF THE CATHOLIC ARCHBISHOP OF SEATTLE OFFICE. OF PROPERTY AND CONSTRUCTION SERVICES This AGREEMENT is made this date of, Novembor 2, 2015 B.�TWEEN the Owner: Corporation of the Catholic Archbishop of Seattle, a Corporation Sole. ("Archdiocese of Seattla") 710 9"' Ave. Seattle, WA 98104 w i and he Consultant: Otalr,'lno, j h I he following Project: Wetiand definoatlon and report for Gethsemane Cemeteryin Federal Way, Washington (subject property pn cal numbers 322104-9025 and 322104-9020). The Owner and Consultant agree as follows. ARTICLE 1 CONSULTANT'S RESPONSIBILITIES Tltd Consultant shall provide Consultant services for the project as defined in Attachment (A). Services shall be performed in a manner consistent witli professional skill and care. ARTICLE 2 OWNER'S RESPONSIBILITIES The Owner shall provide Information reVested by the Consultant in order to fulfill project requir ift6nts, The Owner's designated representative is the Director Property and Construction ,Services for the Archdiocese of Seattle. The Owner may change the designated repmaentative at any time upon written notice to the Consultant. Th4 Parish designated representative Is Richard Peterson,206-524-1451, richp()myeatholiecometeryiorg. AXTICLE 3 OWNERS[ -TIP OF )DOCUMENTS Owiiersbip of any reports, data, surveys, charts, maps, drawings, specifications, memoranda, and any other documents which are doveloped, compiled, or produced as a result of this Agreement, whether or not completed, slialf be co -owned by the Consultant and the Owner, Any reuso of tht=sc materials by the Owner for projects or purposes other than those which fall within the scope of this Contract at the project to which it relates, witboui written permission by the Consultant, will beat the sole risk of the Owner. Tlta Owner acknowledges the Consulta.nt]Consultanes plans and specifications as instuint-nis of professional service. Ulxm completion of the.Agreem.ent, the documents may be used without compensation to the Consultant for future additions, renovations, or modifications. if use$, the Owner agrees to hold harmloss and indemnifjr the Consultant against all claims made against the Consultant for damage or [Witty. including defense costs, arising nut of any rouse of such plans and specifications by any third party without written authorization of the Costsultam. I used, any reference to Ilia Consultant shall be mmovesd born such documents, including but not Iimited to, Consultant coals oft° gistraion, Grin identifientlon and other such rofcrenecs. ARTICLE 4 TERMI.NATION, SUSPENSION OR A13ANDONMYNT Tither the Consultant or the Owner may terminate this Agreement after giving no less than seven days' written notice if the other party substantially fails to perl'brm in accordance with the terms of this Agtwtnent, AI1T[CLE 5 INSURANCE REQUIREMENT'S 5,1;Commereial General Liability. Consultant shall, at its sole cost and expense, secure and maintain an oecurrenee-based commercial genlIral liability insurance policy, with a limit of not less than $1,000,000, combined single limit, on all Services performed by Consultant under this agreement to protect Consultant and Owner, its directors, :agents, employees, successors, and assigns farm and against any and all claims, losses, harm, costs liabilities, damages and txpenses, 'lire pofty shall include employers' liability (Washington Stop Gap Coverage). The policy shall name as an additional insured Owner, its successors and assipis, directors, employees, and agents, and shall include a say uahlNy of interest Vrov€sion. 5.2 ,Buslness Automobile Liability. -Consultant shall secure and maintain during the tern of this Agreement it business automobile policy for autos owned, hired, or loaned by Consultant in the amount of not, less than $1,000,000, combined single limit. 5.3;Professional Liability. Consultant shall secure and maintain professional errors and omissions insurance in an amotun not less than $1,000,000, per claim. and in the aggregate, for claims that may result in any way from negligent performanee of Consultant obligations under this Agreement. Consultant shall maintain such insurance for six years after 9ubstant.ial Completion. Consultant shall promptly notify Owner of any material changes to, interruption of, or termination of this insurance. Consultant shall cootractvolly require its professional consultants of any tier to iria%ntatin professional errors and omissions insurance in att amount of atleast 50% of the above antOunt, except the following consultants shall have $1,000,000 in coverage, if ptnfessional errors and vruissions insurance arenat CORPORATION OF THE CATHOLIC ARCHBISHOP OF SEATTLE - CONSULTANT AGREEMENT Wetland delineation and report for Gethsemane Cemetery reasonably available for Consultant or a class of consultants, Consultant Trust so notify Owner in writing and provide alternativc protection fbi Owner. 5.4 other Insurance. Consultant shall also maintain insurance for claims under worker's Compensation (Industrial Insurance), disability bepefls and other similar employee benefit acts in the amount required by applicable laws. All Insurance's required shall be at the sole expense of Consultant and be placed with such insurers and under such policy forms, limits and dednctibies zs may be reasonably required by Owner. s.$ Within ten days of cxcculion of this At r©omeni, and annually thereafter, Consultant shall deliver W Owner cerlifietttvs of ittsuranve ln�luding renewal or rep#aocmenl oertificates) acceptable to owner and signed by the insurer or its authorized representative, certifying [hot the policies providing insurance of fire kind and coverage required herein is in thil farce and effect. The certificates shall further cefiti y that policies shall not be cancelled or materially changed without giving 30 (lays prior riotico of such cancellation or change and, cKcept fbr professional liability policies, that Owner is rut Additiowd Insured. The foregoing roquircments " to ina'rranee and au eprobiIity to Owner of insurers and insurance to he maintained by Consultant shallI not in any manner limit or qualify tits liabilities or obligations assumed by Corrsuhnnt under this agreement. 5.6 Consultant shell not in nny manner lirnit or qualify the liahllities or obligations assumed by Consultant under this agreement. ARTICLE 6 INi)EMNIFCATION Consultant agrees to indemnify and bold harmless owner, its successors assigns and representatives and the directors, employees and agents oC each of tho foregoing ("Indemnified parties"), from and against any and all claims of third parties and all costs, Nobi Mies, damagoa and expenses (Including, but not limited to, reasonable attorneys' ftics) related to or resulting from sueli claims of third parties arising out of or in casinemion with any misfeasance or negligence in (1) ilre performance. of or fuiIure'to perforro servlcas or o Ill igations under this agreement, or (2) tiro (tots or omissions of Consultant or any of its COW Hants 4f nny iter, the respective 9uccessors and assigns of Consultant or any such eonsuitonts, the dit-eclors, officers, employees and agents of each of the foregoing, ar anyone acting on dousultant's behalf In connection with this Agreement or its performance, PROVMTMI ro%vevcr, that Consultant shall not be required to s6 indemnify any of such TndomnMed Parties against liability for damages caused by or resulting ftoni the sole negligence of IOdemni&d Plorties; PROVIDED FURTHRR that if $[rel) dain ages are caused by or trsuit fmm 4lie ccncurreni ucgiigencc of Indemnified Parties and ar donsulinnt or its agents, consultants or erripleyees, then Consultant's indetinlity haretinder shall be l'nnited to the extent of fire tlagllgenoa of Consultant or its agents, eonsiiltaors or employees. ARTICLE 7 DISPUTES 7,1 In the event Owner and Consultant arc tunable to agree upon tho #nterprelation, application or intcnl of any provision of Phis Agroenicnl, or In the event any dispute, claim, question or disagmmem (collectively rafermd to as a "dispute") arises out of or rrlates to this Agreement, the patties shall use their best efforts to resolve the dispute through negotladou. If the dispute is not resolved by negotiation, tlia parties shall proceed to mediation. C;onoluslon of at least one mediation session shall boa condition preeodetit to Court fitigation. 1.2 Notice of Dispute. Within ten days after a dispute arises, the patty seeking relief shall deliver to the other party a written notice roquesiina resolution of die Dispute uridnr the Dispute resolution procedures of this Agreement. The notice stroll. (s) inoludo a statement of the cause of the Dlspule; (b) cite applicable contract provisions; (c) stoic the relief sought, (d) Werttlty the date the matter became a Tjiopute. 7,.3 Negotiation. Each party shall appoint it senior representative to negotiate the ❑ispute on its behalf'. Within ten days oiler delivery of the Not ico of Dispute, the senior representatives shall meet or confer at a mutually agreed upon time and attempt in good tatth to resolve the Dispute. If the senior representatives are unable 10 resolve the dispute within thirty days of delivery of the Notice of Dispute. the parties shall proceed to resolution of the Dispitte through mediatlon. 1A Mediation. If the dispilte lies not been nuolved by negotiation, within hrty•fivo days after sorvieeof the Notice of Dispute rho parllcs flail mutually appoint a single incdiator to assist them in resolving the dispute. If the parties are unable to agree upon a mediator within the forty-five day period, dither party may submit the dispute to mediation through the American Arbitration Assooiation. The mediation shall be held in Seattle, Washington, unless 1110 parties agree in writing oillerwisa, The Parting shall schedule a mediation session as recap as practicable. The costs ofthc mediation Aall be equally divided between the parties. Conolsisian of at least one mediation session shall be a condition prew&,ni to litigation in an Inatitution of legal or equitable proceedings by enter party, 7.5 in the event of any litigation between the Owner and the Consultant to enforce any provisions or rights liel•eunder, the unsuoeessful party to such litlgation agrees to Puy to the successful parties therein all reasonable casts and expenses incurred tricluding, but not limited to reasonable attorneys' foes, court costs, arbitrat#on fees, and expert witness fees, 7.6 If any pansy who is substantially involved in a common question of faet or law with regard to a dispute which is subject to the mediation procedure cannot be made a party to such .procedure, then at the owner's sole discretion and upon written notice to the Consultant, the dispute which was to be subject to the mediation procedure will no longer be, subject thereto and may be pursued In litigation. Pogo 2 of 3 CORPORATION OFTHE CATHOLIC ARCHBISHOP OF SEATTLE , CONSULTANT AGREEMENT Wetland delineation and report for Gethsemane Cetxetery 7.7 Pending resolution Of any dispute, tho parties sha]I continue to perfonn and meet tile ir oil Ilptions under this agrovrnortt. If it pending dispute affeots or precludes -such performance, Owner shall determir-e and, As appropriate, direct the Inethod or extent of performance to be ptpvided until the dispute is resolved. 1`he failure of Coneuitnnt to comply and cooperate with owner's dctorknittation and directions is ,ustilicntlon for termination of this agraement. Tlie Disputes provisions of this Agreement shall remain in felt fotxte and effect following Any termination Of this agreement for cause or foe owner's convenience. AR11CLY 8 PAYMENT TS AND COMPENSATION TO THE CON 81WANT 8.1 no Owner shall compensate and reimbursed the Consiiltnnt as detormined by Attachnzem (A). 8.2 If through no fault of the Consultant the services covered by this Agreement have not been eomplLied within E€gbtesn 08) mairths at the dam hereof, compensation for the Consultant's services beyond that time shall be nppropriately adjusted. 8.3 Payments arc due and payable upon recoipt of die Consultant's involve. Antounts unpaid Wily (30) days after Invoice date shall bear interest from the data payment ]s due at tine rate 0f six peroent (d°h) per An nutn. 9,4 Consultant Services not covomd by this Agrootnent lneludo, among Others, revisions due to changes in the scope, quality or budget. 'rhe Consultant shall be paid additional fees for these services based on the Consirliam's hourly rates when the services aYeperforrncd. AiRTIC.LE 9 O"IMER 3'ROVISIONS: 911 This Agreement supersedes any similar provision in the attached documents and shall be governed by the laws of the State of ;whington. 9;2 The Owner end Consultant, respectively, bind themselves, their partners, successors, assigns and legal representatives to this Agreement. Neither party to this Agreemunt shsli assign the contract as a whole without w1itten consent oftho other. 9 3 The Consultant and Consuh'ant's consultants thalI have no res pons [bi I ity for the iden hifcrttkokr,discovery, prosettcc: handling, removal al• tilspmai of, or expostFre ofporsons to, hemrcioua materials in any form at the project site, 9i4 No risk allocation will be allowed in this agreement. Refer to the insurance requir MMS listed in articto 5. 9,5 All consultant personnel, during die period when children are present, shall have an identification badge det,oting they are consultant personnel associated with the project. No corisnitarit pe nnel shall he working in an area with children present unless a staff person 4soniated with the parl$h is present. 90.4 List till documen a ached to this agrrxen a isions of this agreement take precedent to Any conflicting terms in the listed documents: ft/�.1'015 K PAf-06 mm (Ptak Scope Work an F WISsfi At eit ent A) Agrexment entered into as of the day and year lust written above. Ct7RPC1lwr'0 OF THE CATHOLIC 1�$Islro �>r SI�ATTr,I [ nk Fe snap Attorney in Fact APPROVED BY; Print nam '~�T� ��f' �e�tjnimtcrt� �LyIAe.Y� RL;ak --- c. Page 3 of 3 ,`-ce'fkefe/r ej 1 1 1 1 I 1 I 1 7 I I WETLAND AND STREAM DELINEATION REPORT Gethsemane Cemetery Federal Way, WA Prepared for: Corporation of the Catholic Archbishop of Seattle 710 9`h Avenue Seattle, WA 98104 Prepared by: Otak, Inc. 11241 Willows Road NE, Suite 200 Redmond, WA 98052 February 25, 2016 �i-g MAR 0-i Z016 CITY OF FEDERAL WAY rnS lr /�y-�9y-kl-;D WETLAND AND STREAM DELINEATION REPORT Gethsemane Cemetery Federal Way, WA February 25, 2016 Prepared By: Otak, Inc. Jeff Gray, Senior Wedand Scientist (425) 822-4446 Project Representative: Richard Peterson (206) 524-1451 Archdiocese of Seattle Other Contributors and Role: Kevin O'Brien, Senior Ecologist I Executive Summary The Corporation of the Catholic Archbishop of Seattle (Archdiocese of Seattle) is undertaking a long range planning effort for Gethsemane Cemetery in Federal Way, Washington, with the goal of achieving long-term master plan development approval from the City of Federal Way through its Process IV land use application process. A Cemetery Master Plan will be prepared, and is intended to guide cemetery development in several phases over the next 50 years. This Wletland and Stream Delineation Report documents baseline wetland and stream boundaries and functions at the Gethsemane Cemetery to support the long range planning effort. Methods to complete the wetland and stream delineation included reviewing background information, conducting a field investigation, and classifying wetland and streams and assessing their functions per local and state regulations. Otak, Inc. biologists delineated wetlands using the three - parameter approach detailed in the Corps of Engineers Wetlands Delineation Manual (USACE, 1987) and the Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Western Mountains, Valleys, and Coast Region (Version 2.0) (USACE, 2010). Wetlands were classified according to Classification of Wetlands and Dee pmater of Untied States (Cowardin, et a1.,1979) and the hydrogeomorphic (HGM) wetland classification (Brinson, 1993). Wetland functions and buffers were rated using the Washington State Wetland Rating System for Western Washington (Hruby, 2014). The field investigation was conducted on November 4, 5 and 12, 2015. Otak, Inc. biologists delineated 14 separate wetlands on the Gethsemane Cemetery properties as shown on Figure 7 in Appendix B. The total area of delineated wetlands is 3.50 acres, mostly occurring as forested and shrub wetland habitats along West Fork Hylebos Creek and along the northern property boundary. Wetlands 1, 4, 6, and 13 extend beyond the property boundaries. No wetlands or streams were observed on the undeveloped portion of the study area east of West Fork Hylebos Creek. The 14 delineated wetlands are variously rated as Category II and III per the 2014 Ecology Wetland Rating System (Hruby, 2014), and have buffers between 60 and 165 feet (Federal Way Revised Code [FWRg19.145.420). Cowardin wetland classes include palustrine forested (PFO), scrub -shrub (PSS), and emergent (PEM) habitats. Wetlands 7, 8, 9, 11, and 12 are classified as PFO; wetlands 4, 10, and 13 are classified as PSS; wetlands 2, 3, and 14 are classified as PEM; and, wetlands 1, 5, and 6 have PFO/PSS/PEM habitat mosaics. Wetlands were classified as depressional, riverine, and slope per the HGM classification system. Wetland 2, artificially created in a roadside ditch along Pacific Highway South, is exempt from the FWRC per Chapter 19.145.110(3), and does not have an associated buffer. The ordinary high water mark was delineated along both sides of West Fork Hylebos Creek. West Fork Hylebos Creek is classified Type F (fish habitat) per FWRC 19.145.260, and has a 100-foot stream buffer. Artificial, intermittently flowing watercourses were delineated between Wetland 2 and Wetland 1 in a roadside ditch, and from a stormwater outfall that discharges to Wetland 6. The intermittent streams are classified Type Ns (seasonal, non -fish habitat), and do not have buffers because they are exempt per FWRC 19.145.110(3). Gethsemane Cemetery i February 25, 2016 Wetland and Stream Delineation Report Table of Contents Chapter1. Introduction.........................................................................................................1 77 Location and Setting....................................................................................................................................1 Chapter2. Methods................................................................................................................2 21 Review of Published Information................................................................................................................. 2 2.2 Evaluation of the Gsoming Season..............................................................................................................2 2.3 Field Inms1igation....................................................................................................................................... 3 2A Wetland and Stream Classification and Ra irgs.......................................................................................... 3 Chapter 3. Existing Conditions...........................................................................................5 31 Landscape Setting and Projectf rea 0vemiew.............................................................................................5 3.2 Wletlands....................................................................................................................................................5 3.3 Streams.................................................................................................................................................... 25 3A Sensitive Plants, Fish, and GWlildlrfe ........................... 25 3.5 Regulatory Summary.................................................................................................................................26 1 3.61V itigation Opportunities...........................................................................................................................27 Chapter4. References.........................................................................................................28 -1 Tables Table 3-1. Delineated Wetlands within the Gethsemane Cemetery........................................................... 7 Table3-2. Wetland 1 Summary........................................................................................................................ 8 Table 3-3. Wetland 2 Summary• ... 9 ......................................................................... Table 3-4. Wetland 3 Summary. .10 .......................................... Table3-5. Wetland 4 Summary......................................................................................................................11 Table3-6. Wetland 5 Summary......................................................................................................................12 Table3-7. Wetland 6 Summary.................................................................................................................13 Table3-8. Wetland 7 Summary...................................................................................................................14 Table3-9. Wetland 8 Summary..................................................................................................................15 Table3-10. Weiland 9 Summary...................................................................................................................16 Table 3-11. Wetland 10 Summary. .17 Table3-12. Wetland 11 Summary.................................................................................................................18 JTable 3-13. Wetland 12 Summary.................................................................................................................19 Table3-14. Wetland 13 Summary.. ............................ - .................. I ............................. .. . . ......... N ................... 20 Table3-15. Wetland 14 Summary..................................................................................................... .....:....... 21 Table 3-16. NRCS Soil Units Mapped on the Gethsemane Cemetery Property....................................22 Gethsemane Cemetery ii February 25, 2016 Wetland and Stream Delineation Report Appendices Appendix A Methods and Tools Appendix B — Project Figures and Background Information Appendix C Wetland Determination Data Forms Appendix D — Ecology Wetland Rating Forms Appendix E — Plant Species Observed within the Study Area Acronyms and Abbreviations Ecology Washington State Department of Ecology ESA Endangered Species Act FWRC Federal Way Revised Code GIS Geographic Information Systems HGM Hydrogeomorphic NRCS Natural Resources Conservation Service NWI National Wetlands Inventory OHWM ordinary high water mark PEM palustrine emergent PFO palustrine forested PHS Priority Habitat and Species USACE U.S. Army Corps of Engineers USFWS U.S. Fish and Wildlife Service USGS U.S. Geological Survey WAC Washington Administrative Code WDFW Washington State Department of Fish and Wildlife WRIA Water Resource Inventory Area Gethsemane Cemetery iii February 25, 2016 Wetland and Stream Delineation Report Chapter 1. Introduction The Corporation of the Catholic Archbishop of Seattle (Archdiocese of Seattle) is undertaking a long range planning effort for Gethsemane Cemetery in Federal Way, Washington, with the goal of achieving long-term master plan development approval from the City of Federal Way through its Process IV land use application process. A Cemetery Master Plan will be prepared, and is intended -� to guide cemetery development in several phases over the next 50 years. This wetland and streams delineation report documents baseline wetland and stream boundaries and functions at the Gethsemane Cemetery to support the long range planning effort. This report will facilitate efforts to: • Document wetland and stream boundary determinations for review by local, state, and federal regulatory authorities; • Document and characterize baseline wetland and stream conditions and wetland functions; • Determine wetland and stream buffer locations and widths per Chapter 19.145 (Environmentally 1 Critical Areas) of the Federal Way Revised Code (FWRC); and, • Assess potential compensatory mitigation opportunities on -site. 1.1 Location and Setting 1 The Gethsemane Cemetery is located in the City of Federal Way in King County, Washington (Appendix B - Figures 1 and 2), and includes the following tax parcels: #322104-9025, #322104- 9020, #218820-4560, #218820-4281, and #218820-4365 (herein referred to as the study area). The parcels are located in Section 32, Township 21 North, Range 4 East, Willamette Meridian. The cemetery is located within the West Fork Hylebos Creek basin within the larger Hylebos Creek watershed. The study area is bordered to the west by Pacific Highway South (State Route 99), to the east by - J Interstate Highway 5, and to the north and south by rural residential, agricultural, and commercial land uses. West Fork Hylebos Creek runs through the center of the study area from north to south. The existing, developed cemetery grounds are mainly located west of West Fork Hylebos Creek. The undeveloped area east of West Fork Hylebos Creek is comprised of secondary -growth forest. Forest lands along West Fork Hylebos Creek are also located north and south of the cemetery. `1 Gethsemane Cemetery 1 February 25, 2016 Wetland and Stream Delineation Report 1 Chapter 2. Methods This chapter summarizes the methods used to comply with local, state, and federal guidance in delineating wetland and stream boundaries in Washington State. See Table A-1 in Appendix A for further details regarding methods used for this report. 2.1 Review of Published Information Available site information was reviewed prior to the field effort to identify any previously documented wetlands, streams, or other site characteristics (e.g., vegetation community patterns, topography, soils, or water courses) that would indicate the presence of wetlands within the Gethsemane Cemetery properties. These maps are typically used as guidance, and do not supersede conditions in the field. As part of this effort, Otak, Inc. biologists reviewed the following sources: • Soils map from the United States Natural Resources Conservation Service (MRCS 2015); • National Wetlands Inventory (United States Fish and Wildlife Service (USFWS,2016); • WDFW Salmonscape and Priority Habitat and Species maps (WDFW, 2016) • King County GIS Data Portal - wetlands (King County 2015); and • Aerial photo of the vicinity using public web -based mapping service (Google Maps 2015). 2.2 Evaluation of the Growing Season Wetland hydrologic conditions are considered present if an area has 14 or more consecutive days of flooding or ponding, or a water table 12 inches or less below the soil surface, during the growing season, depending on soil and plant community conditions (USACE 2010). In the Pacific Northwest coast region, the beginning and ending dates of the growing season can be defined based on two indicators of biological activity that are readily observable in the field: (1) above ground growth and development of vascular plants, and (2) soil temperature. However, due to seasonal fluctuations from year to year the growing season dates may also be approximated by the number of frost -free days, defined as the time from the last date in spring when the ambient air temperature drops to 28°F, to the first date in fall when it drops to 28°F, over a 30-year period (USACE, 2010). As such, the beginning and ending dates for the growing season in the study area were estimated from long-term weather records as the median dates (50 percent probability) for the first and last 28°F days. Based on long-term weather records, the average start and end dates for the growing season for the area are February 6 and December 9, respectively, for a total growing season of 305 days (MRCS 2015). Gethsemane Cemetery 2 February 25, 2016 Wetland and Stream Delineation Report 2.3 Field Investigation Wetland and stream boundaries were assessed and delineated on the Gethsemane Cemetery properties on November 4, 5 and 12, 2015. In accordance with federal, state, and local guidance and regulations, Otak, Inc. biologists delineated wetlands using the three -parameter approach detailed in the Corps of Engineers Vetlands Delineation Manual (USACE, 1987) and the Regional Supplement to the Corps of Engineers Wletland Delineation Manual - Western Mountains, Valleys, and Coast Region (Version 2.0) (USACE, 2010). Following routine methodology, data on vegetation, soils, and hydrology were collected in areas that appeared to have wetland characteristics at 22 data points. The location of each data point is shown on the Delineated Wetlands and Streams Mapping series (Figures 7A through 7E) in Appendix B. Data for wetland and upland plots were recorded on USACE wetland determination data forms and are provided in - Appendix C. Wetland boundaries were marked with sequentially numbered pink pin flags in meadow areas and pink -and -black -striped flagging in shrub and forested areas. Wetland flags were professionally surveyed and transferred to geographical information systems (GIS) mapping V programs. The forested area east of West Fork Hylebos Creek was reviewed by walking transects from the east side of West Fork Hylebos Creek to the eastern parcel boundary near Interstate 5. Two wetland determination data sheets (11 and 12) are provided that document conditions in this area. The ordinary high water mark (OHWM) along West Fork Hylebos Creek was marked in the field using orange flagging. Identification of OHWM was based on the presence of primary field indicators, such as: break in slope, change in sediment and vegetation characteristics, drift lines, erosion/scour, and silt deposits. If a riverine wetland influenced the channel characteristics then it was included with the stream OHWM boundary. Qualitative data on riparian condition was also included as part of the field data collection effort. 2.4 Wetland and Stream Classification and Ratings Wetlands on the Gethsemane Cemetery properties were classified using the Classification of Wetlands and Deepwater Habitats of Untied States (Cowardin, et a1.,1979) and hydrogeomorphic (HGM) wetland classification (Brinson, 1993). Wetland functions were rated using the i-YVashington State Wletland Rating System for Western Washington — 20/4 Update (Hruby, 2014) in accordance with FWRC 19.145.420. Wetland rating forms and figures are provided in Appendix D (Ecology Rating Forms). Wetland buffer widths were determined based i on wetland habitat scores and wetland categories for each wetland. Wetland buffer conditions were qualitatively assessed based on vegetation cover, land use, and presence of invasive species. Delineated streams were classified according FWRC 19.145.260, which follows the Washington Department of Natural Resources stream typing system per Washington Administrative Code (WAC) 222-16-030. Stream buffer widths were determined by stream type per FWRC 19.145.270. —J Gethsemane Cemetery 3 February 25, 2016 Wetland and Stream Assessment Report Wetland and stream locations are described in Chapter 3 and shown on Figure 7 (Delineated Wetlands and Streams Map) in Appendix B. Gethsemane Cemetery 4 February 25, 2016 Wedand and Stream Assessment Report Chapter 3. Existing Conditions 3.1 Landscape Setting and Project Area Overview The Gethsemane Cemetery (Parcel Nos. 322104-9025, 322104-9020, 218820-4560, 218820-4281, and 218820-4365) is located in Water Resource Inventory Area (WRIA) 10 (Puyallup -White) in the City of Federal Way, King County, Washington. The western half of the study area includes the active cemetery with the administrative building, parking lot, driveways, and walkways. The eastern half of the study area is undeveloped, and includes mixed deciduous and evergreen, secondary growth forest habitat. West Fork Hylebos Creek flows from north to south within a ravine that separates the developed and undeveloped portions of the study area (Appendix B, Figure 3 — Topography Map) The study area is bordered to the west by Pacific Highway South (State Route 99), to the east by Interstate Highway 5, and to the north and south by rural residential, agricultural, and commercial - land uses. An offsite wetland mitigation project borders the northern edge of the cemetery properties west of West Fork Hylebos Creek. The climate in Federal Way is characterized by the mild climate of the Puget Sound lowlands with warm, generally dry summers, and cool, wet winters. The average annual rainfall in the Puget Sound lowlands is 32-35 inches. 3.2 Wetlands 3.2.1Overview Otak, Inc. biologists delineated 14 separate wetlands on the Gethsemane Cemetery properties as shown on Figure 7 in Appendix B. The total area of delineated wetlands is 3.50 acres, mostly occurring as forested and shrub wetland habitats along West Fork Hylebos Creek and along the northern property boundary. Wetlands 1, 4, 6 and 13 extend beyond the property boundaries. No wetlands or streams were observed on the undeveloped portion of the study area east of West Fork Hylebos Creek. Wetland determination data forms are provided in Appendix C, and Ecology wetland ratings forms and figures are provided in Appendix D. A list of plant species observed during field work is included as Appendix E. Gethsemane Cemetery 5 February 25, 2016 Wetland and Stream Delineation Report 3.2.2 Background Review Appendix B includes figures associated with the background review, including: an aerial photograph of the Gethsemane Cemetery properties (Figure 2), a topographic map (Figure 3), a NRCS soils map (Figure 4), a NWI map (Figure 5), and a Federal Way wetlands and streams map (Figure 6). Two NWI freshwater wetlands are mapped within the property boundaries, and include forest and shrub habitats. Federal Way maps two wetlands in the study area, and two other wetlands abutting the study area. Wetlands are shown on Parcel Nos. 322104-9025 and 322104-9020. An unnamed tributary to West Fork Hylebos Creek is shown along the northern edge of the study area after crossing underneath SR 99. 3.2.3 Delineated Wetlands The 14 delineated wetlands in the study area are rated as Category II and III per the 2014 Ecology Wetland Rating System (Hruby, 2014), and have buffers between 60 and 165 feet (FWRC 19.145.420). Wetland 2, artificially created in a roadside ditch along Pacific Highway South, is exempt from the FWRC per Chapter 19.145.110(3), and does not have an associated buffer. Cowardin wetland classes included palustrine forested (PFO), scrub -shrub (PSS), and emergent (PEN) habitats. Wetlands 7, 8, 9, 11, and 12 are classified as PFO; wetlands 4, 10, and 13 are classified as PSS; wetlands 2, 3, and 14 are classified as PEM; and, wetlands 1, 5, and 6 have PFO/PSS/PEM habitat mosaics. Wetlands were classified as depressional, riverine, and slope per the HGM classification system. Wetland classes, sizes, and buffer widths are summarized in Table 1 and Table 2. Wetland 1 is located in the northwest corner of the study area. It receives stormwater runoff collected by a roadside ditch (Wetland 2) along the east side of SR 99, and drains to a large wetland complex adjacent to West Fork Hylebos Creek. Wetland 3 is a small wetland in a depression in the western -most corner of the study area adjacent to the east side of SR 99, and likely drains into the municipal stormwater system. Wetlands 4, 5, and 7-13 are situated along the banks of West Fork Hylebos Creek, and are periodically inundated during high flow events. Wetland 6 is a large groundwater -supported wetland complex that maintains flows in West Fork Hylebos Creek. Wetland 14 is another small depression situated at the toe of slope adjacent to a gravel road on the neighboring property. Individual wedand characteristics are summarized in Table 3-1, and wetland profiles are provide in Tables 3-2 to 3-15. Gethsemane Cemetery 6 February 25, 2016 Wetland and Stream Assessment Report _1 Table 3-1. Delineated Wetlands within the Gethsemane Cemetery Wetlands Wetland Classification Wetland Size 4 Habitat Score from Ecology Rating System Buffer Wi(fedth Cowardin2 HGM Ecology3 Square Acre W1 PFO/PSS/ PEM Depressional/Slope Unit 1: III Unit 2:111 Unit 3: II >64,890 >1.49 Unit 1: 6 Unit 2: 5 Unit 3: 7 Unit 1: 165 Unit 2: 105 Unit 3: 165 W2 PEM Slope III 290 0.01 4 0 W3 PEM Depressional 1II 580 0.01 4 60 W4 PSS Riverine II 970 0.02 6 165 W5 PFO/PSS Riverine/Slope II 7,030 0.16 6 165 W6 PFO/PSS Depressional/ Riverine/Slope II >66,750 >1.53 7 165 W7 PFO Riverine II 480 0.01 6 165 W8 PFO Riverine II 400 0.01 6 165 W9 PFO Riverine II 6340 0.15 6 165 W10 PSS Riverine II 260 0.01 6 165 W11 PFO Riverine II 330 0.01 6 165 W12 PFO Riverine II 480 0.01 6 165 W13 PSS Riverine II 910 0.02 6 165 W14 PEM Depressional III 2,940 0.07 4 60 TOTAL 152,650 3.50 a Note: k 1. Wetlands shown on Figure 7, and Figures 7A to 7E in Appendix B. 2. Cowardin et al. (1979). Class based on vegetation: PEM = Palustrine Emergent; PFO = Palustrine Forested; PSS = Palustrine Scrub -Shrub. 3. Ecology category according to Hruby (2014). J4. Wetlands sizes measured within the study area boundaries; Wetlands 1 and 6 extend beyond study area boundaries. 5. Wetland buffer width according to FWRC 19.145.420. Wedand 2 is artificially created and has no buffer because it is exempt from the FWRC per Chapter 19.145.110(3). Gethsemane Cemetery 7 February 25, 2016 Wetland and Stream Assessment Report Table 3-2. Wetland 1 Summary. WETLAND 1— INFORMATION SUMMARY Location: Forest, shrub, and emergent wetland on Parcel No. 322104-9020 Local Jurisdiction City of Federal Way WRIA 10 e t Ecology Rating Unit 1: III (Hruby, 2014) Unit III Unit 3: II Federal Way Rating Same Unit 1: 165 feet Federal Way Buffer Width Unit 2: 105 feet Unit 3: 165 feet Wetland Size on -site 1.49 acres Cowardin Classification PFO, PSS, PEM HGM Classification Depressional, Slope Wetland Data Sheet(s) 1, 3, 5 Upland Data Sheet (s) 2, 4, 6 Flag color Pink/black stripe & pink pin flags Dominant Salix sitchensis, Phalalaris arundinacea, Typba latifolia, Spiraea douglasd Vegetation Soils Silt loam 10YR 3/1 and clay loam 10YR 5/1, with redoximorphic features. Hydrology Receives hydrology from stormwater discharges, groundwater seeps, and precipitation. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wetland 1 provides a moderate level of hydrologic functions because it has a slightly constricted Hydrologic outlet, is relatively flat with small depressions on the surface that trap water, and has a large contributing basin. Wetland 1 receives stormwater discharges from SR 99, and drains to West Fork Hylebos Creek. Wetland 1 provides a moderate level of water quality improvement functions because it is relatively flat with small depressions, and has dense vegetation that traps water and remove sediment and Water Quality excess nutrient/toxicants. Stormwater discharges from SR 99 increases the potential of the wetland to provide these functions. Erosion control and shoreline stabilization is also provided because a portion of the wetland is situated adjacent to a watercourse. Wetland 1 provides a high level of biological and habitat functions. Production/export of organic matter is provided since the wetland does receive overbank flooding and drains to West Fork Habitat Hylebos Creek. The wetland includes a mosaic of different vegetation communities, has multiple hydroperiods, and has accessible undisturbed habitat associated with the West Fork Hylebos corridor. Wetland vegetation is dominated by native plants. The buffer around Wetland 1 in the study area is an upland meadow dominated by non-native Buffer Condition grasses with scattered tree saplings and shrubs. A portion of the buffer is mowed regularly, and Himalayan blackberry has grown over a pile of concrete rubble near SR 99. Gethsemane Cemetery 8 February 25, 2016 Wetland and Stream Assessment Report J Table 3-3. Wetland 2 Summary. WETLAND 2 — INFORMATION SUMMARY Location: Emergent wetland on Parcel No. 322104-9020 adjacent to SR 99 (Pacific Highway South) Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating III (Hruby, 2014) Federal Way Rating III Federal Way Buffer Width 0 (exempt per FWRC19.145.110(3) Wetland Size 0.01 acre Cowardin Classification PEM HGM Classification Slope Wetland Data Sheet(s) 21 Upland Data Sheet (s) 22 Flag color Pink pin flags Dominant Phalari.r arundinacea, Ranunculus repens, Poa pratensis, fgroisti.c capillari.r Vegetation Soils Loam, 10YR 2/1 Hydrology Receives hydrology from surface runoff and precipitltion. