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20130331 RESUBMIT Critical Areas Mitigation Report 05232014WETLANDS )LIFE Environmental Consulting MBFx PwPEarir (aTy of Yews, Wig THUFzsToN Counrrr PARCEL #27192403000 Prepared For: U. Randy V\bber 26550 SE 354th Place Black Diamond, VVA 98010 Prepared By: V 4§tlands & Wildlife, Inc. 7721 -153rd Street SE Snohomish, V\bshington 98296 (425) 337 -6450 Original Report Date: June 10, 2013 Revised Report Date: May 23, 2014 V-507 11E►Iti INTRODUCTION AND BRIEF SITE DESCRIPTION 1 STATEMENT OF QUALJFICATIONs TO CONDUCT THS CRITCAL AREAs EVALUATION 1 NIETHODOLOGIEs OF CRITICAL AREAS EVALUATION 2 F?EsuLTS AND FINDINGS OF CRITICAL AREAS EVALUATION 3 ExISTING FUNCTIONS ANDVALUEs ANALYSIS 4 DISCUSSION REGARDING M-nGATION SEQUENCING 6 PROPOSED COMPENsAToRY M-nGATION EFFORTS 7 DISCUSSION REGARDING REQUIRED FINANCIAL QIARANTEE 8 M-nGATION PLAN PERFORMANCE STANDARDS, MONITORING, MAINTENANCE, AND CONTINGENCY 8 HABITAT ASSESSMENT :.• in ►I'. dal : +►I ►_ 1•► I MIA L• f E I 10 LJMTATIONs AND USE OF THs REPORT 12 REFERENCES AND UTERATuRE FE\ABAED 13 ATrACHMENTs: 1. V%t LAND DETERMINATION DATA FORMS (4 DATA Paws ON -SITE) 2. DOE M7LAND RATING FORM FOR WESTERN WASHNGTON (1 RATING FORM) 3. CRITICAL AREAS & M-nGATION PLAN MAP MAP SHEET CA1.00 INTRODUCTION AND BRIEF SITE DESCRIPTION The subject property is located northwest of the intersection of Rhoton Road SE and Northern Pacific Road NW in the City of Yelm, V\Lashington. This site is further located as a portion of Section 19, Township 17N, Range 2E, W M. The Thurston County tax parcel number for the property follows: 22719240300. Per information obtained from the Thurston County Assessor's Office, the site encompasses approximately 7.51 acres and is zoned for Industrial use. The property is currently owned by Randy and Linda V\bber, also the applicants for the proposed grading permit. Vehicular site access is gained from the east via Rhoton Road SE. The property is currently undeveloped and is generally level, with the western border occupied by Yelm Creek (a Type 5 stream) and an associated Category III wetland. In the City of Yelm, Yelm Creek on the subject site is afforded a Riparian Habitat Area that extends to the outer edge of the floodplain (frequently flooded area), while Category III wetlands with habitat scores of less than twenty points receive 80 -foot protective buffers. The property owner retained Vttlands & Wldlife, Inc. to evaluate the site features and assist with complying with provisions of the Yelm Municipal Code (YMC), Chapter 14.08 (Critical Areas and Resource Lands). Vtt/ands & Wldlife, Inc. conducted site visits to the subject property on February 18, 2013 and May 9, 2013 to perform a detailed Critical Areas evaluation of the site, pursuant to the YMC and professional industry standards. Vtt/ands & Wldlife, Inc. delineated the regulated Critical Areas on the site on May 9, 2013. The delineated Critical Areas locations and other site features are depicted on the attached Critical Areas & Mitigation Plan Map (Map Sheet CA1.00). Please review the attached map and seethe REsuLTs AND FINDINGS OF CwTICALAREAs EvaLuA-noN section of this report for further information. STATEMENT OF QjAuFICATIONS TO CONDUCT TI-IS CRITICAL AREAs EVALUATION Section 14.08.050..1 requires applicants to submit a Critical Areas Report prepared by a qualified professional to the City for review. The following provides a brief overview of my experience and credentials to conduct this Critical Areas evaluation. I am the Founder, Owner, and Principal V\btland and VVIdlife Ecologist of Vttlands & Wldlife, Inc. I attended the University of Montana where I graduated cum laude with a degree in Wldlife Biology. As of 2014, 1 have 13 years of direct experience as a professional Biologist/Ecologist in westem Washington and 17 years of overall experience completing natural resource assessments among many different ecosystems across the western United States. I have worked as a professional Biologist/Ecologist for federal, state, and county environmental agencies, as well as several private environmental consulting firms with specialties in wetlands, streams, rivers, lakes, and wildlife habitat. In my 17 years of experience, I have specialized in review of proposed land use and building development permit applications as they pertain to Critical Areas (wetlands, rivers, streams, lakes, and habitats of protected fish and wildlife species). Much of that experience came as a Senior Reviewing Ecologist for King County DDES and a Regulatory Biologist for Snohomish County PDS. I am listed on several Preferred / Qualified Consultant Rosters throughout western Washington. I am highly experienced with the required U.S. Ammy Corps of Engineers and Washington state wetland delineation methods. In addition to the wetland delineation certification, I am trained by the Washington Department of Ecology and have 9 years of experience in the use of the required V\btland Rating Form for western Washington. I am trained by the Washington Department of Ecology to determine Ordinary High Water W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, V\bshington (Tax Parcel #22719240300) Page 1 Mark (CHVV\ 1) locations for rivers, streams, and lakes. In addition to my expertise related to wetlands and streams, I have many years of experience conducting surveys of special status wildlife species in the western U.S. I received certifications from the Washington Department of Fish and VVIdlife for terrestrial wildlife habitat assessments and wildlife surveys of special status wildlife species in Washington. Over the past 17 years, I have conducted literally over 1,300 biological / ecological assessments in different capacities on properties with many habitat types and zoning designations, from small, urban properties (0.25 acres) to large, rural properties (up to 2,000 acres in size). I have been selected by several local city agencies to provide on -call 3rd -party environmental reviews of proposed projects for ooWliance with local Critical Areas Ordinances and the FEMA Fioodplain Habitat Assessment requirements. WTHom_o m OF CRn1cAL AREAS EVALUA110N VWlands & W/dlife, Inc. used methodologies described in Determininq the Ordinary High Voter Mark on Streams in Vashington State (Washington Department of Eoology Publication #08-000 001, April 2008) to make a determination regarding the Ordinary High Voter Mark (CHVV\ 1) of the stream located on the subject site. The routine methodologies described in the Vashington State Vatlands Identification and Delineation Manual (Vashington State Department of Ecology Publication #96 -94, March 1997) were used to make a determination of wetlands, as required by the City of Yelm. In addition, Ktt/ar7ds & W/dlife, Inc. evaluated the site using the U.S. Amory Corps of Engineers Vatland Delineation Manual produced in 1987 and the U.S. Amory Corps of Engineers Regional Supplement to the Corps of Engineers Vatland Delineation Manual: Vastem Mountains, Valleys, and Coast Region produced in May 2010 (hereinafter referred to as "the Corps Regional Supplement "). The Corps Regional Supplement is designed for concurrent use with the 1987 Corps Vatland Delineation Manual and all subsequent versions. The 2010 Regional Supplement provides technical guidance and procedures for identifying and delineating wetlands that may be subject to regulatory jurisdiction under Section 404 of the Gean Water Act. V\here differences in the two documents occur, this Regional Supplement takes precedence over the Corps Manual for applications in the Vastem Mountains, Valleys, and Coast Region. According to the federal and state methodologies described above, identification of wetlands is based on a three - factor approach involving indicators of hydrophytic vegetation, hydric soils, and presence or evidence of persistent hydrology. Except where noted in the manuals, the three - factor approach discussed above requires positive indicators of hydrophytic vegetation, hydric soils, and wetland hydrology to make a determination that an area is a regulated wetland. Using the aforementioned manuals, the site characteristics for making a wetland determination include the fdlowing: 1.) Examination of the site for hydrophytic vegetation (species present/percent cover); 2.) Examination for the presence of hydric soils in areas where hydrophytic vegetation is present; and 3.) Examination to determine if adequate hydrology exists for suf iident durations during the early part of the growing season in the same locations as the previous two steps. Per industry standards, VW/ands & W/dlife, Inc. examined the entire sul�ect site. Per current City of Yelm W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Veshington (Tax Parcel #22719240300) Page 2 requirements, Vet /ands & W/dlife, Inc. also assessed adjacent properties within 300 feet of the proposed project limits, to the maximum extent possible without entering adjacent properties. V\,hile a detailed assessment of critical areas on adjacent properties was not possible due to lack of legal access, Vtt/ar7ds & Wldlife, Inc. conducted a review of all available information to assess the presence of off -site critical areas within 300 feet of the sulm ect site. This review is necessary to determine if any regulated Critical Areas exist off -site which would cause associated protective buffers to extend onto the property and affect the development proposal. In addition to on -site field reviews, Vtt/ands & W/dlife, Inc. examined aerial photographs and topographical data (elevation contours) on Thurston County's GeoData maps. Soil survey maps produced by the Natural Resources Conservation Service (NRCS), National V\btlands Inventory maps produced by the U.S. Fish and VVIdlife Service (USFV\I SalmonScape fish distribution maps produced by the Washington Department of Fish and VVIdlife OADF\N, StreamNet fish distribution maps produced by Pacific States Marine Fisheries Commission, the Washington State Department of Natural Resources Forest Practices Application Review System Water Type Maps, and Priority Habitats and Species (PHS) maps produced by VDFWwere also evaluated as part of this project evaluation. The boundary of the sulm ect stream and wetland were delineated using bright pink ribbon (highly visible). These flags were then located by a professional surveyor. After the delineation flags were located using this method, Vtt /ands & W/dlife, Inc. imported the flag location data into a computer -aided drawing (CAD) program to depict the wetland boundary location on -site in relation to the property boundary and other existing site features. Yelm Creek (Type 5 stream) and an associated Category III wetland are located on the western portion of the sulm ect site as shown on the attached Critical Areas & Mitigation Plan Map (Map Sheet CA1.00). No other regulated Critical Areas were located on or near the sulm ect site that would affect the proposed development. Co %ardin Classifications: According to the Canrardin System, as described in Classification of Vatlands and Deepwater Habitats of the United States, the classifications for the sulm ect wetland and stream follow. Yelm Creek: Riverine, Intermittent, Streambed, Cobble - Gravel (R4SB3). Wetland A Palustrine, Emergent, Persistent, Seasonally flooded / Saturated (PEM1 E). City of Yelm Code Classifications: Per the Yelm Municipal Code (YMC), Chapter 14.08 (Critical Areas and Resource Lands), the sulm ect wetland and stream are classified as follows: Wetlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, V\Ion (Tax Parcel #22719240300) Page 3 Yelm Creek flows north along the western border of the subject site. The on -site reach of Yelm Creek is an intermittent (Type 5) stream that is dry for much of the year. Type 5 streams in the City of Yelm typically receive a protected 150 -foot Riparian Habitat Area. However, when frequently flooded areas exceed the 150 -foot riparian habitat area width, the riparian habitat area shall extend to the outer edge of the frequently flooded area. Therefore, the effective Riparian Habitat Area of the stream extends to the edge of the frequently flooded area (100 year floodplain). Wetland A is located entirely within the CFMAM of Yelm Creek. Per industry standards and City of Yelm requirements, V\btland A was rated using the Revised V\btland Rating form for VV�stem V\bshington. The wetland appears to meet the outlined criteria for a "Riverind' wetland. Therefore, the hydrogeomorphic (HGM) loss used to rate the wetland is a "Riverine" wetland on the V\btland Rating Form. Using the V\tland Rating Form, the subject wetland scored a total of 45 points (14 points for Water Quality Functions, 16 points for Hydrologic Functions, and 15 points for Habitat Functions) and is therefore considered a Category III wetland. The rating form is attached to this report for viewing. Per YMC 14.08.100F.6, Category III wetlands with habitat scores of less than 20 points, typically require a standard buffer width of 80 feet to be applied parallel to the wetland boundary. Therefore, the standard buffer Width required for Wetland A equals 80 feet. Please see the attached Critical Areas & Mitigation Plan Map (Map Sheet CA1.00) for a depiction of V\btland A and the associated buffer. On -site Vegetation and Soils Data: Vttlands & Wldlife, Inc. collected detailed vegetation and soils data at four different locations on the subject property to gain representative data regarding on -site vegetative and soil characteristics. Please view the four V\tland Determination Data Forms (produced by the Army Corps of Engineers) which describe the actual vegetation and soil characteristics at each data point location. The data forms are attached to this report, and are labeled as DP1 through DP4. Please also view the location of these data points (labeled as DP1 through DP4) shown on the attached Critical Areas & Mitigation Plan Map (Map Sheet CA1.00). Natural Resource Conservation Service Soi ls Description: The Natural Resources Conservation Service (NRCS) mapped the subject property as being underlain by Spanaway gravelly sandy loam, 0 to 3 percent slopes. Spanaway gravelly sandy loam, 0 to 3% slopes is described by the NRCS as a moderately deep, somewhat excessively drained sal on terraces and oc.tvash plains. This soil formed in volcanic ash over gravelly outwash. The surface layer is gravelly sandy loam from 0 to 15 inches below the surface. From 15 to 20 inches below the surface, soils are very gravelly sand. The subsoil in extremely gravelly sand from 20 to 60 inches below the surface. Available water capacity of this soil is low. Spanaway and similar soils comprise this entire unit. Bas-1w FUNCTIONS ANDVALUES ANALYSIS The methodologies for this functions and values analysis are based on professional opinion developed through past field analyses and interpretations. This assessment pertains specifically to the subject wetland W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Veshington (Tax Parcel #22719240300) Page 4 and stream system, but is typical for assessments of similar systems throughout western Washington. The three main functions provided by wetlands include water quality, storn3 ater / hydrologic control, and wildlife habitat. The on -site wetland and stream corridor is comprised primarily of weedy grass land with some patches of scrub -shrub vegetation. V\hen flowing, Yelm Creek provides important functions to its surrounding environment such as hydrological transport, transport of solids (suspended and dissolved), and important fish and wildlife habitat features, among other functions. As discussed previously in this report, the on -site reach of Yelm Creek is an intermittent stream that is dry for much of the year. As a result, this stream has a limited ability to provide the above functions. However, even when not flowing on the surface, this reach of Yelm Creek likely supplies hydrology to fish bearing portions of the stream located downstream. The dense shrubs among parts of this riparian corridor provide very important ecological functions. In addition to providing direct habitat for wildlife species, the dense shrubs among the riparian corridor provide very valuable shade and a source for the future recruitment of large woody debris (LV\D) and organic matter to the stream and wetland environments. V\tlands in westem V\bshington often contain necessary wildlife habitat resources such as food, water, thermal cover, and hiding cover in close proxia *, and the sul�ect wetland and stream provide a secure corridor for wildlife movement. The wetlands and associated buffers provide protected habitat, which beoanes increasingly important as areas become further populated with humans and habitat areas become fragmented. The established, emergent vegetation serves to intercept rain fall before it strikes the sal, thereby