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wedand 2 provides a moderate to low level of hydrologic functions as a roadside ditch because it conveys stormwater to Wedand 1 down gradient. It has a small contributing basin including SR 99, Hydrologic and has small depressions on the surface that trap water, and herbaceous vegetation that slows surface runoff. Wedand 2 is located within the Hylebos Creek basin, which has flooding problems downstream, and makes these hydrologic functions valuable to society. Wetland 2 provides a moderate to low level of water quality improvement functions because it is relatively flat with small depressions, and has dense vegetation that traps water and remove sediment and excess nutrient/toxicants. Wedand 2 receives stormwater from the adjacent roadway Water Quality (SR 99), which increases the potential of the wetland to trap toxicants and improve water quality. Water flows through the wedand unconstrained and is mowed regularly, which limits the ability of Wetland 2 to provide water quality functions. Wetland 2 provides a low level of habitat functions. Production/export of organic matter is provided to a low degree, but herbaceous plants and stormwater flows increase the potential of the Habitat wedand to provide this function. Wedand 2 is adjacent to the roadway, which limits use by wildlife. The wedand provides no habitat for aquatic invertebrates, amphibians, wetland -associated mammals, or wedand-associated birds due to no ponded or marsh areas. The buffer around Wetland 2 is in poor condition. SR 99 borders the west side of Wedand 2. The Buffer Condition buffer east of Weiland 2 includes mowed lawn and cemetery grounds that are maintained. j Gethsemane Cemetery Wedand and Stream Assessment Report February 25, 2016 Table 3-4. Wetland 3 Summary. ' WETLAND 3 — INFORMATION SUMMARY Location: Emergent wetland on Parcel No. 218820-4560 adjacent to SR 99 (Pacific Highway South) s - Dominant Vegetation Phalaris arundinacea, Spiraea douglasit, Juncus Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating (Hruby, 2014) III Federal Way Rating III Federal Way Buffer Width 60 feet Wetland Size 0.01 acre Cowardin Classification PEM HGM Classification Depression Wetland Data Sheet(s) 7 Upland Data Sheet (s) 8 Flag color Pink/black stripe eusus, Equisehan., aruense. Soils Loam, 10YR 4/2 with redoximorphic concentrations at 4" depth. Hydrology Receives hydrology from high groundwater, surface runoff, and precipitation. Rationale for Delineation Satisfies all three wetland criteria. Rationale for Local Rating Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Wetland Functions Summary Wetland 3 provides a moderate level of hydrologic functions because it has a slightly constricted Hydrologic outlet that detains water during wet periods. Wetland 3 is supported by a high groundwater table, surface runoff from adjacent impervious surfaces, and precipitation. Wedand 3 provides a low to moderate level of water quality improvement functions because it has Water Quality a slightly constricted outlet that causes the wetland to retain water, and has dense vegetation that removes sediment and excess nutrient/toxicants. Wetland 3 receives stormwater from the adjacent roadway, which increases the potent 4 of the wetland to trap toxicants and improve water quality. Wetland 3 provides a low level of bif -logical and habitat functions. Wetland 3 is adjacent to SR 99, Habitat which limits its use by wetland -associated wildlife. Wedand vegetation is dominated by non-native, invasive reed canarygrass, which limits the establishment of native vegetation. A single piece of downed large woody debris in the wetland potentially provides habitat for amphibians. The buffer around Wetland 3 includes a mix of developed and undeveloped land cover. Wetland 3 is bordered to the west by SR 99, and to the south by a commercial business with a large gravel Buffer Condition driveway and parking area. Forested and lawn areas are located east of Wetland 3. The small forest path that borders Wetland 3 includes a multi -strata vegetation community dominated by Douglas fir trees. Gethsemane Cemetery 10 February 25, 2016 Wedand and Stream Assessment Report -1 Table 3-5. Wetland 4 Summary. I II I WETLAND 4 — INFORMATION SUMMARY Location: Shrub wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek ? r Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating II (Hruby, 2014) Federal Way Rating II A z• :s Federal Way Buffer Width 165 feet Wetland Size 0.02 acre Cowardin Classification PSS - { `•` HGM Classification Riverine Wetland Data Sheet(s) 13,15 Upland Data Sheet (s) 14,16 Flag color Pink/black stripe Dominant Rubus spectabilis, ff cer dreinatum, Ranunculus repens, Lysicbiton americanus, and Equisetuni arvense. Vegetation Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wetland 4 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has a dense shrub vegetation community that functions to slow down Hydrologic water velocities during floods. Wetland 4 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wetland 4 provides a moderate level of water quality improvement functions because it has surface depressions that trap sediments during flood events, and dense forest and shrub vegetation that can Water Quality remove sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wetland is located along a watercourse. Wetland 4 provides a low to moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and surface flows through Habitat the wetland increase the potential of the wetland to provide this function. Wetland 4 has forest habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wetland vegetation is dominated by native plants. Wetland 4 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer Buffer Condition includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery JWedand and Stream Assessment Report 11 February 25, 2016 Table 3-6. Wetland 5 Summary. WETLAND 5 — INFORMATION SUMMARY Location: Forested and shrub wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek t ' Local Jurisdiction City of Federal Way 4 fF WRIA 10 Ecology Rating (Hruby, 2014) II Federal Way Rating II Federal Way Buffer Width 165 feet Wetland Size 0.16 acres Cowardin Classification PFO/PSS HGM Classification Riverine Wetland Data Sheet(s) 13,15 Upland Data Sheet(s) 14,16 Flag color Pink Black Stripe Dominant lnus rubs, Populus balsimifera sp. trichocarpa, Bubus spectabilis, Lysicbaon amencanus, Tomhea menvem Vegetation Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wetland 5 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has dense forest and shrub vegetation communities that function to Hydrologic slow down water velocities during floods. Wetland 5 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wedand 5 provides a moderate level of water quality improvement functions because it has surface Water Quality depressions that trap sediments during flood events, and dense forest and shrub vegetation that can remove sedin-ent and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wedand is located along a watercourse. Wetland 5 provides a moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and surface flows through the Habitat wetland increase the potential of the wedand to provide this function. Wetland 5 has forest habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wetland vegetation is dominated by native plants. Buffer Condition Wetland 5 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery 12 February 25, 2016 Wetland and Stream Assessment Report I I I Table 3-7. Wetland 6 Summary. WETLAND 6 — INFORMATION SUMMARY Location: Forested and shrub wedand on Parcel No. 322104-9025 along West Fork Hylebos Creek "i 1 Local Jurisdiction City of Federal Way WRIA 10 } .�', r Ecology Rating II AA (Hruby, 2014) Federal Way Rating II Federal Way Buffer Width 165 feet Wedand Size on -site 1.53 acres Cowardin Classification PFO/PSS HGM Classification Depressional, Riverine Wedand Data Sheet(s) 17 Upland Data Sheet(s) 18 Flag color Pink/black stripe Dominant Populus balraniifera spp. tricbocarpa, Salix lasiandra, Kubus spectabilis, Cornus sericea, Lysicbton americanus, Vegetation Equisetum aroense, Sarp;,viurvearpits Soils Organic, 10YR 2/1; sandy loam, 10YR 4/1 with redoximorphic concentrations. Hydrology supported by seeps, overbank flooding from West Fork Hylebos Creek, and a shallow Hydrology groundwater table. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wedand Functions Summary Wetland 6 provides a moderate level of hydrologic functions because it has a large contributing basin, and a slightly constricted outlet that slows surface water from entering West Fork Hylebos Hydrologic Creek. A portion of Wetland 6 receives overbank flooding from the creek, but hydrology is mainly supported by shallow groundwater in alluvial soils. These functions are valuable to the local community as flooding occurs lower in the Hylebos Creek basin. Wetland 6 provides a moderate level of water quality improvement functions as indicated by an organic layer below the soil surface, and dense vegetation that traps water and removes sediment Water Quality and excess nutrient/toxicants. Stormwater discharges from the Gethsemane Cemetery increases the potential of the wetland to provide these functions. Erosion control and shoreline stabilization is also provided because a portion of the wetland is situated adjacent to a watercourse. Wetland 6 provides a high level of biological and habitat functions. Production/export of organic matter is provided since the wetland receives overbank flooding and drains to West Fork Hylebos Creek. The wetland includes a mosaic of different vegetation communities, has multiple Habitat hydroperiods, and has accessible undisturbed habitat associated with the West Fork Hylebos corridor. Wetland vegetation is dominated by native plants. Special habitat features include large woody debris, standing snags, and permanently ponded areas. The buffer west of Wetland 6 in the study area is a secondary growth, mixed deciduous and Buffer Condition evergreen forest on a steep slope that extends up to the Gethsemane Cemetery. Gethsemane Cemetery 13 February 25, 2016 Wetland and Stream Assessment Report Table 3-8. Wetland 7 Summary. WETLAND 7 — INFORMATION SUMMARY Location: Forested wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek Local jurisdiction City of Federal Way { WRIA 10 Ecology Rating II (Hruby, 2014) Federal Way Rating II Federal Way Buffer Width 165 feet Wetland Size 0.01 acre Cowardin Classification PFO HGM Classification Riverine Wetland Data Sheet(s) 13,15 r Upland Data Sheet(s) 14,16 Flag color Pink/Black Stripe Dominant �f lnur rubs, Papules balrimifera Epp. trichocarpa, Rubus rp ectabilis, Lyricbiton americanus, Tomliea menziesii Vegetation Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wetland 7 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has a dense forest vegetation community that functions to slow down Hydrologic water velocities during floods. Wetland 7 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wetland 7 provides a moderate level of water quality improvement functions because it has surface Water QuaLty depressions that trap sediments during flood events, and dense forest vegetation that can remove sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wetland is located along a watercourse. Wetland 7 provides a moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and surface flows through the Habitat wetland increase the potential of the wetland to provide this function. Wetland 7 has forest habitat, and is situated at the mouth of a ravine that provides refuge from roadways or other disturbances. Wetland vegetation is dominated by native plants. Buffer Condition Wetland 7 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery 14 February 25, 2016 Wetland and Stream Assessment Report ITable 3-9. Wetland 8 Summary. WETLAND 8 — INFORMATION SUMMARY Location: Forested wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating II (Hruby, 2014) Federal Way Rating II Federal Way Buffer Width 165 feet Wetland Size 0.01 acre '". Cowardin Classification PFO 4 HGM Classification Riverine Wetland Data Sheet(s) 13,15 Upland Data Sheet(s) 14,16 Flag color Pink/Black Stripe Dominant 1lnus rubra Populus balsimifera ptricboca a, Rubus spedabilis, L szcbiton americanus, Tomkea mn esii Vegetation Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wetland 8 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has dense forest and shrub vegetation communities that function to Hydrologic slow down water velocities during floods. Wetland 8 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wetland 8 provides a moderate level of water quality improvement functions because it has surface depressions that trap sediments during flood events, and dense forest vegetation that can remove Water Quality sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wetland is located along a watercourse. Wetland 8 provides a moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and surface flows through the Habitat wetland increase the potential of the wetland to provide this function. Wetland 8 has forest habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wetland vegetation is dominated by native plants. Wetland 8 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer Buffer Condition includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery Wedand and Stream Assessment Report 15 February 25, 2016 Table 3-10. Wetland 9 Summary. WETLAND 9 — INFORMATION SUMMARY Location: Forested wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating II (Hruby, 2014) Federal Way Rating II Federal Way Buffer Width 165 feet Wetland Size 0.15 acre Cowardin Classification PFO HGM Classification Riverine Wetland Data Sheet(s) 13,15 Upland Data Sheet(s) 14,16 Flag color Pink/Black Stripe Dominant Vegetation d' lnus rubra, Populus balsimifera sp p. tricbocarpa, Rubus spectabilis, Lysicbiton amuicanus, Tomliea men!�iesd Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Local Rating Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Wetland Functions Summary Wedand 9 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has dense forest and shrub vegetation communities that function to Hydrologic slow down water velocities during floods. Wetland 9 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wetland 9 provides a moderate level of water quality improvement functions because it has surface Water Quality depressions that trap sediments during flood events, and dense forest and shrub vegetation that can remove sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wetland is located along a watercourse. Wetland 9 provides a low to moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and surface flows through Habitat the wetland increase the potential of the wetland to provide this function. Wetland 9 has forest habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wetland vegetation is dominated by native plants. Buffer Condition Wetland 9 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery 16 February 25, 2016 Wetland and Stream Assessment Report 1 1 Table 3-11. Wetland 10 Summarv. I I I WETLAND 10 — INFORMATION SUMMARY Location: Shrub wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek Local jurisdiction City° of Federal Way WRIA 10 r Ecology Rating II (Hruby, 2014) Federal Way Rating II Federal Way Buffer Width 165 feet Wetland Size 0.01 acres �. Cowardin Classification PSS HGM Classification Riverine Wetland Data Sheet(s) 13,15 Upland Data Sheet (s) 14,16 Flag color obnupta, Tomliea menyicsii Pink/Black Stripe Dominant Rubu.r sfiectabili,r, Ly.richiton americanu.r, Carex Vegetation Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating. Wetland Functions Summary Wetland 10 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has a dense shrub vegetation community that functions to slow down Hydrologic water velocities during floods. Wetland 10 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wedand 10 provides a moderate level of water quality improvement functions because it has surface depressions that trap sediments during flood events, and dense forest and shrub vegetation Water Quality that can remove sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wedand is located along a watercourse. Wedand 10 provides a low to moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and Habitat surface flows through the wetland increase the potential of the wetland to provide this function. Wetland 10 has shrub habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wetland vegetation is dominated by native plants. Wetland 10 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer Buffer Condition includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. J Gethsemane Cemetery 17 Wetland and Stream Assessment Report February 25, 2016 Table 3-12. Wetland 11 Summary. Vegetation Y lnus rubra, Populus balsimifera .pp. tricbocarpa, Bubus .rpectabilis, Lysicbiton americanus, Tomliea men!iesii Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Delineation Satisfies all three wetland criteria. Rationale for Local Rating Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Wetland Functions Summary Wetland 11 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has dense forest and shrub vegetation communities that function to Hydrologic slow down water velocities during floods. Wetland 11 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wetland 11 provides a moderate level of water quality improvement functions because it has Water Quality surface depressions that trap sediments during flood events, and dense forest and shrub vegetation that can remove sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wetland is located along a watercourse. Wetland 11 provides a low to moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and Habitat surface flows through the wetland increase the potential of the wetland to provide this function. Wetland 11 has forest habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wedand vegetation is dominated by native plants. Buffer Condition Wetland 11 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery 18 February 25, 2016 Wetland and Stream Assessment Report i I I I Table 3-13. Wetland 12 Summary. WETLAND 12 — INFORMATION SUMMARY Location: Forested wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek J Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating II (Hruby, 2014) Federal Way Rating II Federal Way Buffer Width 165 feet Wetland Size 0.01 acre Cowardin Classification PFO ' HGM Classification Riverine #� Wetland Data Sheet(s) 13,15 Upland Data Sheet(s) 14,16 sf Flag color Pink/Black Stripe Tomliea men esii Dominant lnus rubra, Po ulus balsir�i era p trichoca a Kobus ectabilis L p�sichiton americanus Vegetation Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wetland 12 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has dense forest and shrub vegetation communities that function to Hydrologic slow down water velocities during floods. Wetland 12 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wetland 12 provides a moderate level of water quality improvement functions because it has surface depressions that trap sediments during flood events, and dense forest and shrub vegetation V-7ater Quality that can remove sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wetland is located along a watercourse. Wetland 12 provides a low to moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and Habitat surface flows through the wetland increase the potential of the wetland to provide this function. Wetland 12 has forest habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wetland vegetation is dominated by native plants. Wedand 12 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer Buffer Condition includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery 19 February 25, 2016 p Wetland and Stream Assessment Report Table 3-14. Wetland 13 Summary. WETLAND 13 — INFORMATION SUMMARY Location: Shrub wetland on Parcel No. 322104-9025 along West Fork Hylebos Creek 4 Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating II (Hruby, 2014) II Federal Way Rating Federal Way Buffer Width 165 feet } ~ Wetland Size 0.02 acre Cowardin Classification PSS a HGM Classification Rivexine Wetland Data Sheet(s) 13,15 r `-' Upland Data Sheet(s) 14,16 Flag color Pink/Black Stripe Dominant Rubus spectabilis, Polygonum cuspidatum, Lysicbiton americanus, Carex obnupta, Tomliea men.Ziesii Vegetation Soils Sandy loam, 10YR 3/1 and 2.5Y 4/1; G1 4/N below 12 inches. Hydrology Receives hydrology from seeps and overbank flooding from West Fork Hylebos Creek. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Local Rating Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Wetland Functions Summary Wetland 13 provides a moderate level of hydrologic functions because it provides overbank storage during high flow events, and has a dense shrub vegetation community that functions to slow down Hydrologic water velocities during floods. Wetland 13 has high potential to provide these hydrologic functions because the stream is not downcut, the upstream contributing basin is largely developed, and flows upstream are not controlled by dams or other flow control devices. Wetland 13 provides a moderate level of water quality improvement functions because it has Water Quality surface depressions that trap sediments during flood events, and dense shrub vegetation that can remove sediment and excess nutrient/toxicants. Erosion control and shoreline stabilization are also provided, as the wetland is located along a watercourse. Wetland 13 provides a low to moderate level of biological and habitat functions. Production/export of organic matter is provided to a moderate degree, as deciduous plants and Habitat surface flows through the wetland increase the potential of the wetland to provide this function. Wetland 13 has shrub habitat, and is situated within a ravine that provides refuge from roadways or other disturbances. Wetland vegetation includes a patch of nonnative, invasive Japanese knotweed (Polygonum cuspidatum). Buffer Condition Wetland 13 is situated along West Fork Hylebos Creek within a steep ravine, and the upland buffer includes secondary -growth, mixed deciduous and evergreen forest habitat with a shrub understory. Gethsemane Cemetery 20 February 25, 2016 Wetland and Stream Assessment Report J I Table 3-15. Wetland 14 Summary. WETLAND 14 — INFORMATION SUMMARY Location: Emergent wetland on Parcel No. 322104-9025 Local Jurisdiction City of Federal Way WRIA 10 Ecology Rating III (Hruby, 2014) Federal Way Rating III Federal Way Buffer Width 60 feet Wetland Size 0.07 acre Cowardin Classification PEM HGM Classification Depression R Wetland Data Sheet(s) 19 Upland Data Sheet (s) 20 Flag color Pink/Black Stripe Dominant Phalaris arundinacea Vegetation Soils Clay loam, 10YR 4/2 with redoximorphic concentrations stating at 4 inches depth. Hydrology Receives hydrology from high groundwater, stormwater runoff, and precipitation. Rationale for Satisfies all three wetland criteria. Delineation Rationale for Follows Ecology rating system (Hruby 2014) per FWRC 19.145.420. Local Rating Wetland Functions Summary Wetland 14 provides a moderate level of hydrologic functions because it has no outlet, a small Hydrologic contributing basin, and retains water during storm events and wet periods. These functions are valuable to surrounding communities due to flooding that occurs lower in the Hylebos Creek basin. Wedand 14 provides a low to moderate level of water quality improvement functions because it retains water due to the lack of an outlet, and has dense herbaceous vegetation that removes Water Quality sediment and excess nutrient/toxicants. Wetland 14 receives stormwater runoff from an adjacent gravel roadway, which increases the potential of the wetland to trap toxicants and improve water quality. Wedand 14 provides a low level of biological and habitat functions. Wedand 14 is adjacent to a gravel road and hay field, which limits its use by wetland -associated wildlife. The southwest edge of Habitat the wetland is bordered by a barbed wire fence. Wetland vegetation is dominated by non-native, invasive reed canarygrass, which limits the establishment of native vegetation. The buffer west and south of Wetland 14 includes a gravel roadway and hay field, which is mowed regularly. The buffer east and north of Wetland 14 is a steep slope dominated by Himalayan Buffer Condition blackberry (Rebus americanus). A second -growth, mixed deciduous and evergreen forest abuts the southeastern edge, and has a dense understory of Himalayan blackberry within 150 feet of the boundary of Wetland 14. Gethsemane Cemetery 21 February 25, 2016 Wetland and Stream Assessment Report Soils Soil units mapped within the study area include Alderwood gravelly sandy loam, Bellingham silt loam, Kitsap silt loam, and Norma sandy loam (Table 3-16). The majority of Gethsemane Cemetery is mapped as Kitsap silt loam. The NRCS soils map is provided as Figure 4 in Appendix B. Table 3-16. NRCS Soil Units Mapped on the Gethsemane Cemetery Property - Soil Series Slope % Drainage Class Parent Material Depth to Water Table (inches) Alderwood gravelly 6-15, and Glacial drift / glacial 18-37 sandy loam 15-30 Moderately well drained outwash over dense glaciomarine deposits Bellingham silt loam 0-2 poorly drained Alluvium 0-12 and 2-8 and Lacustrine deposits with a 18-36 Kitsap silt loam 15 Moderately well drained minor amount of volcanic ash Norma sandy loam 0-2 poorly drained Alluvium 0 During the delineation, wetland soils were observed to generally consist of a low-chroma matrix with common, faint to prominent redoximorphic features occurring as soft masses or along pore linings. Matrix colors documented in wetlands generally included black (10YR 2/1), very dark grayish brown (10YR 3/2), and dark grayish brown (10YR 4/2). Redoximorphic features consisted of common, dark yellowish brown (10YR 4/6 and 5/6) concentrations along pore linings and depletions (10YR 5/1 and 4/2) within 8 inches of the soil surface in the soil profile. Surface soil textures consisted of loam, silt loam, and clay loam. Mixed soil matrices were also observed due to the history of land disturbance in the study area. The two most commonly used hydric soil indicators during the delineation were F3 (Depleted Matrix) and F6 (Redox Dark Surface) (USACE 2010). Upland soil profiles typically have a lighter matrix (10YR 3/3, 7.5YR 5/3), or similarly very dark grayish brown (10YR 3/2) matrix as wetland soils but with redoximorphic features beginning approximately 16 inches below the soil surface. Vegetation Wetlands on the Gethsemane Cemetery property have forest, shrub, and emergent vegetation communities. Forest and shrub wetland vegetation communities occur in the floodplain of West Fork Hylebos Creek, and emergent and shrub wetland vegetation communities occur along property boundaries west of West Fork Hylebos Creek. Gethsemane Cemetery 22 February 25, 2016 Wetland and Stream Assessment Report I Forested wetlands are typically dominated by a canopy of red alder j lnus rubra, FAC) and black cottonwood (Populus balsamifera spp. trichocarpa, FAC), with a shrub understory of salmonberry (Rebus spectabilis, FAC), redstem dogwood (Cornus sericea, FACW), Sitka willow (Salix sitchensis, FACW), and Himalayan blackberry (Rebus armeniacus, FACU). Herbaceous vegetation in the forested wetlands includes slough sedge (Carex obnupta, OBL), small -fruited bulrush (Scirpus microcarpus, OBL), western skunk cabbage (Lysichiton americanus, OBL), and common horsetail (Equisetum arvense, FAC). Herbaceous vegetation in the emergent wetland vegetation communities includes soft rush (Tuncus eusus, FACW), reed canarygrass (Phalaris arundinacea, FACW), and colonial bentgrass jgrostis capillaris, FAC). Upland forest vegetation included Douglas fir (Psuedotsuga mentiesat,. FACU), Western red cedar (Thuja plicata), red alder, big -leaf maple j cer macrophyllum, FACU), common snowberry (Symphoricarpos alba, FACU), vine maple (1 cer cininatum, FAC), Himalayan blackberry, red elderberry (Sambucus racemosa, J FAC), osoberry (Oemleria cerasiformis, FACU), and sword fern (Pnlystii-bum munitum, FACU). Upland meadows typically had a mix of bentgrass, reed canarygrass, bluegrass (Poa sp., NI), and ryegrass (Lolium perenne, FAC). See Appendix E for a list of plant species observed in the study area. Hydrology IThe delineated wetlands drain to West Fork Hylebos Creek. Wetlands were classified as riverine, 1 depressional, and slope per the HGM classification system. The riverine wetlands (Wetlands 4, 5, and 7-13) along West Fork Hylebos Creek are periodically inundated by overbank flooding. Many of these riverine wetlands also receive surface water from groundwater seeps on slopes in the ravine. Wetland hydrology in depressional wetlands (1, 3, 6, and 14) is supported by high groundwater, precipitation, and stormwater runoff. Wetland 14 is in a depression with no surface water outlet. Wetland 2 is a slope wetland in a roadside ditch that collects surface runoff from SR 99 and discharges to Wetland 1. 3.2.4 Wetland Functions Wetland functions were evaluated using the Ecology's 11lashington State Wetland Rating System for Western Wlashington (Hruby, 2014). Wetland functions were assessed according to three groups of functions: hydrologic (reduce flooding and stream degradation), water quality improvement, and habitat. All wetlands were categorized as Category II or III. Wetland rating forms and figures are provided in Appendix D (Ecology Rating Forms). HGM classes of wetlands in the study area include depressional, slope, and riverine. Depressional and riverine wetlands provide moderate to high levels of water quality, hydrologic, and habitat functions, whereas as slope wetlands provide low to moderate levels of these wetland functions. Riverine and depressional wetlands directly associated with West Fork Hylebos Creek provide the J Gethsemane Cemetery 23 February 25, 2016 Wetland and Stream Assessment Report highest level of wetland functions due to the flooding problems lower in the Hylebos Creek basin and the salmonid resources in the Hylebos Creek watershed. The storage capacity and water quality functions provided by depressional wetlands is valuable to society due poor water quality in West Fork Hylebos Creek, and the flooding problems lower in the basin near the confluence with the main stem of Hylebos Creek near Interstate-5. West Fork Hylebos Creek is listed on Washington State's list of impaired waters [303(d) list] for bacterial exceedances. Riverine wetlands along West Fork Hylebos Creek provide a moderate degree of sediment and nutrient/toxicant removal due to dense vegetative communities, shallow inundations that can capture sediment, and frequent interactions during flood events. Wetland habitat functions were rated the highest in Wetland 1 (Unit 3) and Wetland 6 due to the interspersion and variety of wetland habitats (PFO, PSS, PEM), wetland habitat association with West Fork Hylebos Creek, and special habitat features (e.g., snags; large, downed woody debris; lack of invasive plant species, and plants overhanging the creek). All other wetlands were rated low to moderate for habitat functions. The potential of the surrounding landscape to support wetland habitat functions is rated medium to low due to the extent of development in the surround areas. Wetland functions for individual wetlands are summarized in Table 3-1 on page 6 of this report, and also provided in the wetland profiles in Tables 3-2 to 3-15. 3.2.5 Wetland Buffers Wetland buffer habitat around Wetlands 1, 2, 3, and 14 is disturbed due to regularly mowed lawns, roads, and maintained grass meadows. Wetland 1 is bordered to the south by a grass meadow that includes reed canarygrass, colonial bentgrass, bluegrass, and ryegrass, with small shrub patches consisting of Nootka rose (Rosa nutkana) and Himalayan blackeberry. Non-native, invasive plant species present include Canada thistle (G4,wx arvense) and Himalayan blackberry. Wetland 2 is a roadside ditch, and is bordered to the west by SR 99 and to the east by mowed lawn. Buffer habitat around Wetland 3 includes a commercial trucking facility and parking lot to the south, SR 99 to the west, mowed lawn to the north, and upland forest with Douglas -fir trees to the north east. Wetland 14 is bordered to the north, east, and south by a Himalayan blackberry thicket, and a gravel road abuts the southern edge. Buffer habitat adjacent to Wetlands 4-13 is primarily forested. Wetlands 4, 5, and 7-13 are located along West Fork Hylebos Creek in a ravine, and the forested buffer protects water quality in the creek as well as the habitat functions provided by these riverine wetlands. The canopy in these forested buffers includes big -leaf maple, Douglas -fir, and Western red cedar. The buffer along the western edge of Wetland 6 in the study area also includes a forested steep slope, which is dominated by red alder trees. Per FWRC (19.145.420), wetland buffer widths are based on wetland categories and the habitat scores from the 2014 Wlashington State lrletland Rating System for Western Wlashington (Hruby, 2014). As Gethsemane Cemetery 24 February 25, 2016 Wetland and Stream Assessment Report such, Wetlands 3 and 14 have a buffer width of 60 feet, and Wetlands 4-13 have a buffer width of 165 feet. Wetland 2, artificially created in a roadside ditch along Pacific Highway South, is exempt I from the FWRC per Chapter 19.145.110(3), and does not have an associated buffer. Wetland 1 was divided into three separate units for categorization and rating purposes based on changes in hydrology. Wetland 1 (Unit 1) has a 165-foot buffer; Wetland 1 (Unit 2) has a 105-foot buffer; and 1 Wetland 1 (Unit 3) has a 165-foot buffer. See Table 3-1 on page 6 of this report for a summary of wetland characteristics, Ecology categories, habitat function scores, and associated buffer widths. 3.3 Streams Three watercourses were identified on the Gethsemane Cemetery property: two constructed stormwater features, and West Fork Hylebos Creek. West Fork Hylebos Creek flows south through f steep -sided ravine in the center of the property east of the developed portion of the cemetery (Appendix B - Figure 7). The West Fork Hylebos system is a riffle -pool system, with a substrate characterized by dominant gravel component and subdominant fine component. Representative bankfull widths and bankfull depths averaged 20 feet and 3.5 feet, respectively. During the fieldwork, representative wetted widths and wetted depths averaged 11 feet and 0.5 feet, respectively. Large woody debris (LWD) appears abundant, measured at 12 pieces per 100 feet (LWD diameters at 12-inches or more). Riparian habitat and canopy consists of forested and shrub habitat comprised primarily of western red cedar, red alder, salmonberry, and vine maple. 1 Riverine wetlands are situated along portions of the stream edges in the ravine (Wetlands 4, 5, and 7- 13), and at the mouth of ravine (Wetland 6). West Fork Hylebos Creek is classified as Type F (fish 1 habitat) per FWRC 19.145.260, and has a 100-foot buffer from the OHWM per FWRC 19.145.270. Additional watercourses include a stream segment in the roadside ditch east of SR 99 that connects Wetlands 1 and 2, and an intermittently flowing stream that discharges from a stormwater outfall to Wetland 6 (Figure 7). Both of these watercourses flow ephemerally following precipitation events. They are manmade, but because they have an OHWM and drain to regulated wetlands, they are assumed to be regulated by the USACE. These intermittent watercourses are classified as Type Ns (seasonal non -fish habitat) per FWRC 19.145.260, but do not have associated buffers because they are artificially created in uplands and are exempt from FWRC per Chapter 19.145.110(3).. The wetlands that these two watercourses discharge to do not have surface water connections to West Fork Hylebos Creek, and preclude fish populations from using these watercourses. 3.4 Sensitive Plants, Fish, and Wildlife Several sensitive fish species are known to occur in West Fork Hylebos Creek in the study area, including: chum salmon (Oncorhynchus keta), winter steelhead (Oncorhynchus mykiss), coho salmon (Oncorhynchus kisutch), Pink salmon (Oncorhynchusgorbuscha), and Chinook salmon (Oncorhynchus tshanytscha). Breeding habitat for fall chum and coho salmon have also been identified in West Fork Hylebos Creek (WDFW 2016). Puget Sound winter -run steelhead distinct population segments Gethsemane Cemetery 25 February 25, 2016 Wetland and Stream Assessment Report :=i (DPS) and fall -run evolutionarily significant unit (ESU) Chinook salmon are listed as threatened under the Endangered Species Act (ESA) in King County, and all fish species are listed as priority species by Washington Department of Fish and Wildlife (WDFW). No designated critical habitat for ESA -listed species was identified as occurring within or near the project vicinity. Pacific pond turtle (1 ctinemys marmorata) is known to potentially occur in aquatic habitats within the vicinity (<0.5 mile) of the study area, and is state -listed as Endangered. It is not a federally -listed species under ESA. No sensitive plant species are known to occur within or near the vicinity of the Gethsemane Cemetery. WDFW priority habitats that occur or may occur in the project vicinity (<0.5 mile) include freshwater forested/shrub wetlands, freshwater emergent wetlands, and freshwater pond (WDFW 2016). 3.5 Regulatory Summary Wetlands and streams on the Gethsemane Cemetery property are regulated by federal (USACE), state (Ecology and WDFW), and local (Federal Way) agencies. Wetland and stream buffers are regulated by the City of Federal Way and Ecology. Impacts to wetland and streams and their buffers require prior authorization and coordination with regulatory agencies. 3.5.1 U.S. Army Corps of Engineers The USACE regulates wetlands, streams, and other drainages under Section 404 of the Clean Water Act. The USACE requires notification for all disturbances to wetlands, streams, and potentially to other drainages, such as roadside ditches. The USACE automatically asserts jurisdiction over some surface waters and will need to complete a "significant nexus" determination for others, depending on the degree of connection to other waters, the classification of these associated waters, and their significance in the larger drainage basin. It is anticipated that the USACE will regulate the discharge of fill material into all wetlands, streams, and ditches on the Gethsemane Cemetery property due to surface and subsurface hydrological connectivity to West Fork Hylebos Creek, which drains to Commencement Bay. 3.5.2 Washington State Department of Fish and Wildlife WDFW requires issuance of a Hydraulic Permit Approval (HPA) prior to any activities that may directly or indirectly affect streams or associated wetlands. WDFW is anticipated to have jurisdiction over West Fork Hylebos Creek, and stream -associated wetlands. An HPA may be required for any work near the creek and riparian corridor, and potentially on other wetlands on property if impacts could potentially alter the hydrology in the associated stream corridor. Gethsemane Cemetery 26 February 25, 2016 Wetland and Stream Assessment Report 1 3.5.3 Washington State Department of Ecology Ecology regulates activities in wetlands and streams under Section 401 of the Clean Water Act through the Water Quality Certification process. Ecology has authority over discharge into all wetlands and streams, and can impose buffers and compensatory mitigation for impacts under Revised Code of Washington (RCW) 90.48. 3.5.4 City of Federal Way The City of Federal Way regulates wetlands and streams and their associated buffers through Chapter 19.145 (Environmentally Critical Areas) of the FWRC. All wetlands and streams on the Gethsemane property are regulated by the City of Federal Way except for Wetland 2 and the two k intermittent streams because these features were artificially created in uplands [FWRC k 19.145.110(3)]. Activities that modify wetlands or streams or their buffers require a critical areas report that adequately evaluates the proposed action and probable impacts. Additional compensatory mitigation actions may be necessary to offset impacts to these regulated areas to be in compliance with FWRC Chapter 19.145. I J j 3.6 Mitigation Opportunities Local, state, and federal agencies require projects impacting wetlands, streams or their buffers to follow mitigation sequencing that includes measures to avoid, minimize, restore, and compensate for unavoidable impacts. It is incumbent on the applicant to show and document mitigation sequencing before alterations are approved. Other opportunities exist for offsetting impacts to wetland buffers per FWRC 19.145.440, including: buffer averaging, buffer reduction with enhancement, and buffer increases. Development within buffers may be approved if one of these permitting strategies is employed, and compliance with FWRC is achieved. Buffer mitigation opportunities exist on the Gethsemane Cemetery property through one or a combination of these methods. Gethsemane Cemetery 27 February 25, 2016 Wetland and Stream Assessment Report I I J Chapter 4. References Brinson, M.M. 1993. Hydrogeomorphic classification for wetlands. Technical Report. WRP-DE-4. 79 pp. Washington, D.C: U.S. Army Corps of Engineers, Wetlands Research Program. Cowardin, L.M., V. Carter, F. Golet, and E.T. LaRoe. 1979. Classification of wetlands and deepwater habitats of the United States. FWS/OBS-70/31. 131 pp. Washington, D.C: U.S. Fish & Wildlife Service, Office of Biological Services. Google Maps. 2015. Available at http://maps.google.com/, accessed October 23, 2015. Hruby, T. 2014. Washington State Wetland Rating System for Western Washington — 2014 Update. Washington State Department of Ecology Publication # 14-06-029. King County. 2015. King County GIS Center — King County GIS Data Portal. Available at ht wu7xv5.ki❑ counn.. ov sdata ortal , accessed October 29, 2015. Lichvar, R.W., M. Butterwick, N.C. Melvin, and W.N. Kirchner. 2014. Western Mountains, Valleys, and Coast: 2014 Regional Wedand Plant List. Phytoneuron 2014-41: 1-42. Natural Resources Conservation Service (MRCS). 2015. WETS Station — Seattle Tacoma INTL AP, WA 233. United Sates Department of Agriculture. Available at: http://www.wcc.nres.usda.gov/climate/navigate—wets.html, accessed November 10, 2015. NRCS. 2015. Web Soil Survey. United States Department of Agriculture. Available online at http://websoilsurvey.nres.usda.gov/., accessed December 2011. NRCS. 2015. The PLANTS Database (last updated October 19, 2015). National Plant Data Team, Greensboro, NC. United States Department of Agriculture. Retrieved October 2015, from http://plants.usda.gov. U.S. Army Corps of Engineers (USACE). 1987. Corps of Engineers Wetland Delineation Manual. Technical Report. Y-87-1. Vicksburg, Mississippi: U.S. Army Corps of Engineers Environmental Laboratory. USACE. 2010. Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Western Mountains, Valleys, and Coast Region, Version 2.0, ed. J.S. Wakeley, R.W. Lichvar, and C.V. Noble. ERDC/EL TR-10-3. Vicksburg, Mississippi: U.S. Army Engineer Research and Development Center. U.S. Fish and Wildlife Service (USFWS). 2016. National Wetlands Inventory website. U.S. Department of the Interior, Washington D.C. Available at: http://www.fws.gov/wetlands Washington Department of Fish and Wildlife (WDFW). 2016. PHS on the Web. Available online at htm�l2l2s.wdfiy.■v,a.ggv/phson.tic ave , accessed on January 4, 2016. Gethsemane Cemetery 28 February 25, 2016 Wetland and Stream Delineation Report J Appendix A Methods and Tools Table A-1. Methods and Tools Used to Prepare the Report. Parameter Method or Tool Website Reference Wetland Delineation WSDOT Delineation Guidance Documents http://www.wsdot.wa.gov/E Website nvironment/Biolo /Wetlan ds/Delineation.htm#DelinG uidDocs Corps of Engineers Wetlands Delineation Manual http:f/el.erdc.usace.army. mi U.S. Army Corps of Engineers. 1987. Corps of Engineers Wetland Delineation Manuel. Environmental Laboratory Wetlands Research Program Technical Report Y-87-1, U.S. Army Corps of Engineers, Engineer Waterways Experiment Station, Vicksburg, Mississippi. Ilel ubsl df/wlman87, df Regional Supplement to the Corps of Engineers Wetland Delineation Manual WMVC http://www.usace.armYmil/ U.S. Army Corps of Engineers. 2010. Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Western Mountains, Valleys, and Coast Region (Version 2.0), ed. J.S. Wakely, R. W. Lichvar, and C.V. noble. ERDC/EL TR-10-3. Vicksburg, MS: U.S. Army Engineer Research and Development Center. Portals/2/docs/civilworks/re oulatorylreg supplwest mt _finalsupr).odf Wetland Classification USFWS / Cowardin Classification System http://www.fws.goytnwi/Pub Cowardin, L. M., V. Carter, F. C. Golet, E. T, La Roe. 1979. Classification of wetlands and deepwater habitats of the United States. Government Printing Office, Washington, D.C. s Reports/Class Manua{/cl ass titiepg.htm Hydrogeomorphic Classification (HGM) System htt ://el.erdc.usace.arm ,mi Brinson, M. M. (1993). "A hydrogeomorphic classification for wetlands," Technical Report WRP-DE-4, U.S. Army Engineer Waterways Experiment Station, Vicksburg, MS. NTIS No. AD A270 053. I/wetlandslpdfs/wrpde4.ndf Wetland Rating Washington State Wetland Rating System: Western WA httio://www.ecy.wa,00ylbibli Hruby. 2014. Washington State Wetland Rating System for Western Washington —2014 Update. Publication # 14-06-029. o/0406025.html Federal Way Revised Code (FW RC) http://www.codgpublishinc. Website. Requires compliance with FWRC (19.145.420) and use of 2014 Ecology rating system. comANA/FederalWay! Stream Delineation OHWM http:l/www.usace.army.ml(/ U.S. Army Corps of Engineers. 