reducing erosion and improving water quality. Furthermore, the dense vegetation and adsorbent soils serve to trap sediment and pollutants and provide increased water quality functions to aid in a reduction of sediment which results in cleaner water leaving the site. The association of this wetland to Yelm Creek allows it to moderate stream flows (when flowing) by adsorbing water during storm events and slowly releasing it during periods of lower flows, as well as to help maintain base flows. Please see Map Sheet CA1.00 which depicts the project proposal on the project site. The applicant is proposing to raise the elevation level of the eastern portion of the property through placement of fill materials to an approximate elevation level of 335 feet above sea level. The eastern portion of the property is located outside of all wetlands, stream, and fish and wildlife habitat conservation area but is currently mapped as being located within a FEMA flood hazard area. The applicant is proposing to fill 132,264 square feet of area located among the eastern portion of the on -site flood hazard area. Based on information from the project engineer, the project proposal will result in a total volume of approximately 3,650 cubic yards of fill material being placed in this portion of the flood hazard area, and will modify the flood hazard area to eliminate this area from the floodplain of Yelm Creek During this construction process, the applicant is proposing to scrape the topsoil from this proposed fill area and stockpile the topsoil for future placement among the proposed restoration planting areas in the western portion of the site. In order to provide equivalent potential flood storage capacity on the site, the applicant is proposing to W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Veshington (Tax Parcel #22719240300) Page 5 remove (cut) 3,650 cubic yards of existing soil (equivalent volume to that which is proposed for fill) from 83,350 square feet of area which is located among the western portion of the property. This project will result in a balanced cut and fill volume, and the proposed cut will maintain the level of flood storage capacity that currently exists on the site, while also creating a more connected floodplain for Yelm Creek. After this project is completed, the Riparian Habitat Area associated with Yelm Creek will extend further east on the property than it currently does, and will extend out to the eastern edge of the newly created flood hazard areas (perYMCsection 14.08.140.D.2.c.ii). The proposed project will avoid impacts to Yelm Creek and the associated riparian wetland. However, the proposal will result in unavoidable temporary grading impacts to much of the western portion of the property, including portions of the on -site buffer for Yelm Creek and associated wetland. The proposed grading areas have been heavily disturbed in the past (dump truck piles of fill material can be seen in several locations), contain large quantities of Scots broom (Cytisus scoparius, Nol /Upl), and currently provide a relatively loN level of ecological functions and values. The vast majority of the proposed grading areas are currently dominated by Scots broom, currently classified as a Gass B noxious weed in V\Lashington State. Al Scots broom within the project work areas will be removed and transported to an approved off -site location as part of this project. To ensure that no loss of ecological functions and values occurs on the site or within close proximity of Yelm Creek, the applicant is proposing to retain large patches of existing native, intact trees and shrubs which are located among the northwestern portion of the site (see Map Sheet CA1.00 for locations). After the grading efforts have been completed, the applicant is also proposing to restore the entire 83,350 square feet of temporarily impacted Riparian Habitat Area by planting native trees and shrubs as described below. DISCUSSION REGARDING Nr11GA11oN SEQUENCING Pursuant to YMC 14.08.050.D, the applicant explored other development options which would avoid or minimize impacts to the on -site flood hazard areas. However, due to the location and extent of the flood hazard area on the site it would be difficult to derive a reasonable use of the property while avoiding all impacts to the floodplain. It is not reasonably feasible to accomplish this proposed project except as outlined in this report and shown on project plans. In addition, it is the professional opinion of Vet /ands & W/dlife, Inc. that implementing this proposal will actually increase and improve the ecological functions floodplain environment by creating floodplain that is more connected to Yelm Creek than the current floodplain. The applicant is proposing to minimize impacts to the floodplain and the Riparian Habitat Area by placing the proposed building pad in the eastern portion of the site, adjacent to Rhoton Road SE in a portion of the floodplain that is partially isolated from Yelm Creek by the presence of the Centex property and piles of fill material to the south. In addition, the applicant is proposing to limit the creation of the compensatory flood storage area to portions of the site that currently contain a high percentage of invasive species and provide a loN level of functions and values. By creating con-pensatory flood storage area nearer to Yelm Creek, preserving native vegetation on the site, and restoring/enhancing the flood storage area with beneficial native trees and shrubs, it appears that the potential ecological lift to functions and values outweighs a no-action approach and will provide more ecological