2014. A Guide to Ordinary High Water Mark (OHWM) Delineation for the Non -Perennial Streams in the Western Mountains, Valleys, and Coast Region of the United States, ed. M.K. Mersel and R.W. Lichivar. ERDCL/CRREL TR-14-13. Hanover, NH: U.S. Army Engineer Research and Development Center. Portals/2/docs/civilworks/re aulatory/rec sups/west mt Tfinalsum) aua2014.pdf OHWM http:/lwww.ecfr_govlccti- Congressional Federal Register 33 Part 328 Definition of Waters of the United States. bin/text- i d x?tpi =lecf rb rowse/Ti tle 33/ Gethsemane Cemetery February 25, 2016 Wedand and Stream Delineation Report �1 Parameter Method or Tool Website Reference 33cfr328 main 02.1I Stream Department of Forest Practices Water Washington Administrative Code (WAC) 222- Classification Natural Resources Typing: 16-030. DNR Water typing system. (DNR) Water htbx//www.stage.dnr.wa.go Typing System vlforestpracticeslwatertypin - 9 WAC 222-16-030: h ttp:lla p ps. l eg , wa. g ov/WA Cldefault.as x?cite=222- 16-030 Water Type Mapping, http://www3.wadnr.gov/dn r a 5/website/f arslviewer. htm Federal Way htto://www.codeoublishing. Federal Way Revised Code 19.145.260 of Revised Code comlWAlFederalWay! Article III (Fish and Wildlife Habitat Conservation Areas). Wetland Western htto:/lrsgisias.crrel.usace.ar Lichvar, R.W., M. Butterwick, N.C. Melvin, Indicator Mountains, Valleys, mv.milINWPLI and W.N. Kirchner. 2014. Western Status and Coast 2014 Mountains, Valleys, and Coast. 2014 Regional Regional Wetland Wetland Plant List. Phytoneuron 2014-41: 1- Plant List 42. Plant Names USDA PLANTS http://plants.usda.gov/ Website Database Report Federal Way http:liwww_codeoublishing. Federal Way Revised Code 19.145.080 and Preparation Revised Code comANAlFederalWavi 19.145.410. Soils Data Soil Survey Web Soil Survey: Websites htty:liwebsoi Isurvey.nres.us da. ov/a A(Veb5oilSurve .asap Soil Data Mart: h tty Flso i Id ata ma rt. n res. usd a•oov/ Threatened Washington Natural http://www.dnr.wa.clov/nhol Washington Natural Heritage Program (list and Heritage Program updated September 2014). Endangered, Endangered threatened, and sensitive plants of Species Washington. Washington State Department of Natural Resources, Washington Natural Heritage Program, Olympia, WA Threatened Washington Priority http://wdfw.wa.gov/hats/,phs Priority Habitats and Species (PHS) and Endangered Habitats and page_htm Program — August 2008 Washington State Species Species Priority Habitats and Species List. Website reviewed January 3, 2016. Gethsemane Cemetery February 25, 2016 Wetland and Stream Delineation Report Parameter Method or Tool (continued) NOAA fisheries species list and maps USFWS species lists by County Website htf ://www.nwr.noaa. ov)E Websites SA-Salmon- Listings/Salmon- Po p ulati onsll n d ex. cfm and htto:/lwww.nmfs. noaa.govl rip species/ King County: Website htt ://ecos.fws. ovftess pu blic/re orts/s ecies-b - current -range - county fips=53033 Gethsemane Cemetery Wedand and Stream Delineation Report Reference February 25, 2016 J I J Appendix B Project Figures and Background Information This appendix includes: ■ Figure 1: Vicinity Map ■ Figure 2: Site Map (aerial photograph) -■ Figure 3: Topography Map ■ Figure 4: NRCS Soils Map -■ Figure 5: National Wetlands Inventory Map '■ Figure 6: City of Federal Way Wetlands Map ■ Figure 7: Wetlands and Streams Delineation Map ■ Figure 7A: Wetland 1 Map in Figure 7B: Wetlands 2 & 3 Map in Figure 7C: Wetlands 4-5 and Wetlands 7-13 Map + Figure 7D: Wetland 6 Map ■ Figure 7E: Wetland 14 Map Gethsemane Cemetery February 25, 2016 Wetland and Stream Delineation Report St v, — a ° QitirT �4uaR MfotrW4n• x Lab P.nA '` N kriila 5tal5 Fark _ \%ash on Maplt- �Dn Des 1r.t11e+• SW343thSt a' Stryc 61hAoeS Dlnine5rttt N a project rnvingl nYY c o Federal Location Al bw o SW s J'V Univasity 349th Pi iaioissx Place y ant way t+E'� c` a .w., Ptnrallnp Bonn eV Enu, Lake"- Lakesaood Parkland . 3 Yyiac ak.6.n• jjJ Spanaway South 29th 5t NE . —SW 356thSt ¢ gW 396Yh St t"O" 9 3561h St - Hill Fort Levis M v.Yn hi 0ary Reservation _ � w -S 360th St z w ` z fA yaPa o a r.M'W.tu 4 s siau,st 6 4 L w � i� nr 1�. a :•�. a n Birch St o c e ill 4 � Qh 5t E Emeraid St n a a f C1 W L S W a L = Ott, 5t E w t o --Milton Milton Way L y Milton a' 1rm Sr r 5 fr'r a Pacific Hwy !; r p Taylor St E 201h St E - 20th St E - Yuma St 20th St E s Fi fe 4 fidS c T 24th St E - . . _ 3 6 26th St E �r9 � a — � � w 3 C Note: katltanc.e BIvoE. -Basemap provided byArcGIS Online. -All project specific data was made by Yr�c Otak, Inc Figure 1 Legend Vicinity Map Gethsemane Cemetary 1 inch = 3,000 feet Wetland Delineation on Gethsemane Feet Cemetary, Federal Way, WA 0 3,000 Y..inroiect1326007 326551CAp D1G I S%1XDs1FIg01 _ V,ci nity{Nap. mxd Date: 112712015 NRCS Soils �Kitsap silt loam, 15 to 30 Alderwood and Kitsap -soils, percent slopes very steep ®Kitsap silt loam, 2 to 8 Alderwood gravelly Mandy loam, 15 to 30 percent slopes =Norma sandy loam percent slopes =Pits Alderwood gravelly =Seattle muck ®sandy loam, 6 to 15 -Semiahmoo muck percent slopes KRWater -Bellingham silt loam FEDERAI i ' 7rHSTNE JOHNSON.R MILTON Figure 4 Legend NRCS Soils Map Gethsemane ry _ � _ � Jurisdiction Wetland Delineation on Gethsemane r Stream Lakes/Ponds Cemetary, Federal Way, WA 6 LJ r NNote: -Basemap provided by ArcGIS Online, -Municipal data is from City of Federal Way, -Soils data is from the NRCS Soils Survey Geographic Database. -All project specific data was made by Otak, Inc. 1 inch = 500 feet " Feet j — 0 500 KS,lpr eoftU6OM3M51CADMGI"XDsTI904 Soals-mxd Date: 1 /27/20 _J 5 6 3 4 Wetland 1 ti �1 9 is .. Note: Basemap provided by ArcGIS Online. -Municipal and wetland data is from City of Federal Way. -All project speck data was made by j 1 Otak, Inc. Figure7A Legend Wetland 1 Map .... Estimated Wetland Gethsemane _ Ordinary High Boundary Cemetary Water Delineated Wetland Culvert (approx. 1 inch = 100 feet Boundary Wetland Delineation on Gethsemane - Wetland Area x location) Data Point Feet Cemetary, Federal Way, WA !<. --tixl o goo K:%prvjectt32WW265$ CADDr GISWXOsW o7A—woand1 rnxd Dale: 2177416 {1J We. lancl'1 W@tIgn— '2 r 1 4 7 8 - x Note: HIIeHand'3 •Bawrnap provided byArcGIS Online. -Munlapal and wetland data is from City of Federal Way. All project specific data was made by . Otak, Inc FigureM Legend Wetlands 2 and 3 Map .... Estimated Wetland Gethsemane _ _ Ordinary High Boundary Cemetery Water I Delineated Culvert (approx. 1 inch = 100 feet Wetland Boundary location) Wetland Delineation on Gethsemane r' , Cemetary, Federal Way, WA - u Wetland Area x_i DataPoint 0 100 eet K)proiect1326001326551CAt7D%GISUAXDs4Flg078_WetlanQ&3.mxd Dale: 21112016 I I j I j j rr..r�r T Note. -Basemap provided byArcGIS Online. -Municipal and wetland data is from City of Federal Way. -All project speck data was made by Otak, Inc. Figure7D Legend Wetland 6 Map .... Estimated wetland Gethsemane Boundary Cemetary Delineated Wetland Ordinary High Water �— : •.- - Boundary 1 inch = 100 feet Wetland Delineation on Gethsemane •,_,.;, Wetland Area F—�Ml;Q (7(j Data Point Feet Cemetary, Federal Way, WA ! 0 100 A Note: -Basemap provided byArcGIS Online. -Municipal and wetland data is from Cily of Federal Way. -All pro)ecl specific data was made by 010. Inc. Figure7E Legend Wetland 14 Map ... Estimated wetland Gethsemane Boundary Cemetary Delineated Wetland x ' Data Point Boundary 1 inch = 100 feet Wetland Delineation on Gethsemane Feet Cemetary, Federal Way, WA i' ,.,, Wetland Area 0 100 z_.,..,..,xaycnrnaeaciarnnrnnic��avnetr�.n�c ., 1 gate: 2/1/2016 Appendix C —Wetland Determination Data � Forms J I Gethsemane Cemetery February 25, 2016 JWetland and Stream Delineation Report WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Federal WayiKincr Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 1 Investigator(s): Jeff Gra y and Kevin O'Brian Section, Township, Range: S32. T21N, 44EE Landform (hillslope, terrace, etc.): depression Local relief (concave, convex, none): concave Slope (%): 0=2 Subregion (LRR): A Lat: - Long: - Datum: Soil Map Unit Name: Betlin ham silt loam NWI classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) iUMMARY OF FINDINGS — Attach site map showing samplinq point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ Hydric Soil Present? Yes ® No ❑ Is the Sampled Area Yes ® No ❑ within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: All three wetland indicators present. Data point located 10' north of flag Al2. VtGt I A I IVN — use scienimc names OT Ianrd Tree Stratum (Plot size: 30' radius) Absolute %Cover Dominant Spec les7 Indicator Status Dominance Test Worksheet: 1. Sa6x sftGhensis 15 ves FACW Number of Dominant Species 3 (A) That Are OBL, FACW, or FAC: 2 3. Total Number of Dominant 3 (B) 4. � _— Species Across All Strata: 50% = 7_5, 20% = 3 15 = Total Cover Percent of Dominant Species 100 (A/B) $spling/Shrub Sualtum (Plot size: IV radlus) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Satix sfthensis 85 ves FACW 2. Rubus specfebjff 8 no FAC Total % Cover of: Multiply bV7 3 OBL species x1 = 4 FACW species x2 = 5 FAC species x3 = 50% = 46.5, 20% = 18.6 93 = Total Cover FACU species x4 = Herb Stratum (Plot size: F r• adius) UPL species x5 = 1. Phalaris agunj area 55 Les FACW Column Totals: (A) (B) 2. Eauisetum ervense 10 3. Athyrium fifix-femina WR. CY00s0lom 5 4. 5. 6. 7. 8. 9. 10. 11. 50% = 35, 20% = 14 70 Woody Vine Stratum (Plot size: 10'radius) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum 25 59' wale Remarks: Hydrophytic vegetation indicator present no no = Total Cover = Total Cover FAC FAC Prevalence Index = B/A = Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' El data - Morphological Adaplations' (Provide supporting data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes ® No ❑ US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemete SOIL Samnlinn Pnint• 1 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc2 Texture Remarks 00=3 10YR 2/1 100 silt loam 3-14 10YR 3/1 100 10YR 4/6 3 C M sill loam 14-20+ 10YR 5/1 90 10YR 4/6 10 C M clay loam 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ® Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Hydric soil indicator F6 present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ® Surface Water (Al) ❑ Water -Stained Leaves (69) ❑ Water -Stained Leaves (B9) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) (MLRA 1, 2, 4A, and 413) ® Saturation (A3) ❑ Salt Crust (1311) ® Drainage Patterns (B10) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (1313) ❑ Dry -Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-Neutral Test (D5) ❑ Surface Soil Cracks (66) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost -Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ® No ❑ Depth (inches): 2 Water Table Present? Yes ® No ❑ Depth (inches): 10 Saturation Present? Yes ® No (includes capillary fringe) ❑ Depth (inches): 8 Wetland Hydrology Present? Yes ® No ❑ Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: Wetland hydrology indicators present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Federal WavlKino Sampling Date: 11/5/15 Applicant/Owner: Archdiocese or Seattle State: WA Sampling Point: 2 Investigator(s): Jeif Gray and Kevin O'Br en Section, Township, Range: S32, T21N. R4E l Landform (hillslope, terrace, etc.): hillslooe Local relief (concave, convex, none): none Slope (%): 2-5 II Subregion (LRR): A Lat: - Long: = Datum: - Soil Map Unit Name: Bellingham sill loam NWI classification: ; Are climatic / hydrologic Are Vegetation ❑, conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ j Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) J SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transepts, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H drip Soil Present? Yes ❑ No ® Is the Sampled Area Y within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point not in a wetland; all three wetland indicators not present. Data point located 10' south of flag Al2. VEGETATION — Use scientific names of plants Absolute Dominant Indicator Tree Stratum Plot size: 30' radius ( ) % ver S eedes? Status 1. _ — 2. — 3. — 4. — 50% = 20% _ = Total Cover Saplingtftub Stratum (Plot size: 15 radiu ) 1. BkLas arms iac s 10 no FACU 2. Salix silchensis 40 ves FACW 3. Sambucus raeemosa 5 no FACU 4. — 5. — 50% = 27 5 20% = 11 55 = Total Cover Herb Stratum (Plot size: ' radlus) 1. phataris arundi ee 75 yes FACW 2. EEr urselum arvense 25 ,Les FAC 3. — 4. — 5. 6. — 7. — 8. 9. — 10. 11. — —� 50% = 50, 20% = 20 100 = Total Cover Woody Vine Stratum (Plot size: 1 ' radius) 1. - 2. 50% = 20% _ = Total Cover % Bare Ground in Herb Stratum 0 Remarks: Hydrophytic vegetation indicator present Yes ❑ No Dominance Test Worksheet: Number of Dominant Species 3 That Are OBL, FACW, or FAC: Total Number of Dominant 3 Species Across All Strata: Percent of Dominant Species 100 That Are OBL, FACW, or FAC: (A) (B) (A/B) Prevalence Index worksheet: Total % Cover of: Multiply by: OBL species x1 = FACW species x2 = FAC species x3 = FACU species x4 = UPL species x5 = Column Totals: (A) (B) Prevalence Index = B/A = Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' - Morphological Adaptations' (Provide supporting El data data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes Present? No ❑ US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 Project Site: Gethsemane Cemetery Ramnlinn Pnint• 2 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc2 Texture Remarks 0-18 2.5 Y 5/3 100 _ _ SCL exture: saftdy clay loam 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (At) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water l able (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (1313) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches) Water Table Present? Yes ❑ No ® Depth (inches) Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (139) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (1310) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) Saturation Present? Yes ❑ No ® Depth (inches): Wetland Hydrology Present? Yes ❑ No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available Remarks: No wetland hydrology indiactors present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Federal WavliCinq Sampling Date: 11/5/15 Applicant/Owner: Archd€ecese of Seattle State: WA Sampling Point: 3 Investigator(s): Jeff Gray and Kevin O'Brlen Section, Township, Range: S32. T21N._R4E Landform (hillslope, terrace, etc.): Depression Local relief (concave, convex, none): concave Slope (%): 0=2 Subregion (LRR): A Lat: _ Long: = Datum: Soil Map Unit Name: Belli n ham silt loam NW I classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ® No ❑ Is the Sampled Area Yes ® No ❑ y within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: All three wetland indicators present. Data point located 8' west of flag A18. VEGETATION — Use scientific names oT piants Tree 5lratum (Plot size: 30' radius) Absolute 90 Cover Dominant Sgeeies? Indicator Status Dominance Test Worksheet: 1. _ Number of Dominant Species 2 (A) 2 That Are OBL, FACW, or FAC: 3. Total Number of Dominant 3 (B) 4. Species Across All Strata: 50% = 20% _ = Total Cover Percent of Dominant Species 66.7 (A/B) SanlinalShruh Stratum (Plot size: 15' r ' That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Rubus amreniecus 2 ves FACU 2 Total % Cover of: Multioly bw 3 OBL species x1 = 4. FACW species x2 = 5. FAC species x3 = 50% = 1, 20% = <1 2 = Total Cover FACU species x4 = Herb Stratum (Plot size: 5 radius) UPL species x5 = 1. Phalaris arundinacee 73 yg-s FACW Column Totals: (A) (B) 2. Cirsium arvense 2 no FAC Prevalence Index = B/A = Hydrophytic Vegetation Indicators: 3. Agro0s caniilaris 25 Les FAC 4 ❑ 1 — Rapid Test for Hydrophytic Vegetation 5 ® 2 - Dominance Test is >50% 6. ❑ 3 - Prevalence Index is <3.0' 7. 4 - Morphological Adaptations' (Provide supporting ❑ data in Remarks or on a separate sheet) 8 g ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. 'Indicators of hydric soil and wetland hydrology must 50% = 50, 20% = 20 100 Total Cover be present, unless disturbed or problematic. Woody, Vine Stratum (Plot size: 10' radius) 1. - �^ Hydrophytic 2. Vegetation Yes ® No ❑ 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 0 Remarks: Hydrophytic vegetation indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SOIL Sampling Point:3 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture Remarks 0=8 10YR 4/2 100 f clay loam 8-18+ 10YR 4/2 85 10YR 4/6 8 C M silty clay 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. ZLocation: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (All) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ® Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ElSandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must e present, unless disturbed or probll ematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Remarks: Hydric soil indicator F3 present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (B9) ® High Water Table (A2) (except MLRA 1, 2, 4A, and 46) ® Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (131) ❑ Aquatic Invertebrates (1313) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (67) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ® No Saturation Pres t? ❑ Depth (inches): 4 Yes ® No ❑ Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (69) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (1310) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) en . Yes ® No ❑ Depth (inches): 3 Wetland Hydrology Present? Yes ® No ❑ (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: Wetland hydrology indicators present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemete City/County: Federal WavlKing Sampling Date: 11/5115 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 4 Investigator(s): Jeff G ra y and Kevin O'S 6en Section, Township, Range: S32. T21N. R4E Landform (hillslope, terrace, etc.): terrace Local relief (concave, convex, none): none Slope (%): 0=2 Subregion (LRR): A Let: = Long: - Datum: _ Soil Map Unit Name: Bellingham !Ot_loam NWI classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ Hydric Soil Present? Yes ❑ No ® Is the Sampled Area Yes ❑ No within a Wetland? Wetland Hydrology Present? Yes ❑ No KemarKS: uaia point not iocatea wnnm a weumw, au tn— ,,...,,——....o... r•••••• ••••••••-•• - ---. _.. _a -- VEGETATION - Use scientnic names oT plants Tree Stratum (Plot size: 30' radius) Absolute Dominant indicat % Cover Soecles? Status 2. — 3. 4. 50% = 20% _ Saollnc/Shr0 Stratum (Plot size: 1 ' radius) 1. Rubus armeniacus 8 2. 3. 4. 5. 50% = 4, 20% = 1_6 8 Herb Sirat4m (Plot size: 5' (adlus) 1. Phafar+s arundlnacea 15 2. Agrostis ca il7sris 80 3. Vrda emericana 5 4. 5. 6. 7. 8. 9. 10, 11. 50% = 50, 20% = 20 100 Stratum (Plot size: 10' ra i ) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum 0 Remarks: Hydrophytic vegetation indicator present = Total Cover ves FACU = Total Cover no FACW ves FAC no FAC = Total Cover = Total Cover Dominance Test Worksheet: Number of Dominant Species 1 That Are OBL, FACW, or FAC: Total Number of Dominant 2 Species Across All Strata: Percent of Dominant Species 50 That Are OBL, FACW, or FAC: — Prevalence Index worksheet: Total % Cover of: Multiply by: OBL species x1 = FACW species 15 x2 = 30 FAC species 85 x3 = 255 FACU species 8 x4 = 32 UPL species x5 = Column Totals: 108 (A) 317 (B) Prevalence Index = B/A = 2.93 Hydrophytic Vegetation Indicators: ❑ 1 - Rapid Test for Hydrophytic Vegetation ❑ 2 - Dominance Test is >50% ® 3 - Prevalence Index is <3.0' ❑ 4 - Morphological Adaptations' (Provide supporting data In Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes ❑ No Present? US Army Corps of Engineers Western Mountains, Valleys, and Coast - Version 2.0 Project Site: Gethsemane Cemetery SOIL Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc2 Texture 0-16 10YR 3/2 100 loam 16-20+ 10YR 4/2 82 10YR 4/6 8 C M silty clay 10YR 5/1 10 D M Point: 4 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Remarks Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or oroblematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicators present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 413) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (131) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (66) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ❑ No ❑ Depth (inches): Water Table Present? Yes ® No ❑ Depth (inches): 20 Saturation Present? Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (69) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (1310) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) (includes capillary fringe) Yes ® No ❑ Depth (inches): 18 Wetland Hydrology Present? Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: No wetland hydrology indicators present. Yes ❑ No US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: GoDsemane Cemelery City/County: Federal WaylKinq Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of_Sea tlle State: WA Sampling Point: 5 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: 532. T21N. R4E Landform (hillslope, terrace, etc.): hillsloo Local relief (concave, convex, none): co• ncaSlope (%): 2=5 Subregion (LRR): A Lat: = Long: _ Datum: Soil Map Unit Name: Norma sandy, loam NW I classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ Hydric Soil Present? Yes ® No ❑ Is the Sampled Area yes ® No ❑ within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: All three wetland indicators present. Data point located 8' NE of flag A31. VEGETATION — Use scienttttc names oT plants Tree Stratum (Plot size: 30' radius) Absolute Dominant Indicat I° Cover Species? Status 1. _ — 2. — 3. 4. — 50°/ = 20°/ _ = Total Cover o o Sa iin hruh tratum (Plot size: 1 5'radius) 1. - 2. 3. 4. 5. 50% _ , 20% _ Herb Stratum (Plot size: 5' ra i ) 1. cirsium arvenge 5 2, fl Krum cNaf m 15 3. P..ir ostis capfflaris 55 4. Vicia amedcapa5 5. Rumex onmus 5 6. Latium oerenrr 15 7. 8. 9. 10. 50% = 50, 20% = 20 100 WoodyyIne Stratu (Plot size: 10, ra i ) 1. _ 2. 50% _ , 20% _ % Bare Ground in Herb Stratum 0 Remarks: Hyrdophytic vegetation indicator present = Total Cover no FAC no FACW ves FAC no FAC no FAC no FAC = Total Cover Dominance Test Worksheet: Number of Dominant Species 1 That Are OBL, FACW, or FAC: — Total Number of Dominant 1 Species Across All Strata: Percent of Dominant Species 100 That Are OBL, FACW, or FAC: Prevalence Index worksheet: Total % Cover of: Multiply b OBL species A = _ FACW species x2 = — FAC species x3 = _ FACU species x4 = UPL species x5 = _ Column Totals: (A) — Prevalence Index = B/A = Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' ❑ 4 - MorphoiogicaT Adaptations' (Provide supporting data In Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. (B) Hydrophytic Vegetation Yes ® No ❑ = Total Cover Present? IUS Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 Project Site: Gethsemane Cemetery SOIL Samniinn Pnint• ti Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Locz Texture Remarks 0=7 10YR 3/2 100 loam 7-18 10YR 5/2 81 10YR 4/6 15 C M silt clay 10YR 4/1 4 D M 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ® Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ElRedox Depressions (F8) wetland hydrology must e present, unless disturbed or roblematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Hydric soil indicator F3 present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ Water -Stained Leaves (139) ® High Water Table (A2) (except MLRA 1, 2, 4A, and 46) (MLRA 1, 2, 4A, and 413) ® Saturation (A3) ❑ Salt Crust (B11) ❑ Drainage Patterns (610) ❑ Water Marks (131) ❑ Aquatic Invertebrates (1313) ❑ Dry -Season Water Table (C2) ❑ Sediment Deposits (82) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (64) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-Neutral Test (D5) ❑ Surface Soil Cracks (66) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Frost -Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ® No ❑ Depth (inches): 8 Saturation Present? (includes capillary fringe) Yes ® No ❑ Depth (inches): j Wetland Hydrology Present? Yes ® No ❑ Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Wetland hydrology indicators present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region J J J Project Site: Gethsernane_Cemeter City/County: Federal WayXing Sampling Date: 11/5115 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 6 Investigator(s): Jeff GraV and Kevin O'Brien Section, Township, Range: S32. T21N. R4E Landform (hillslope, terrace, etc.): hillslo a Local relief (concave, convex, none): none Slope (%): 2=5 Subregion (LRR): A Lat: _ Long: - Datum: Soil Map Unit Name: Norma sandy Ieam NW I classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ❑ No ® Is the Sampled Area Yes El No y within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point not located within a wetland; all three wetland indicators not present. Data point located 8' southwest of flag A31. VEGETATION — Use scientific names of plants 'free Stratum (Plot size: 30' ra ius) 1. _ 2. 3. 4. 50% = 20% _ lin hrub Stratum (Plot size: 15' radiu ) 1. Crateeaus monoama 2. 3. 4. 5. 50% = 2_5, 20% = 1 Herb Stratum (Plot size: 5' radius) 1. Aaresfls caoillaris 2. Lofi rye 3. Eaffoblurn eiliafum 4. Vicia americana 5. 6. 7. 8. 9. 10. 11. 50% = 50, 20% = 20 Woody Vine Stratum (Plot size: 10' radius) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum 0 Absolute Dominant Indicator Dominance Test Worksheet: % Cover Soecies? Status 5 = Total Cover ves FAC Number of Dominant Species 2 That Are OBL, FACW, or FAC: Total Number of Dominant 2 Species Across All Strata: Percent of Dominant Species That Are OBL, FACW, or FAC: 100 (A) (B) (A/B) Prevalence Index worksheet: _ Total % Cover of: Multiply by: OBL species x1 = FACW species x2 = FAC species x3 = 5 = Total Cover FACU species x4 = UPL species x5 = 65 ves FAC Column Totals: (A) (B) 20 ves FAC Prevalence Index = B/A = Hydrophytic Vegetation Indicators: 10 no FACW 5 no FAC ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' 4 - Morphological Adaptations' (Provide supporting ❑ data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ___ ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must 100 — = Total Cover be present, unless disturbed or problematic. Remarks: Hydrophytic vegetation indicator present. US Army Corps of Engineers Hydrophytic Vegetation Yes ® No ❑ = Total Cover Present? Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery 'L*" Samnlinn Pnint F, Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc2 Texture Remarks 0-14 10YR 3/2 100 loam 1414=18 2.5Y 4/2 90 10YR 4/6 8 C M silty clay 10YR 4/1 2 D M 18-22+ 10YR 5/2 80 10YR 4/6 15 C M silty clay 10YR 4/1 5 D M 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (172) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions F8 p ( ) wetland hydrology must e present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (131) ❑ Aquatic Invertebrates (1313) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (68) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ® No S t t' P t? ❑ Depth (inches): 18 Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) a ura ion resen . Yes ® No ❑ Depth (inches): 17 Wetland Hydrology Present? (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: No wetland hydrology indicators present. Yes ❑ No US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM —Western Mountains, Valleys, and Coast Region Project Site: Geth emane Cemet City/County: Federal Wavlltin�c Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 7 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32. T21N. R4E Landform (hillslope, terrace, etc.): Depression Local relief (concave, convex, none): con caVQ Slope (%): 0=2 Subregion (LRR): A Lat: - Long: = Datum: _ Soil Map Unit Name: Kilsap silt loam. 2-8016 slopes NW I classification: _ Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ Is the Sampled Hydric Soil Present? Yes ® No ❑ I within a Wetlar Wetland Hydrology Present? Yes ® No ❑ RCIIIGII�J. /'�11 a�„ca ��c�,o„u •„u,vuav,.a ,.. .......... —... ,. �...-.���-�_ ._ __ .i - _ VEGETATION — Use scientific names of plants Tree Stratum (Plot size: 30' radius) Absolute %Cover Dominant Species? indicator Status Dominance Test Worksheet: 1. _ Number of Dominant Species 3 (A) That Are OBL, FACW, or FAC: 2 3. Total Number of Dominant 3 (B) Species Across All Strata: 4 50% = 20% _ = Total Cover Percent of Dominant Species 100 (A/B) S tin IShrub Stratum ' (Plot size: 1 radius) That Are OBL, FACW, or FAC: 1. Fraxinus. /tif�olla 12 yes FACW Prevalence Index worksheet: 2. A er cifcinatyM yes FAC Total % Cover of: MUE i b 3. — OBL species x1 = 4 T FACW species x2 = 5 FAC species x3 = 50% = 6, 20% = 3_2 16 = Total Cover FACU species x4 = Herb Stratum (Plot size: 5' radius) UPL species x5 = 1. Pholads arondinaces 96 yes FACW Column Totals: (A) (B) 2. Jun as effuses 4 no FACW Prevalence Index = B/A = 3 Hydrophytic Vegetation Indicators: 4 — ❑ 1 — Rapid Test for Hydrophytic Vegetation 5 ® 2 - Dominance Test is >50% 6. ❑ 3 - Prevalence Index is <3.0' 7, ❑ 4 - Morphological Adaptations' (Provide supporting data In Remarks or on a separate sheet) 6 Y 9 ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. 'Indicators of hydric soil and wetland hydrology must 50% = 50, 20% = 20 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ' raditi I Hydrophytic 2. Vegetation Yes ® No ❑ 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 0 Remarks: Hydrophytic vegetation indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SOIL .q-1;.n Pnin4.7 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Locz Texture Remarks 0=4 10YR 4/2 100 clay loam 4-18 10YR 4/2 78 10YR 5/6 18 C PUM siltV clay 10YR 5/1 4 D M 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ® Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ElSandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Hydric soil indicator F3 present. U411:Ze7116Zd'1 Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ® Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) (MLRA 1, 2, 4A, and 413) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Drainage Patterns (1310) ❑ Water Marks (131) ❑ Aquatic Invertebrates (613) ❑ Dry -Season Water Table (C2) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (C1) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-Neutral Test (D5) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Frost -Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (BB) Field Observations: Surface Water Present? Yes ® No ❑ Depth (inches): 2 Water Table Present? Yes ® No ❑ Depth (inches): 0 Saturation Present? Yes ® No (includes capillary fringe) ❑ Depth (inches): 0 Wetland Hydrology Present? Yes ® No ❑ Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Wetland hydrology indicator present US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemi3tery City/County: Federal WaOKing Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 8 Investigator(s): Jeff GraVend _Kevin UBrien Section, Township, Range: S32. T21N. 1341E Landform (hillslope, terrace, etc.): hillslope Local relief (concave, convex, none): none Slope Subregion (LRR): A Lat: - Long: _ Datum: Soil Map Unit Name: Kltsap silt loam. 2-8% slope-$ NW I classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ dric Soil Present? Yes ❑ No ® Is the Sampled Area H y within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point not located within a wetland; not all three wetland indicators present. Data point located 8' northeast of flag C6. i Yes ❑ No 19 VCIOC I A I IVIY — use bUIVIIIIIIt; IIdrrItM UI Ian&-$ Tree Stratum (Plot size: 0' ius) Absolute Cover Dominant es? Indicator. Status Dominance Test Worksheet: 1. Pseuedotsyrta rnenzfesil 55�es FACU Number of Dominant Species 3 (A) 2 � � That Are OBL, FACW, or FAC: 3 Total Number of Dominant (B) 4 J Species Across All Strata: 50% = 27.6. 20% = 11 55 = Total Cover Percent of Dominant Species ° 43 /° (A/B) Sa lin lShrub Stratum (Plot size: 15' radius) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Rukus saeattabilis 15 Y�S_ FAC 2. Rubus armeniacus 10 Les FACU Total % Cover of_ Multiply by-, 3. oernleria cerasi(orrrafs 10 Les FACU OBL species 5 x1 = 5 4. Corylus cornula 5 no FACU FACW species 20 x2 = 40 5. Gaultheria shallon 10 des FACU FAC species 50 x3 = 150 50% = 25, 20% = 10 50 = Total Cover FACU species 90 x4 = 270 Herb Stratum_(Plot size: 5'radius) UPL species x5 = 1. Phalaris arundLriaGea 20 ves FACW Column Totals: 165 (A) 465 (B) 2. Carex obnunla 5 no OBL Prevalence Index = B/A = 2.82 Hydrophytic Vegetation Indicators: 3. Ecuiselum arvense 7 no FAC 4. T lmie�esu 8 nc FAC ❑ 1 — Rapid Test for Hydrophytic Vegetation 5. Poa oratensls 5 no FAC ❑ 2 - Dominance Test is >50% 6. Acroslis capHlois 10 yes FAC ® 3 - Prevalence Index is <3.0' 7, Cirsiam anrensg 5 no FAC - Morphological Adaptations' (Provide supporting El4 data in Remarks or on a separate sheet) 8 g, ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. 'Indicators of hydric soil and wetland hydrology must 50% = 30, 20% = 12 60 Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: 10' radlus) 1. - Hydrophytic 2 Vegetation Yes ® No ❑ 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 40 Remarks: Hydrophytic vegetation indicator present. j US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery, SOIL Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture 0-6 10YR 3/3 100 loam 6-18 2.5Y 4/3 70 silty clay 2.5Y 513 30 Sar1:-,krr, Point: 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Remarks Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or Droblematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No to Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (131) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No P � ® Depth (inches): Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (69) (MLRA 1, 2, 4A, and 41B) ❑ Drainage Patterns (610) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) Saturation resent. (includes capillary fringed Yes ❑ No ® Depth (inches): Wetland Hydrology Present? Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: No wetland hydrology indicators present. Yes ❑ No US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Federal WaylKing Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 9 Investigator(s): iefF Gray and Kevin O'Brien Section, Township, Range: S32. T21N, R4E Landform (hillslope, terrace, etc.): hillside Local relief (concave, convex, none): concave Slope (%): 5=8 Subregion (LRR): A Lat: = Long: - Datum: Soil Map Unit Name: Norma sandy loam NWI classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ® No El within the Sampled Area Yes [I No y within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point not in a wetland; not all three wetland indicators present. Data point located at flag DP1. VEGETATION — Use scientific names of Tree Stratum (Plot size: 30' radius) 1. - 2. 3. 4. 50% = 20% _ Saplln,g0hrub Stratum (Plot size: 15 radius) 1. Rosa nootkana 2. 3. 4. 5. 50% = 2_5. 20% = 1 Herb Stratum (Plot size: radi ) 1. Poa nralensiS 2. Lolium perenne 3. Clrsium arvanse 4. Vicia americana 5. 6. 7. 8. 9. 10. 11. 50% = 50, 20% = 25 Woody Vine Stratum (Plot size: 10' radius) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum 0 Absolute % Cover 5 Dominant lnoicator Species? Status = Total Cover yes FAC Dominance Test Worksheet: Number of Dominant Species 3 That Are OBL, FACW, or FAC: — Total Number of Dominant 3 Species Across All Strata: — Percent of Dominant Species 100 That Are OBL, FACW, or FAC: Prevalence Index worksheet: Total % Cover of: tiM hiply by: OBL species x1 = _ FACW species x2 = FAC species x3 = _ 5 = Total Cover FACU species x4 = ` UPL species x5 = 70 yes FAC Column Totals: (A) — 20 Les FAC Prevalence Index = B/A = Hydrophytic Vegetation Indicators: 5 no FAC 5 no FAC ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' 4 - Morphologleal Adaptations' (provide supporting ❑ data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must 100 — = Total Cover be present, unless disturbed or problematic. Remarks: Hydrophytic vegetation indicator present. (B) Hydrophytic Vegetation Yes ® No ❑ = Total Cover Present? US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SOIL _ Sampling Point: $. Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc2 Texture Remarks 0=4 10YR 4/2 100 clay loam 4-12 10YR 4/2 92 10YR 4/6 8 C M silty clay Pedox con.. have sharp boundaries 12-18 2.5Y 5/2 85 10YR 4/6 10 C M silty clay 10YR 4/2 5 D M 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ® Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ElSandy Gleyed Matrix (S4) ElRedox Depressions (F8) wetland hydrology must e present, unless disturbed or roblematic. Restrictive Layer (if present). Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Hydric soil indicator F3 present, but sharp boundaries of redox concetrations indicate that they are likely relic features HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 413) (MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Drainage Patterns (1310) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (B13) ❑ Dry -Season Water Table (C2) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift Deposits (63) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-Neutral Test (D5) ❑ Surface Soil Cracks (66) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Frost -Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (68) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No ® Depth (inches): Saturation Present? Yes ❑ No (includes capillary fringe) ® Depth (inches): Wetland Hydrology Present? Yes ❑ No Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: No wetland hydrology indicators present. US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Fedefal Wayl inn Sampling Date: 1115/15 Applicant/Owner: Archdiocese or Seattle State: WA Sampling Point: 10 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32, T21N. R4E Landform (hillslope, terrace, etc.): hills lope Local relief (concave, convex, none): concave Slope (%): 5=8 Subregion (LRR): A Lat.- _ Long: = Datum: Soil Map Unit Name: Norma sandy loam NWI classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Hydric Soil Present? Wetland Hydrology Present? Yes ❑ No Yes ® No ❑ Is the Sampled Area within a Wetland? Yes ❑ No Remarks: Data point not located within a wetland; all three wetland indicators not present. Data point located at flag DP2. Yes ❑ No VEGETATION — Use scientitic names or plants Tree Stratum Plot size: 0' radlus ( ) Absolute Cover Dominant 5_00cleS7 Indicator Status Dominance Test Worksheet: 1. _ Number of Dominant Species 2 (A) 2 That Are OBL, FACW, or FAC: 3. Total Number of Dominant 4 (B) 4. Species Across All Strata: 50% = 20% _ = Total Cover Percent of Dominant Species 50 (A/B) Sanlinot5hrub Stratum (Plot size: 15' r i ) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Flsnaula aurshlans 5 ves FAC 2. Rubus armeniacus 3 ves FACU Total Q/ Cover of: Multiply by: 3. OBL species 0 x1 = 4. FACW species 0 x2 = 5. FAC species 85 x3 = 255 50% = 4, 20% = 1_6 8 = Total Cover FACU species 23 x4 = 92 Herb Stratum (Plot size: ' radlu) UPL species x5 = 1. Daucus carota 20 ves FACU Column Totals: 108 (A) 347 (B) 2. A rostiss pg llians 60 3. Holcus lanatus 12 4. Trifolium repens 8 5. 6. 7. 8. 9. 10. 11. 50% = 50, 20% = 20 100 Woody Vine Stratum (Plot size: 10' radius) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum 0 Remarks: No hydrophytic vegetation indicator present = Total Cover = Total Cover FAC FAC FAC Prevalence Index = B/A = 3.21 Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ❑ 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' ❑ 4 - Morphological Adaptations' (Provide supporting data in Remaitcs or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes ❑ No Present? US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 Project Site: Gethsemane Cemetery SOIL Sampling Point: 10 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture Remarks 0-12 10YR 3/2 95 10YR 4/6 5 C M clay loam Redox features start at 4�' 1212=18 10YR 4/2 80 10YR 4/6 10 C M silty clay 10YR 3/2 10 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ® Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Hydric soil indicator F3 present, but redox concentrations have sharp boundaries which indicates they are likely relict features HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (B9) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (131) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No ® Depth (inches): Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (139) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) a ura ion resen . (includes capillary fringe) Yes ❑ No ® Depth (inches): Wetland Hydrology Present? Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicators present. Yes ❑ No US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region I I Project Site: Gethsemane Cemela City/County: Federal Wav)Kina Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 11 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: 22 T21N. R4E Landform (hillslope, terrace, etc.): Hillsloae Local relief (concave, convex, none): none Slope (%): 2=5 Subregion (LRR): A Let: = Long: _ Datum: Soil Map Unit Name: Kitsap silt loam 2-8% slo NWI classification: _ Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (if no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ❑ No H dric Soil Present? Yes ❑ No ® Is the Sampled Area Yes ❑ No Y within a Wetland. Wetland Hydrology Present? Yes ❑ No Remarks: Data point not located within a wetland; all three wetland indicators absent. Data point located in upland forest east of West Fork Hylebos Creek. VEGETATION — Use scientific names of Tree Stratum (Plot size: 30' rsdlus) Absolute a Cover Dominant Spades? Indicator Status Dominance Test Worksheet: 1. Acermacmnhvllum 15 yes FACU Number of Dominant Species 3 (A) 2. A/n, s� 30 ves FAC That Are OBL, FACW, or FAC: 3. .Thula p 20 yes FAC Total Number of Dominant 7 (B) 4. 7 u a hefem h f!e 10 no FACU Species Across All Strata: 50% = 37.5, 20% = 15 75 = Total Cover Percent of Dominant Species 43% (A/B) S n hrub Stratum (Plot size: I& radius) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Okemlerl8 cirasiformis 12 yes FACU 2. R s s CIa611t 8 yes FAC Total % Cover of: Mulliply_b� 3. Ruhus armeniacus 5 yes FACU OBL species x1 = 4 — FACW species x2 = 5 FAC species 58 x3 = 174 50% = 12.5. 20% = 5 25 = Total Cover FACU species 50 x4 = 200 Hertz Stratum (Plot size: 5' ra i ) UPL species x5 = 1. Pofvstichum munlfum 8 yes FACU Column Totals: 1 08 (A) 374 (B) 2 Prevalence Index = B/A = 3.46 Hydrophytic Vegetation Indicators: 3 4 ❑ 1 — Rapid Test for Hydrophytic Vegetation 5 ❑ 2 - Dominance Test is >50% 6, ❑ 3 - Prevalence Index is <3.0' 7, 4 - Morphological Adaptations' (Provide supporting ❑ data in Remarks or on a separate sheet) 8 g ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. — 'Indicators of hydric soil and wetland hydrology must 50% = 4, 20% = 1_6 8 Total Cover be present, unless disturbed or problematic. Woody Vine $Iralurn (Plot size: 1 ' i ) Hydrophytic 2. Vegetation Yes ❑ No 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 0 (11affM) Remarks: Hydrophytic vegetation indicator not present. US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SAII Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture Remarks 0=3 10YR 3/3 100 loam 3-12 10YR 413 100 loam 1212 18 2.5Y 5/3 100 clay loam 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (B9) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 413) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (131) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (C1) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No ® Depth (inches): Saturation Present? Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (139) (MLRA 1, 2, 4A, and 413) ❑ Drainage Patterns (1310) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) (includes capillary fringe) Yes ❑ No ® Depth (inches): Wetland Hydrology Present? Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicators present. Yes ❑ No US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 W WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane C meter City/County: Federal Wav'Kina Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 12 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: 532. T21N, R4E Landform (hillslope, terrace, etc.): terrace Local relief (concave, convex, none): none Slope (%): 2=3 Subregion (LRR): A Lat: - Long: - Datum: - Soil Map Unit Name: Kitsap silt loam 2-8% slopes NW] classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ❑ No Hydric Soil Present? Yes El No ® Is the Sampled A?ea within a Wetland. Wetland Hydrology Present? Yes ❑ No Remarks: Data point not located within a wetland; all three wetland indicators absent. Data point located near old homestead. VEGETATION — Use sclentitic names of plants Plot size: 37' radius Absolute Dominant Indicat 7rafl Stratum ( ) Cover species? Status 1. Malus domestics 15 n/a" NI 2. Alnus rubra 90 y9S FAC 3. 4, 50% = 5, 20% = 2 10 SaolinolShrub Stratum (Plot size: 1V radius) 1. Rubus laciniatus 5 2. Rubuis armeniacus 25 3. Oemleria cerasiformis 12 4. Sambucus racemosa 5 5. _ 50% = 23.5. 20% = 9_4 47 Herb Stratum_(Plot size: 5' radius) 1, En6lo6ium ciliatum 10 2. Cirslum ❑ulaare 15 3. Urtica dioica 18 4. Tolmiea menziesh 25 5. Poa so. 8 6. E uisel�r um arvens 10 7. 8. _ 9. 10. _ 11. _ 50% = 43, 20% = 17.2 86 Woody Vine Stratum (Plot size: 10' radi-u s) 1. Rubus ursinus 12 2. _ 50% = 6, 20% = 2_4 12 % Bare Ground in Herb Stratum Remarks: `excluded from calculations per chapter = Total Cover no FACU FACU ves FACU no FACU = Total Cover no FACW no FAC FAC FAC n/a` NI no FAC = Total Cover Yes ❑ No Dominance Test Worksheet: Number of Dominant Species 3 That Are OBL, FACW, or FAC: Total Number of Dominant 6 Species Across All Strata: — Percent of Dominant Species 50 That Are OBL, FACW, or FAC: — Prevalence Index worksheet: Total % Cover of: Multiply OBL species x1 = FACW species 10 x2 = 20 FAC species 78 x3 = 234 FACU species 42 x4 = 168 UPL species x5 = Column Totals: 930 (A) 422 (B) Prevalence Index = B/A = 3.25 Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ❑ 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' ❑ 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a seperate.sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic YLS FACU Hydrophytic Vegetation = Total Cover Present? • no hydrophytic vegetation indicator present. Yes ❑ No (A) (B) (A/B) f US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 Project Site: Gethsemane Cemetery SOIL :Camntinn Pnint• 17 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) Type' Loc2 Texture Remarks 0-5 10YR 3/3 100 loam 5-13 10YR 4/3 80 loam 10YR 3/3 20 1313=18 2.5Y 5/3 100 clay loam 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (178) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (B9) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (139) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) Water Table Present? Yes ❑ No ® Depth (inches): Saturation Present? Yes ❑ No ® Depth (inches): Wetland Hydrology Present? Yes ❑ No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM —Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Federal WaylKing Sampling Date: 11/12/15. Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 13 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32. T21N. R4E Landform (hillslope, terrace, etc.): floodolain Local relief (concave, convex, none): none Slope (%): 0=2 Subregion (LRR): A Lat: _ Long: _ Datum: Soil Map Unit Name: Kitsao sift loam, 15 to 30°Ln_slopes NW I classification: _ Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ J Hy dric Soil Present? Yes ® No ❑ Is the Sampled Area Yes ® No ElII within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: Data point located within a wetland; all three indicators present. Data point located 10' northwest of flag J1. vt_cat I A I tury — use scientinc names or Plants Tree Stratum (Plot size: 30' radius) % Cover Dominant ecies? Indicatortum Status Dominance Test Worksheet: 1. Alnus rubra 35 yes FAC Number of Dominant Species 5 (A) 2 That Are OBL, FACW, or FAC: 3• Total Number of Dominant 5 (B) 4 Species Across All Strata: 50% = 17.5, 20% = 7 35 = Total Cover Percent of Dominant Species 100 (A/B) SapGriglShrub Stratum (Plot size: i5' radius) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Ruhus soectal)iirs 35 ves FAC 2. RubyaarviHorus 5 no FACU Total % Cover of: Multiply bv: 3. Acer circinatum 15 ves FAC OBL species x1 = 4. Polyoonum cusofdatum 10 no FACU FACW species x2 = 5, FAC species x3 = 50% = 32.5, 20% = 13 65 = Total Cover FACU species x4 = Herb Stratum (Plot size: 5' radius) UPL species x5 = 1. carex obnunla 25 ves OBL Column Totals: (A) (B) 2. Tolmiea menziesii 10 3. 4. 5. 6. 7. 8. 9. 10. 11, 50% = 12.5, 20% = 5 25 Woody Vine Stratum (Plot size: 1V mdlus) 1. _ 2. 50% = 20% _ % Bare Ground in Herb Stratum 75 silt Remarks: Hydrophytic vegetation indicator present = Total Cover = Total Cover FAC Prevalence Index = B/A = Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is ,�3.0' ❑ 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes ®' No ❑ Present? f US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 ,�1 Project Site: Gethsemane Cemetery Ann Camnlinn Pninf• 17 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc2 Texture Remarks 0-10 10YR 3/1 100 SSL sandy silt loam: scour and silt deposits 1010=18 2.5Y4/1 100 SSL saridVsillluaur 18-24 G14/N 100 loamy sand 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ® Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Data point located on vegetated flats in floodplain of Hylebos Creek. Scour during flood events inhibits development of redoximorphic features in soil profile. Hydric soil assumed to be present due to presence of wetland hydrology and hydrophytic vegetation indicators. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (B9) ® High Water Table (A2) (except MLRA 1, 2, 4A, and 413) ❑ Saturation (A3) ❑ Salt Crust (1311) ❑ Water Marks (131) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ® No S P � ❑ Depth (inches): 11 Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (139) (MLRA 1, 2, 4A, and 413) ❑ Drainage Patterns (B10) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) aturation resent. Yes ® No ❑ Depth (inches): 10 Wetland Hydrology Present? (includes capillary fringe) _ Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: Wetland hydrology indicator present. Yes ® No ❑ US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Federal WaV]Kinn Sampling Date: 11/12/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 14 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32. T21N, R4E Landform (hillslope, terrace, etc.): Hillslope Local relief (concave, convex, none): none Slope Subregion (LRR): A Lat: _ Long: = Datum: _ Soil Map Unit Name: Kitsap silt loam, 15 to 30% slopes NW I classification: _ Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SIIMMARY OF FINDINGS — Attach site maD showing samDlina point locations. transects. important features. etc. Hydrophytic Vegetation Present? Yes ❑ No H dric Soil Present? Yes ❑ No ® y Is the Sampled Area Yes El No within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point located in upland; all three wetland indicators absent. Data point located 10' northeast of flag J1. VEGETATION — Use scientinc names or piants Tree Stratum (Plot size: 30' radius) Absolute Cover Dominant ie ? Indicator% Status Dominance Test Worksheet: 1. 7huis ❑cicala 45Les FAC Number of Dominant Species 2 (A) 2. Acer macrunh Ivfum 20Les FACU That Are OBL, FACW, or FAC: 3. Alnus rubra 5 no FAC Total Number of Dominant 5 (B) 4. Species Across All Strata: 50% = 35, 20% = 14 70 = Total Cover Percent of Dominant Species 40 (A/B) SanlintslShr� b Sim (Plot size: 15' ra i s) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Acer circinatum 35 ves FAC 2. Oemterla cerasiformis 10 ves FACU Total % Cover of: Muilt l b 3. Sambuous racemosa 5 no FACU OBL species x1 = 4, FACW species x2 = 5. FAC species 85 x3 = 255 50% = 25, 20% = 10 50 = Total Cover FACU species 70 x4 = 280 Heft Stratum (Plot size: ' radio) UPL species x5 = 1. Palvstichum munl(um 35Les FACU Column Totals: 155 (A) 530 (B) 2. f Prevalence Index = B/A = 3_4 Hydrophytic Vegetation Indicators: 3. 4. ❑ 1 — Rapid Test for Hydrophytic Vegetation 5, ❑ 2 - Dominance Test is >50% 6. ❑ 3 - Prevalence Index is <3.0' 7. 4 - Morphok)gical Adaptations' (Provide supporting 8 ❑ data In Remarks or on a separate sheet) g, ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. Indicators of hydric soil and wetland hydrology must 50% = 17.5, 20% = 7 35 Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: 10' radius) 1. Hydrophytic 2 Vegetation Yes ❑ No 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 65 (leaf fall] Remarks: Hydrophytic vegetation indicator not present. US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SOIL Samolino Point: 14 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture Remarks 0-18 2.5Y 5/3 85 SSL sandy sift loam 10YR 3/3 15 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) © Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Depressions FB Redox De P ( ) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 413) (MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (611) ❑ Drainage Patterns (1310) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (B13) ❑ Dry -Season Water Table (C2) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (C1) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-Neutral Test (D5) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Frost -Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No ® Depth (inches): Saturation Present? Yes ❑. No (includes capillary fringe) ® Depth (inches): Wetland Hydrology Present? Yes ❑ No Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemetery City/County: Federal WavlKfng Sampling Date: 11/12/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 15 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32. T21N, R4E Landform (hillslope, terrace, etc.): floodpiain Local relief (concave, convex, none): none Slope (%): 0=2 Subregion (LRR): A Lat: = Long: = Datum: _ Soil Map Unit Name: Kitsao silt loam. 15 to 30% slopes NWI classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ® No ❑ Is the Sampled Area Yes ® No [Iy within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: Data point located within a wetland; all three wetland indicators present. Data point located 10' northwest of flag E6. VtUt I A I IUN — use scieninic names or piams Tree Stratum (Plot size: 30' radius) Absolute % cove r Dominant 5 cie Indicator Status Dominance Test Worksheet: 1. Alnus rubs 35 yes FAC Number of Dominant Species 6 (A) 2 That Are OBL, FACW, or FAC: 3. Total Number of Dominant 8 (B) 4 Species Across All Strata: 50% = 17.5, 20% = 7 35 = Total Cover Percent of Dominant Species 100 (A/B) Sa01ino15hrub Stratum (Plot size: 15' radius) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Rubps�ectatriiis 45 Yes FAC 2. Acer circinatum 15 yes FAC Total % Cover of: Multiply L•., 3. Rubus parviftarus 5 no FACU OBL species x1 = 4, FACW species x2 = 5, FAC species x3 = 50% = 32.5, 20% = 13 65 = Total Cover FACU species x4 = Herb Stratum (Plot size: B' radius) UPL species x5 = 1. Lysichiton aman=us 10 yes OBL Column Totals: (A) (B) 2. Tolmiea menziesii 8 yes FAC Prevalence Index = B/A = Hydrophytic Vegetation Indicators: 3. Rthyrium fflix-temina 5 yes FAC 4, — ❑ 1 — Rapid Test for Hydrophytic Vegetation 5, ® 2 - Dominance Test is >50% 6. ❑ 3 - Prevalence Index is <3.0' 7. ❑ 4 - Morphological Adaptations' (Provide supporting 8 data in Remarks or on a separate sheet) g_ — ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. 'Indicators of hydric soil and wetland hydrology must 50% = 12.5, 20% = 4-.6 23 Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: 10' radius) 1. Rubus urinus 5 yes FACU Hydrophytic 2 Vegetation Yes ® No ❑ 50% = 2_5, 20% = 1 5 = Total Cover Present? % Bare Ground in Herb Stratum 77 (silt deposits) Remarks: Hydrophytic vegetation indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 Project Site: Gethsemane Cemetery SOIL amnliro Point: 15 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture Remarks 0-8 10YR 3/1 100 sandy loam 8-12 2.5Y 411 100 sandy foam 12-20+ G14/N 100 u loamVsand 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. ZLocation: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ® Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Data point located on vegetated flats in floodplain of Hylebos Creek. Scour during flood events inhibits development of redoximorphic features in soil profile. Hydric soil assumed to be present due to presence of wetland hydrology and hydrophytic vegetation indicators. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ® Surface Water (Al) ❑ Water -Stained Leaves (B9) ❑ Water -Stained Leaves (69) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 46) (MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Drainage Patterns (B10) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (613) ❑ Dry -Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-Neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost -Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ® No ❑ Depth (inches): 8 Saturation Present? Yes ® No (includes capillary fringe) ❑ Depth (inches): 7 Wetland Hydrology Present? Yes ® No ❑ Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: Wetland hydrology indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cernetery City/County: Federal Way/KirL4 Sampling Date: 11/12/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 16 Investigator(s): Jeff Gray, and Kevin O'Brien Section, Township, Range: S32 T21N Landform (hillslope, terrace, etc.): hillslove Local relief (concave, convex, none): none Slope (%): >30 Subregion (LRR): A Lat: - Long: = Datum: - Soil Map Unit Name: Kitsaa silt loam. 15 to 30%slopes NW I classification: _ 1 Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) 1 SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ❑ No Hydric Soil Present? Yes ❑ No ® Is the Sampled Area Yes [I No _ within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point not located within a wetland; all three wetland indicators absent. Data point located 10' northwest of flag E6. I J Vhtjh I A I IUN — use scientnic names or plants Stratum Plot size: 0' radlus ) ( � Absolute % Cover n[ DomTree Species? Sp"i Indicator Status Dominance Test Worksheet: 1. Thule plicate 35 yes FAC Number of Dominant Species 2. Ag ermacro h um 25 yes FACU That Are OBL, FACW, or FAC: 3. Total Number of Dominant 5 4 Species Across All Strata: — 50% = 30, 20% = 12 60 = Total Cover Percent of Dominant Species 40 5an1in91Shrub Stratum (Plot size: dies) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Mahonia nervosa 8 yes FACU 2. Aeerairclrralum 20 yes FAC Total % Cover of: Multiply by: 3. OBL species x1 = 4 FACW species x2 = 5 FAC species 55 x3 = 115 50% = 14, 20% = 5_6 28 = Total Cover FACU species 103 x4 = 412 Herb Stratum (Plot size: 5' radius) UPL species x5 = 1. Palvslichum munitum 70 yes FACU Column Totals: 158 (A) 527 (B) 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 50% = 35, 20% = 14 770 Wood Vine Stratum (Plot size: 0' radlu ) 1. _ 2. 50% = 20% _ % Bare Ground in Herb Stratum 30 (leaf rally Remarks: Hydrophytic vegetation indicator not present Prevalence Index = B/A = 3.3 Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ❑ 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' ❑ 4 - Morphological Adaptations` (Provide supporting data In Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) = Total Cover 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes ❑ No = Total Cover Present? (A) (B) (A/B) I US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 Project Site: Gethsemane Cemetery SAIL t@ tm n D'Inf- In Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' LocZ Texture Remarks 0-18 2.5Y 5/3 90 SSL sandy silt loam 10YR 3/3 10 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (178) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (1311) ❑ Water Marks (131) ❑ Aquatic Invertebrates (1313) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (64) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (65) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (66) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (69) (MLRA 1, 2, 4A, and 413) ❑ Drainage Patterns (1310) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No ® Depth (inches): Saturation Present? Yes ❑ No ® Depth (inches): Wetland Hydrology Present? Yes ❑ No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region J J Project Site: Gethsemane Cemetery City/County: Federal WavlKinq Sampling Date: 11/12/15 Applicant/Owner: Archdiocese of Seattl State: WA Sampling Point: 17 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32. T21N RaE Landform (hillslope, terrace, etc.): toe of $loe Local relief (concave, convex, none): none Slope (%): 0=2 Subregion (LRR): A Lat: _ Long: = Datum: Soil Map Unit Name: Bellingham silt loam NW I classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (if needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ Hydric Soil Present? Yes ® No ❑ Is the Sampled Area Yes ® No ❑ within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: Data point located within a wetland; all three wetland indicators present. Data point located 10' south of flag F12. VEGETATION — Use scientific names of 7ree_Stratum (Plot size: 30' radlus) 1. Alnus rubra 2. 3. 4. 50% = 20, 20% = 8 3aollnolShrub Stratum (Plot size: 15' ra ) 1. Rubus snectabilis 2. 5am ucus cemosa 3. 4. 5. 50% = 32.5, 20% = 13 Herb Stratum (Plot size: 5' radius) 1. Lvsfchilon amer[cartus 2. EGuisetum arvense 3. Afhwium felix rimina 4. i as miucrarous 5. 6. 7. 8. 9. 10. 11. 50% = 22.5. 20% = 9 Woody Vine tratum (Plot size: 1 ' radi s) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum (mud. I € fall Absolute Dominant Indicator % Cover Sfleci Status 40Les FAC 40 = Total Cover 60 ves FAC 5 no FACU 65 = Total Cover 15 ves OBL 5 no FAC 10 Les FAC 15 Les OBL 45 = Total Cover Remarks: Hydrophytic vegetation inidcator present. US Army Corps of Engineers = Total Cover Dominance Test Worksheet: Number of Dominant Species 5 That Are OBL, FACW, or FAC: Total Number of Dominant 5 Species Across All Strata: — Percent of Dominant Species 100 That Are OBL, FACW, or FAC: Prevalence Index worksheet: Total % Cover of: Multiply by; OBL species x1 = FACW species x2 = — FAC species x3 = FACU species x4 = — UPL species x5 = — Column Totals: (A) — Prevalence Index = B/A = Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' El data - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? (B) Yes ® No ❑ Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SOIL Sampling Point: 17 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type` Locz Texture Remarks 0=4 10YR 2/1 100 ^ y manic mucky peat 4-18+ 10YR 411 70 10YR 4/6 18 C M Bandy loam G1 5/N 12 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ® Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ElSandy Gleyed Matrix (S4) ElRedox Depressions (F8) wetland hydrology must e present, unless disturbed or probll ematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Remarks: Hydric soil indicator F3 present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (B9) ® High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ® No ❑ Depth (inches): 2 Saturation Present? Yes ® No ❑ Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) (includes capillary fringe) Yes ® No ❑ Depth (inches): 0 Wetland Hydrology Present? Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: Wetland hydrology indicator present Yes ® No ❑ US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region �I I Project Site: Gethsemane_Cemeta[V City/County: Federal WayXing Sampling Date: 11/12/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 18 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32. T21N. R4F Landform (hillslope, terrace, etc.): hiil� slope Local relief (concave, convex, none): none Slope (%): 1015 Subregion (LRR): A Lat: _ Long: - Datum: Soil Map Unit Name: Bellingham silt loarrl NWI classification: _ Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks,) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SIIMMARY OF FINDINGS - Attach site map showinq samplinq point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ I Hydric Soil Present? Yes ❑ No ® Is the Sampled Area within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point located in upland; not all three wetland indicators present. Data point located 10' north of flag F12. Yes ❑ No VELETA I IUN - use scienrmc names or psanrs Pot size: ' i Tree Stratum li3 ( -d�) - Absolute % Cover Dominant Species? Indicator Status Dominance Test Worksheet: 1. Pauedctsuaa rnenziesN 25 yes FACU Number of Dominant Species 2 (A) 2. Alnus rubra 35 Y�2§ FAC That Are OBL, FACW, or FAC: 3. Total Number of Dominant 6 (B) 4. — Species Across All Strata: 50% = 30, 20% = 12 60 = Total Cover Percent of Dominant Species 33.3 (A/B) Safllin 1ST, hruh Stratum (Plot size: 15' radius) That Are OBL, FACW, or FAC: 1. Hex�uifa#um 10 Les FACU Prevalence Index worksheet: 2. Oemleria cerasilorMIS 20 Les FACU Total % Cover of: Multiply by: 3. Acercircinatum 15�es FAC OBL species x1 = 4 FACW species x2 = 5 FAC species 50 x3 = 150 50% = 22.5, 20% = 9 45 = Total Cover FACU species 90 x4 = 270 Herb Stratum (Plot size: 5'radius) UPL species x5 = 1. [ichum mum 35 ves FACU Column Totals: 140 (A) 420 (B) 2 Prevalence Index = B/A = 3 3 Hydrophytic Vegetation Indicators: 4 ❑ 1 - Rapid Test for Hydrophytic Vegetation 5 ❑ 2 - Dominance Test is >50% 6, ® 3 - Prevalence Index is <3.0' 7. 