benefits to the nearby environment, and to the Yelm Creek drainage basin overall. W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Veshington (Tax Parcel #22719240300) Page 6 ''•'•7 • N&72% •' • •' To ensure that no loss of functions and values occurs to the flood hazard areas or on -site critical areas, the applicant is proposing to restore the entire 83,350 square feet (1.91 acres) of cut with native trees and shrubs. During grading, topsoil in the proposed cut area should be reserved and stockpiled on -site. This should be replaced on the surface of the cut at a minimum depth of six inches to ensure a suitable planting medium. Please see Map Sheet CA1.00 for a depiction of the proposed restoration area on the subject site. Per industry standards and guidelines, this mitigation proposal includes calculating required plant quantities by planting 60% of the mitigation area with native trees and planting 40% of the mitigation area with native shrubs. The native trees are proposed to be planted on 12 -foot centers (spaced a minimum of 12 feet apart), while the native shrubs are proposed to be planted on 6 -foot centers (spaced a minimum of 6 feet apart) among the mitigation areas. Using this approach, the applicant is proposing to plant a total of 348 trees and 924 shrubs among the buffer restoration area, as outlined in the table below. Proposed Buffer Restoration Plantings (quantities based on 83,350 SF) CaT= Nam Latin Name Sim 09 SP99 Quantity 1. Douglas fir Pseucbtsuga menziesii 1 Mien 12 ft. min 87 2. Big -leaf maple Acerrracrophyllum 1 -gallon 12 ft. min 87 3.Oregcn Mite oak Quercus gan yang 1 Mien 12 ft. min 87 4 Black cottonwood Fbpu/us ba/sarrifera 1-gaIIon 12 ft. min 87 5. Snowberry *Thoricalpos albus 1 -gaIlcn 6 ft. min 154 6. Serviceberry Arre/anchiera/nifolia 1 gallon 6 ft. min 154 7. Hazelnut Cay/us comuta 1 gallon 6 ft. min 154 8. Nootka rose Rasa nutkana 1 gallon 6 ft. min 154 9.Osoberry Oariaia oaasifarris 1 gallon 6 ft. min 154 10. Oregon grape Babais rawsa 1-gdlcn 6 ft. min 154 Prior to any earthwork within or near Critical Area buffers, temporary erosion and sediment control measures (silt fence or similar best management practices) will be installed around the proposed disturbance limits to minimize potential erosion from reaching the adjacent wetland and stream. Please see Map Sheet CA1.00 for a depiction of the proposed conceptual mitigation plan associated with the required Critical Areas Variance on the project site. The applicant is proposing to seed all bare ground areas which are temporarily disturbed as part of this project immediately upon oompletion of the grading. To aid in soils stabilization, all bare ground areas within the impacted buffer area shall be seeded to the grass seed mixtures below, or a similar grass seed mixture: CoTmon Name Latin Name lbs. /1,000 s.f. Colonial bentgrass Agrostis tenuis 0.6 Red fescue Festuca rubra 0.3 V\hiteclover Trifoliumrepens 0.2 W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, V\bshington (Tax Parcel #22719240300) Page 7 The silt fence and all erosion and sediment control measures will remain in place until the soil is sufficiently stabilized to prevent erosion of soil in dose proximity to Yelm Creek and the associated riparian wetland. DISCUSSION REGARDING REQUIRED FINANCIAL GUARANTEE A performance bond shall be provided to the City of Yelm for the period of five years from the completion of the project, in the amount of 150% of the estimated oust of the uncompleted actions. Annual monitoring reports and seasonal maintenance will be required to assure the success of this enhancement plan. Yelm shall release this bond at the end of five years, upon a determination that all portions of this mitigation project have succeeded per the performance standards outlined in this report. The following is an estimate of plant materials and labor only, and does not represent a bid to install: ESTIMATED COST OF PLANT MATERIAL AND LABOR (1,272 plants @$9.50 /plant) $12,084.00 ESTIMATED COST OF MONITORING @$600 / YEAR FOR 5 YEARS $3,000 ESTIMATED COST OF MAINTENANCE @$600 / YEAR FOR 5 YEARS $3,000 EST MATED COST OF GRASS SEED $50.00 TOTAL EST MATED COSTS TO I MPLEMENT THI S MITI GATT ON PLAN $18,134.00 TOTAL BOND AMOUNT (150% OF TOTAL ESTIMATED COSTS) $27,201.00 Nr11GA11oN PLAN PERFORMANCE STANDARDs, MONITORING, MAINTENANCE, AND CONINGENCY Goals and Objectives of the Mitigation Plan Time primary goals of the mitigation plan described above follow. 1. OFF -set all proposed Riparian Habitat Area impacts associated with the proposed development described above; 2. Remove the non - native, invasive vegetation among the restoration area; 3. Increase the quantity & diversity of native vegetation within the Riparian Habitat Area; and 4. Allow for responsible residential development and associated infrastructure, while also increasing the ecological functions provided by the on -site stream, wetland, and Riparian Habitat Area. Mitigation Plan Installation Inspection and As -Built Report Following the installation of the compensatory mitigation plan components detailed in this report, the applicant will contact Mdands & Wldlife, Inc. or another qualified professional of their choosing to conduct a site visit to confirm that all mitigation plan components have been implemented as outlined in this report. After conducting that installation inspection, Mdands & Wldlife, Inc. will prepare a Mitigation Plan As -Built Report and submit that report to the City of Yelm. Time As -Built Report will provide confirmation that the plan was implemented as outlined, or detail any minor adjustments required to the mitigation plan during its on -site implementation. Time 5 -year monitoring and Abdands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, V\bshington (Tax Parcel #22719240300) Page 8 maintenance period associated with the project will begin after the As -Built Report has been reviewed and approved by the City of Yelm, or assigned representatives. Success Criteria / Performance Standards: The applicant proposes to meet the following plant cover and survival standards among the on -site mitigation areas in an attempt to measure success of the proposed mitigation planting plan and compensate for project impacts among the on -site stream buffer: Performance Standards Monitoring Year after installation Year One Year Two Year Three Year Four Year Five Shrub and Sapling Tree Cover* >30% >30% >50% >60% >75% Shrub and Sapling Tree Survival 100% >90% >80% >80% >75% Percent Non- native, Invasive Species <20% <20% <20% <20% <20% *Note: The performance standards above include beneficial native plants in that naturally pioneer in the planted area. Monitoring and Maintenance Duration and Schedule: Pursuant to the Qty of Yelm standards and requirements, approved / installed mitigation projects shall be monitored for a minimum of five (5) years from the date of plant installation to ensure that the performance standards outlined in the approved mitigation plan have been met. Vttlands & W Idlife, Inc. or another qualified professional will conduct one (1) annual monitoring visit to examine the status and determine success among the mitigation areas. During the first annual monitoring site visit, representative photo points shall be established among the mitigation areas. The photographs taken at these photo points shall provide a general overview of the mitigation areas. Photographs shall be taken from the same photo points during each subsequent monitoring visit to provide visual information from known locations. The qualified professional will submit one (1) annual progress report to the City of Yelm for the first four (4) years of the monitoring period. These annual monitoring reports shall assess both achievement of yearly goals and progress towards overall achievement of the project goals. Monitoring reports will include an assessment of the approximate percent cover of native vegetation, presence of invasive vegetation, any other ecological concerns or recommrriendations among the mitigation areas, and overall effectiveness of the mitigation site. A final monitoring report will be submitted to the City of Yelm at the end of the fifth (5th) year to ensure that the performance standards outlined in the mitigation plan have been met. During the 5-year monitoring period, the applicant or retained professionals shall also perform maintenance of the mitigation area(s) in accordance with industry standards and guidelines. Maintenance may include regular watering, weeding around the base of installed plants, pruning, replacement plantings as necessary to achieve performance standards, removal of all noxious and invasive weeds, and any other measures needed to ensure performance standards are met throughout the mitigation areas as outlined above. If the project meets all of the criteria for success at the end of the five -year monitoring period, no further action will be required by the applicant and the financial guarantee amount described above will be returned to the applicant in full. If the definition of success is not met for any reason at the end of the five- W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, V\bshington (Tax Parcel #22719240300) Page 9 year monitoring period, the maintenance and monitoring period will be extended for one year at a time until the site meets the performance standards outlined. This mitigation plan and the accompanying maintenance and monitoring will not be considered fully complete until written confirmation is received from the City of Yelm. Likelihood of Success associated with this Compensatory Mitigation Proposal: Pursuant to YMC section 14.08.050.E.1.c, this mitigation proposal will be implemented in a manner which provides a high chance of meeting the success criteria and perfommance standards previously outlined in this report. The applicant will install the mitigation measures in the appropriate time of year (plant in the late fall or early spring). Al non- native, invasive vegetation within the mitigation area will be removed from the mitigation planting area. As previously described, the applicant will provide regular monitoring and maintenance of the planting area over a minimum of a 5-year period. Due to this information and all other information outlined in this report, it is the professional opinion of Kttlands & Wldlife, Inc. that this mitigation proposal has a high likelihood of success, as long as the compensatory mitigation measures are implemented as outlined in this report and ecological industry standards are used for all project commponents. Please also see below for a discussion regarding contingency plans. Contingency Plan Related to Plant Success: If it is determined at any time during the monitoring period that the performance standards or goals of the mitigation plan are not being met, a contingency plan will be devised to improve or alter those elements that are deficient. If measures beyond standard maintenance of the mitigation areas are required, a plan containing these measures shall be submitted to the City of Yelm for their review prior to implementation. Contingency Plan Related to Property Ownership: If the sulmect properties change ownership at any time during implementation of the proposed mitigation