4 - Morphological Adaptations' (Provide supporting ❑ data In Remarks or on a separate sheet) 8 9 ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. Indicators of hydric soil and wetland hydrology must 50% = 17.5, 20%= 7 35 Total Cover be present, unless disturbed or problematic. Woody Vine Sitr lum (Plot size: 10' radius) 1. - Hydrophytic 2. Vegetation Yes ® No ❑ 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 65 Remarks: Hydrophytic vegetation indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast - Version 2.0 Project Site: Gethsemane Cametery SOIL Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture 0-18 10YR 3/3 100 silt loam Point: 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 'Location: PL=Pore Lining, M=Matrix Remarks Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (All) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ElSandy _ Gleyed Matrix (S4) ElRedox Depressions (F8) wetland hydrology must e present, unless disturbed or probll ematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No ® Depth (inches): Saturation Present? Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) (includes capillary fringe) Yes ❑ No ® Depth (inches): Wetland Hydrology Present? Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicator present. Yes ❑ No US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cemete City/County: Federal WayKjna Sampling Date: 11/12/15 Applicant/Owner: Archdiocese of Seattfe State: WA Sampling Point: 19 Investigator(s): Jeff Gray and Kevin a8rien Section, Township, Range: S32. T21N R4 Landform (hillslope, terrace, etc.): depression adiacent to road Local relief (concave, convex, none): concave Slope (%): 0=2 Subregion (LRR): A Lat: - Long: = Datum: Soil Map Unit Name: Kitsap sill foam. 2 to 8% sic pes NW I classification: _ Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ® No ❑ Is the Sampled Area Yes ® No ❑ y within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: Data point located within a wetland; all three wetland indicators present. Data point located 5' south of flag L5. VEGETATION — Use scientnic names or planrs Tree Stratum (Plot size: 80' radius) Absolute Dominant Indicat % Cover Sper,ies? Status 1. 2. 3. 4. 50% = 20% _ SaplingtShruh Stratum (Plot size: 1 ' radius) 1. - 2. 3. 4. 5. 50% = 20% _ Herb Stratum (Plot size: 5' ra i ) 1. Marls arundlnacea 100 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 50% = 50, 20% = 20 100 Woody Vine Stratum (Plot size: 1 ' radi ) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum 0 Remarks: Hydrophytic vegetation indicator present US Army Corps of Engineers = Total Cover = Total Cover yes FACW = Total Cover = Total Cover Dominance Test Worksheet: Number of Dominant Species 1 That Are OBL, FACW, or FAC: — Total Number of Dominant 1 Species Across All Strata: Percent of Dominant Species 100 That Are OBL, FACW, or FAC: Prevalence Index worksheet: Total % Cover of: NtUMPly by OBL species x1 = _ FACW species x2 = _ FAC species x3 = Y FACU species x4 = _ UPL species x5 = _ Column Totals: (A) Prevalence Index = B/A = Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' ❑ 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. (B) Hydrophytic Vegetation Yes ® No ❑ Present? Western Mountains, Valleys, and Coast— Version 2.0 Project Site: Gethsemane Cemetery SOIL Point: Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loe Texture Remarks 0-18 10YR 4/2 82 10YR 416 18 C M clay loam redox features start at 4" 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (At) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Al 1) ® Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ElSandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must e present, unless disturbed or roblematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ® No ❑ Remarks: Hydric soil indicator F3 present HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ® Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ Water -Stained Leaves (B9) ® High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) (MLRA 1, 2, 4A, and 413) ❑ Saturation (A3) ❑ Salt Crust (1311) ❑ Drainage Patterns (1310) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (B13) ❑ Dry -Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-Neutral Test (D5) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (67) ❑ Other (Explain in Remarks) ❑ Frost -Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ® No ❑ Depth (inches): 2 Water Table Present? Yes ® No ❑ Depth (inches): 0 Saturation Present? Yes ® No (includes capillary fringe) ❑ Depth (inches): 0 Wetland Hydrology Present? Yes ® No ❑ Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: Wetland hydrology indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region I Project Site: Gethsemane Cemeterery City/County: ale eral WavlKin❑ Sampling Date: 11/12/15 Applicant/Owner: A hdiccese or Seattle State: WA Sampling Point: 20 Investigator(s): Jeff GraV and Kevin O'Bdan Section, Township, Range: S$2. T21N, 114E Landform (hillslope, terrace, etc.): hlllslope Local relief (concave, convex, none): none Slope (%): 151520 Subregion (LRR): A Lat: _ Long: = Datum: Soil Map Unit Name: Kitsart silt loam 2-8% slop es NW I classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ❑, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ® No ❑ Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ❑ No ® Is the Sampled Area Y within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point located in upland; all three wetland indicators not present. Data point located 10' north of flag L5 Yes ❑ No VEGETATION — Use scientlric names or pianrs Dominance Test Worksheet: Tree Stratum (Plot size: 30' radius) Absolute Dominant Indicator % Cover specie Status 1. Atnus rubs 15 Les FAC Number of Dominant Species 2 (A) 2. That Are OBL, FACW, or FAC: 3. Total Number of Dominant 3 (B) 4. Species Across All Strata: 50% = 7_5, 20% = 3 15 = Total Cover Percent of Dominant Species 66.7 (A/B) 5a I{n hrub Stratum (Plot size: 15' radius) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1. Rubus armeniacus 75 ves FACU 2. C la us mono na 10 no FAC Total % Cover of: Multiply 3 OBL species x1 = 4 FACW species x2 = 5 FAC species x3 = 50% = 42.5, 20% = 17 85 = Total Cover FACU species x4 = Herb Stratum (Plot size: 5' ra i s) UPL species x5 = 1. Phalads aranorind0a 5 yq_S FACW Column Totals: (A) (B) 2 Prevalence Index = B/A = Hydrophytic Vegetation Indicators: 3 4 ❑ 1 — Rapid Test for Hydrophytic Vegetation 5 ® 2 - Dominance Test is >50% 6. ❑ 3 - Prevalence Index is <3.0' 7. 4 - Morphological Adaptations` (Provide supporting ❑ data in Remarks or on a separate sheet) 8 y _ — ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. 'Indicators of hydric soil and wetland hydrology must 50% = 2_5, 20% = 1 5 Total Cover be present, unless disturbed or problematic. W20y Vine Stratum (Plot size: 10' radius) 1. Hydrophytic 2 Vegetation Yes ® No ❑ 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 95 fleaf fall) Remarks., Hydrophytic vegetation indicator present. i US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 Project Site: Gethsemane Cemetery SOIL 4e.nnHl D-;f +. IA Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' LoC2 Texture Remarks 0-18 10YR 5/3 90 silt loam 10YR 3/3 10 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ElSandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Yes ❑ No ED Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 46) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (613) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (133) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (136) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (68) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (69) (MLRA 1, 2, 4A, and 413) ❑ Drainage Patterns (1310) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) Water Table Present? Yes ❑ No ® Depth (inches): Saturation Present? Yes ❑ No ® Depth (inches): Wetland Hydrology Present? (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicator present. Yes ® No ❑ US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region Project Site: Gethsemane Cernet�2ree City/County: Federal WnylKirg Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 21 Investigator(s): Jeff Grav and Kevin O'Brien Section, Township, Range: S32. T21N. Rdi= Landform (hillslope, terrace, etc.): roadside ditch Local relief (concave, convex, none): concavg Slope (%): 3=5 Subregion (LRR): A Lat: - Long: = Datum: Soil Map Unit Name: Kitsan sit loam. 2-8% slopes NW I classification: _ Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (if no, explain in Remarks.) Are Vegetation ®, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ❑ No Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ® No ❑ Is the Sampled Area Yes ® No ❑ y within a Wetland? Wetland Hydrology Present? Yes ® No ❑ Remarks: Data point located in a wetland; all three wetland indicators present. Data point located at flag 135. Roadside ditch mowed regularly. VEGETAI IUN — Use scienLlrlc names or piants Tree Stratum %(Plot size: 30' radius) Absolute Dominant StaIndtus t e Cover Species? Status 2. — 3. 4. 50% = 20% _ Sapling/Shrub Slratum (Plot size: 19 radius) 1. - 2. 3. 4. 5. 50% = 20% _ Herb Stratum (Plot size: 5' radius) 1. P balaris arundirr c a 45 2. Ranu%ylus renens 25 3. Lpliurn perqnne 15 4. AgMgL& caodla6 10 5. 6. 7. 8. 9. 10. 11. 50% = 47.5. 20% = 19 95 Woody VineStratum (Plot size: 1 ' ra iu ) 1. - 2. 50% = 20% _ % Bare Ground in Herb Stratum 5 water Remarks: Hydrophytic vegetation indicator present = Total Cover = Total Cover Les FACW ryes FAC nc FAC no FAC = Total Cover Dominance Test Worksheet: Number of Dominant Species 2 That Are OBL, FACW, or FAC: — Total Number of Dominant 2 Species Across All Strata: Percent of Dominant Species 100 That Are OBL, FACW, or FAC: Prevalence Index worksheet: Total % Cover of: Multroly by: OBL species x1 = — FACW species x2 = FAC species x3 = — FACU species x4 = — UPL species x5 = — Column Totals: (A) — Prevalence Index = B/A = Hydrophytic Vegetation Indicators: ❑ 1 — Rapid Test for Hydrophytic Vegetation ® 2 - Dominance Test is >50% ❑ 3 - Prevalence Index is <3.0' El data - Morphaiogical Adaptations' (Provide supporting data in Remarks or on a separate sheet) ❑ 5 - Wetland Non -Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. v Hydrophytic Vegetation = Total Cover Present? (B) Yes ® No ❑ US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SOIL Sampling Point:21 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' LocZ Texture Remarks 0-8 10YR 2/1 100 loam hardpan at 8": saturated to surface 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils': ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ® Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (176) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 'Indicators of hydrophytic vegetation and ElSandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: hardpan Depth (inches): 8" Hydric Soils Present? Yes ® No ❑ Remarks: Hydric soil determined to be present due to saturation in entire soil profile, and presence of hydrophytic vegetationand wetland hydrology HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ® High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) ® Saturation (A3) ❑ Salt Crust (1311) ❑ Water Marks (B1) ❑ Aquatic Invertebrates (613) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (63) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (66) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes ® No ❑ Depth (inches): _ Water Table Present? Yes ® No ❑ Depth (inches): 8 Secondary Indicators (2 or more required) ❑ Water -Stained Leaves (139) (MLRA 1, 2, 4A, and 413) ❑ Drainage Patterns (1310) ❑ Dry -Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost -Heave Hummocks (D7) Saturation Present? Yes ® No ❑ Depth (inches): 0 I Wetland Hydrology Present? Yes ® No ❑ (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: Primary wetland hydrology indicators present. US Army Corps of Engineers Western Mountains, Valleys, and Coast — Version 2.0 WETLAND DETERMINATION DATA FORM — Western Mountains, Valleys, and Coast Region J Project Site: Gethsemane Cemeserery City/County: Federal Wa, lKiin Sampling Date: 11/5/15 Applicant/Owner: Archdiocese of Seattle State: WA Sampling Point: 22 Investigator(s): Jeff Gray and Kevin O'Brien Section, Township, Range: S32. T21N. R4E Landform (hillslope, terrace, etc.): hillslo a along roadside ditch Local relief (concave, convex, none): convex Slope (%): 25 Subregion (LRR): A Lat: - Long: = Datum: _ Soil Map Unit Name: Kilsap silt loam 2• % I NWI classification: Are climatic / hydrologic conditions on the site typical for this time of year? Yes ® No ❑ (If no, explain in Remarks.) Are Vegetation ®, Soil ❑, or Hydrology ❑, significantly disturbed? Are "Normal Circumstances" present? Yes ❑ No Are Vegetation ❑, Soil ❑, or Hydrology ❑, naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ® No ❑ H dric Soil Present? Yes ❑ No ® Is the Sampled Area Yes ❑ No y within a Wetland? Wetland Hydrology Present? Yes ❑ No Remarks: Data point located in upland; all three wetland indicators not present. Data point located 10' east of flag B5. Area mowed regularly. VtGt I A I IUN — use scienunc names oT plants Tree Stratum Plot size; 30' ra ius ( —�) Absolute over Dominant Spedies? Indicator Status Dominance Test Worksheet: 1. _ — Number of Dominant Species 2 (A) 2 — That Are OBL, FACW, or FAC: 3. Total Number of Dominant (B) 4. Species Across All Strata: 50% = 20% _ = Total Cover Percent of Dominant Species 100 (A/B) SafllinplShrub Stratum (Plot size: 1 ' r dius) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 1 _ — 2 Total % Cover of: Multiply by: 3. OBL species x1 = 4, FACW species x2 = 5. FAC species x3 = 50% = 20% _ = Total Cover FACU species x4 = Herb Stratum (Plot size: F radla) UPL species x5 = 1. Lollrum nerenne 35 ves FAC Column Totals: (A) (B) 2. Fesruce sp.- 15 no _ Prevalence Index = B/A = Hydrophytic Vegetation Indicators: 3. Plari=fanceolafit 5 no FACU 4. Poa cratens+s 25 yes FAC ❑ 1 — Rapid Test for Hydrophytic Vegetation 5. Qq&K Ls cargla 10 no FACU ® 2 - Dominance Test is >50% 6. ❑ 3 - Prevalence Index is <3.0' 7. - Morphological Adaptations' (Provide supporting El data data in Remarks or on a separate sheet) 8 g ❑ 5 - Wetland Non -Vascular Plants' 10. ❑ Problematic Hydrophytic Vegetation' (Explain) 11. 'Indicators of hydric soil and wetland hydrology must 50% = 45, 20% = 18 90 Total Cover be present, unless disturbed or problematic. Wogdy Vine Stratu (Plot size: 10' radius) Hydrophytic 2. Vegetation Yes ® No ❑ 50% = 20% _ = Total Cover Present? % Bare Ground in Herb Stratum 10 Remarks: Hydrophytic vegetation indicator present. US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 Project Site: Gethsemane Cemetery SOIL Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loe Texture 0=7 10YR 3/3 100 loam 7-18 10YR 3/3 60 loam 2.5Y 4/3 40 S mpling Point: 2" 'Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix Remarks Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3: ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except MLRA 1) ❑ Very Shallow Dark Surface (TF12) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (A11) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (Al2) ❑ Redox Dark Surface (F6) ❑ Sandy Mucky Mineral (S1) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox Depressions (F8) wetland hydrology must be present, unless disturbed or Droblematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soils Present? Remarks: No hydric soil indicator present. HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water -Stained Leaves (139) ❑ High Water Table (A2) (except MLRA 1, 2, 4A, and 413) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (131) ❑ Aquatic Invertebrates (1313) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift Deposits (B3) ❑ Oxidized Rhizospheres along Living Roots (C3) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stresses Plants (D1) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No ® Depth (inches): Water Table Present? Yes ❑ No S ' P 0 ® Depth (inches): Yes ❑ No Secondary Indicators (2 or more required) ElWater-StainedLeaves (B9) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) El Dry -Season Water Table (C2) El Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) El Shallow Aquitard (D3) ❑ FAC-Neutral Test (D5) El Raised Ant Mounds (D6) (LRR A) ElFrost-HeaveHummocks (D7) aturation resent. Yes ❑ No ® Depth (inches): Wetland Hydrology Present? (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: - Remarks: No wetland hydrology indicator present. Yes ® No ❑ US Army Corps of Engineers Western Mountains, Valleys, and Coast —Version 2.0 I I I 11 I j j Appendix D —Ecology Wetland Rating Forms Gethsemane Cemetery February 25, 2016 Wedand and Stream Delineation Report 9 z O mct s w o O m m —g Q > m 3 3 O 2 .�. 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O b ° O N —p3 c° QG' X pJ Nm O N N O• p < S •r e ° d O 7 O M 0. O?? ° S d a W a Z l0 o a• '• 06 W W O? E N Z y 2 z p p o 2 n � m v o 'r 0 a d ° u n �'o= m po 3 i" 'p or a od sF 0 0, 1Nn w, x �' c pl ry o Nd o p R ` 9 3 ' O< a s 13 a F S `c C G N Wetland 1 - Unit 1: -Depressional -PFO, PSS, PEM -Saturated PEM - v -,Wetland :l Wetland 1- Unit 2: -Slope .-PEM (dense, uncut) -Saturated rota }ittenVy fimvditch io Wetland 1 - Unit 3 (continues offsite): -Depressional , -Abuts West Fork Hylebos Creek -Saturated and occasionally inundated ->1/4 acre of PFO, PSS, and PEM Figure 1 Legend Wetland 1 Map _ _ .. Estimated Wetland Gethsemane Boundary Cemetary Delineated Wetland Culvert (approx. Boundary r location) Wetland Delineation on Gethsemane _ Cemetary, Federal Way, WA Wetland Area I x- Data Point Note: Basemap provided byArcGIS Onli -Municipal and wetland data is fron City of Federal Way. -All project speck data was made Otak Inc. 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M m o ti m n m o a c- $ ^^ w g F °?oo mg ao R c.-p F n m g wnw z y z zTI o O 2 z j Figure'l Wetland 14 Map Wetland Delineation on Gethsemane Cemetary, Federal Way, WA I[-1 nmlar11i7R(InLi 7fi541CA DrYe IgWYD&lFm 137 E 19 'I afusthrle ernergent (F 2T no outlet 3) 5❑%4 urzFted only, 5- oc.`casio .611y flooded Legend _ _ _ _ Estimated Wetland Gethsemane Boundary Cemetary Delineated Wetland (x Data Point Boundary — =`• I Wetland Area Note: Basemap provided by ArcGIS Online. -Municipal and wetland data is from City of Federal Way. _All project specific data was made by Otak, Inc. 1 inch = 100 feet Feet+ 0 100 Date: 2M/2016 OVli RXj Qg.R.LI ri [p17aa�.a �5 n E-I u R � 9Rjmg C C nRog ;7 N :.I NO k (p .4 5 r I a.. I CD MA s'.~r 7. e I� i6 - 11 I s b r m 4` I, ip 1 N 59lh AVe NE vRF 39th Ave CIE a nJ AVe E ry= n$iln AVc N E m AM AVg @ GUM AvaE 316AVO$W $ vaa:AYee . rsE - - �+ Pacific llwy ai =irk 3S r CL C{� t c 1, ;0 i Aa•. ' O F o, 1 T ff, ldl�IlvnRlg•. 17Hr w N r7 .I h� 0 N ti 5p �I . d tQ 7011. AV.-S Z o N � n � I � y w A w m mr.o mo Z . - ]dlh Ave9 E V iD g i � r v� P 42nd ave5 &e I _ 11rd AvC 5 a 3 —45W Ade3ra _- - — - - JOFY IIIYIi N 444h Ave 5 !1'1lam gvaE 1 _� } !&d AV-3 m 126 /f 1` �7w VA — 1 CD Cn j v n o 3 n n n n d •e 3 n n n oC m0 n- 3 3 nT 3 m 3 3 n � � a a O s V d C L y G d m Or o (� 6 Q A � K to a S. 0 + � z F n 3 0 O n n m 2 S a� oT .. C.O •i a 2 o^ p n c m C a R b p VI ^ G lT v � � �J a - m - e F^ � n d de OtJ h T X O a 3 z ro l o 0 3 �• � ei F d 3 D LA d13d v � —�a 3 3 � 3• D � 1 N n ry"1 jiji R S 2 a i� s a� v a Appendix E Plant Species Observed within the Study Area Table E-1. Plant Species Observed within the Study Area Genus Species Common Name WIS* Acer circinatum vine maple FAC Acer macrophyllum big -leaf maple FACU Agrostis capillaris bentgrass FAC Alnus rubra red alder FAC Anthoxanthum odoratum sweet vernalgrass FACU Athyrium filix-femina lady fern FAC Carex obnupta slough sedge OBL Cirsium arvense Canada thistle FAC Corpus sericea redstem dogwood FACW Dactylis glomerata orchard grass FACU Elymus sp. ryegrass, wheatgrass NI Epilobium sp. willowherb FACU Equisetum arvense field horsetail FAC Festuca rubra red fescue FAC Fraxinus latifolia Oregon ash FACW Gaultheria shallon salal FACU Geum macrophyllum large -leaf avens FAC Holcus lanatus common velvetgrass FAC Ilex aquifolium English holly FACU Juncus effusus soft rush FACW Lolium perenne perennial ryegrass FAC Lysichiton americanus yellow skunk cabbage OBL Oemleria cerasiformis Osoberry FACU Phalaris arundinacea reed canarygrass FACW Poa pratensis Kentucky bluegrass FAC Polystichum munitum sword fern FACU Populus Trichocarpa black cottonwood FAC Potentilla ansenne ssp. pacifica Pacific silverweed OBL Pseudotsuga menziesii Douglas fir FACU Pteridium aquilinum bracken fern FACU Ranunculus repens creeping buttercup FAC Rosa nutkana Nootka rose FAC Rubus armeniacus Himalayan blackberry FACU Rubus laciniatus evergreen blackberry FACU Rubus spectabilis salmonberry FAC Rubus ursinus trailing blackberry FACU Rumex crispus curly dock FAC Salix lasiandra Pacific willow FACW Gethsemane Cemetery February 25, 2016 Wetland and Stream Delineation Report Salix sitchensis Sitka willow FACW Sambucus racemosa red elderberry FACU Scirpus microcarpus small -fruited bulrush OBL Spiraea douglasii Douglas spirea FACW Stachys cooleyae Cooley hedgenettle FACW Symphoricarpos albus Common snowberry FACU Taraxacum officinale common dandelion FACU Thuja plicata Western red cedar FAC Urtica dioica stinging nettle FAC Veronica americana American brooklime OBL * Wetland Indicator Status (WIS) per Lichivar, et al. (2014): OBL = occurs in wetlands > 99% of time FACU =occurs in wetlands 1-33% of time FACW = occurs in wetlands 67-99% of time UPI, =occurs in uplands > 99% of time FAC = occurs in wetlands 34-66% of time NI = no indicator Gethsemane Cemetery February 25, 2016 Wetland and Stream Delineation Report