plan described above, or during the 5-year monitoring and maintenance period associated with the proposed mitigation plan, the current property owner(s) shall inform the prospective real property purchaser(s) of the mitigation requirements. The proposed mitigation plan shall run with the land (in perpetuity), and the current property owner(s) shall ensure that the approved mitigation components are implemented as stated, monitored for compliance with the performance standards outlined in this plan, and maintained in accordance with this plan and ecological industry standards. HABITAT ASSESSMENT Typical vegetation over the subject site is dominated by Scots broom (Cytisus scoparius, Nd /Upl), with smaller amounts of serviceberry (Arralanchier atnifolia, FacU), Oregon grape (Berberis nervosa, FacU), colonial bentgrass (Agrostis tenuis, Fac), and common vetch (Vaa sativa, Upl) present in portions of the site as well. Black locust (Rcdt is pseudoacacia, Nol /Upl) trees are also present in the northwestern portion of the sulm ect property. No endangered species are present on or adjacent to the subject site. No species of local importance, priority species, or endangered, threatened, sensitive, or candidate species are known to have a primary association with habitat on or adjacent to the project area. W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Veshington (Tax Parcel #22719240300) Page 10 Threatened winter Steel head (Oncorhynchus n yldss) are known to utilize the lower reaches of Yelm Creek (west of NVV Crystal Springs Road) for rearing and migration. Mazama Pocket Gophers (7horrorrys rrazarra) are mapped by V\DFVV as occurring approximately 0.7 miles northwest of the subject site. Mazama Pocket Gophers are currently classified by V\DFVVas a State Threatened species. A communal roost of State Candidate, Townsend's big-eared bats (Caryraorhinus townesendii) is located approximately 0.78 miles to the south of the subject site. The 0.7 mile distance of the project site from the Mazama Pocket Gopher colony is well outside of the 5.64 -meter radial buffer distance needed to protect this species. VUhile no buffer setback is reco amended for Townsend's big -eared bats, the proposed project will not disturb suitable roosting habitat crucial for the bats survival which include caves, mines, hollow trees, and built structures such as bridges and silos. The distance of the project from these species is also well outside of the 100 feet at which the project- related construction noise is anticipated to attenuate to the ambient (existing baseline) noise level. For a detailed description of haN the 100 -foot distance was detemired, as well as for a detailed assessment of the impact that the proposed project will have on threatened fish species, please refer to the FEMA Fioodplain Habitat Assessment associated with this project which was prepared by Mdands and Wldlife, Inc. Given the distance of the proposed project from the above species, and the fact the project - related construction noise is anticipated to attenuate to the ambient noise level within 100 feet, the proposed project is anticipated to have no effect on State Threatened Mazama Pocket Gophers or on State Candidate, Townsend's big-eared bats. Furthermore, the FEMA Fioodplain Habitat Assessment determined that this project will also have no effect on threatened fish species. No other special- status species are known to exist on the site, and no special- status species are expected to utilize the site for habitats of primary association. Therefore, this project is not expected to adversely affect any special- status fish or wildlife species. In fact, the proposed mitigation plan associated with this project will likely create beneficial ecological effects for wildlife species when compared to existing site conditions. PROJECT° s I NPACT DETER NA-ION Ra -ATED To CRn1CAL AREAS The current floodplain location is not located in a landscape position (context) where it is able to provide the most beneficial ecological functions to Yelm Creek. The current floodplain located among the eastern portion of the site is nearly entirely disconnected from Yelm Creek due to a significant amount of man -made disturbances such as fill, impervious surfaces, and industrial land use activities (see Figure 4 attached to this report). The proposed increase in floodplain area closer to Yelm Creek would allow for more effective and natural floodplain processes to occur. In addition, the applicant is proposing to create compensatory flood storage area among portions of the site that are currently dominated by non- native, invasive vegetation (Scots broom) and therefore provide a low level of ecological functions. By creating compensatory flood storage area nearer to Yelm Creek, preserving native vegetation on the site, and restoring/enhancing the flood storage area with beneficial native trees and shrubs, the proposed project will provide an ecological lift to the level of functions and values provided by this site. Pursuant to YMC section 14.08.120.E.6, the proposed project will not block any existing side channels of Yelm Creek The proposed project will not inhibit natural channel migration processes and will not be located within a channel migration zone. There will be no loss of floodplain water storage capacity or increase in stonmmwater runoff to adjacent properties as a result of this project. In fact, this project will W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Veshington (Tax Parcel #22719240300) Page 11 significantly increase the connectivity between the existing eastern portion of the floodplain and Yelm Creek Some scrub -shrub vegetation will be impacted during the proposed project activities, and the applicant is proposing to replace all impacted vegetation by planting a total of 348 native trees and 924 native shrubs as outlined in this report. Floodplain refugia will be relocated from the eastern portions of the site to the western portions of the site, and will function more effectively during times when the area is flooded (due to a direct connection to Yelm Creek). No water quality impacts (increase in sedimentation or pollutants) are expected to occur as a result of this project, and temporary erosion and sediment control best management practices will remain in place and functioning until all soils are stabilized on the site. Based on the detailed site evaluation in conjunction with the applicant's proposal, it is the professional opinion of Vbt/ands & Wldlife, Inc. that no long -term adverse environmental impacts will occur to the on- site Critical Areas or associated buffers as a result of the proposed project. In fact, this project will result in an overall increase in ecological functions provided by the sul�ect site if all mitigation measures are implemented as stated in this plan. WTATIONS AND USE OF THS REPORT This Critical Areas Report & Proposed Mitigation Plan is supplied to Randy and Linda V\bber as a means of determining whether any wetlands, streams, and/or wildlife habitat conservation areas regulated by the Qty of Yelm Critical Areas Regulations exist on the site or within close proximity of the site which would affect the permit requirements of the proposed development on the site. This report is intended to provide information deemed relevant in the applicant's attempt to comply with the regulations currently in effect. The work for this report has conformed to the standard of care employed by professional ecologists in the Puget Sound region. No other representation or warranty is made concerning the work or this report. This report is based largely on readily observable conditions and, to a lesser extent, on readily ascertainable conditions. No attempt has been made to determine hidden or concealed conditions. If such conditions arise, the information contained in this report may change based upon those conditions. Please note that Vtt/ands & Wldlife, Inc. did not provide detailed analysis of other permitting requirements not discussed in this report (i.e. structural, drainage, geotechnical, or engineering requirements). The lawns applicable to Critical Areas are subject to varying interpretations. VUmile Vtt/ands & Wldlife, Inc. upheld professional industry standards when completing this review, the information included in this report does not guarantee approval by any federal, state, and/or local permitting agencies. Therefore, the work associated with this proposal shall not commence until permits have been obtained from all applicable agencies. If any questions arise regarding this review, please contact me directly at (425) 337 -6450. VWlands & Wldlife, Inc. Scott Sp0oner One-ierI Principal V\btland &VVIdlife Ecologist W,btlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Veshington (Tax Parcel #22719240300) Page 12 REFERENCES AND LJTERATURE REmB ED City of Yelm Munid pal Code. Chapter 14.08 (Critical Areas and Resource Lands). Yelm, Washington. Cowardin, et al, 1979. Gassification of VVatlands and Deepwater Habitats of the United States. U.S.D.I. Fish and Wildlife Service. FVVS/OBS- 79/31. December 1979. Environmental Laboratory. (1987). "Corps of Engineers VVatlands Delineation Manual," Technical Report Y- 87-1, U.S. Am-y Engineer Waterways Experiment Station, Vicksburg, Miss. Hruby, T. 2004. Washington State wetland rating system for vA?stem Washington - Revised. Washington State Department of Ecology Publication # 04- 06-025. National Marine Fisheries Service (NMFS). 2010. Endangered and Threatened Species under NMFS' Jurisdiction. (Updated February 28, 2013). SalmonScape. Interactive Mapping website administered by the Washington Department of Fish and Wildlife. http: / /wdfw.vva.goy/ mapping /salmonscape/index.html. V\bbsite last visited on June 3, 2013. Thurston County Geodata Center. http: / /vwwv.geodata.org/. Vq) bsite last visited on June 3, 2013. StreamNet. Fish Data for the Northwest. Administered by the Pacific States Marine Fisheries Commission. http: / /vwwv.streamnet.org/. Website last visited on June 3, 2013. U.S. Amay Corps of Engineers (2010). "Regional Supplement to the Corps of Engineers VVatland Delineation Manual: Western Mountains, Valleys, and Coast Region (Version 2.0)," ERDC/EL TR 10 -3, U.S. Army Engineer Research and Development Center, Vicksburg, MS. U.S. Fish and VVldlife Service (2010). Listed and Proposed Endangered and Threatened Species and Critical Habitat; Candidate Species; and Species of Concern in Thurston County as prepared by the U.S. Fish and VVldlife Service Washington Fish and Wildlife Office. (Revised December 15, 2010). U.S. Fish and Wildlife Service. National VVatlands Inventory VVatlands Mapper. http: // 107.20. 228. 18Mttlands AAbtlandsMapper.html #. Last updated May 22, 2013. VV✓bsite last visited on June 2, 2013. Washington State Department of Fish and Wildlife. Priority Habitats and Species map for Section 19, Township 17 North, Range 02 East. http:/ /wdfw.wa.gov /conservatiorVphs✓. Washington State VVatlands Identification and Delineation Manual. Washington State Department of Ecology. Publication #96 -94. March 1997. Web Soil Survey. United States Department of Agriculture. Natural Resources Conservation Service. http:// websoilsurvey. nres.usda.goy /app/Hon-ePage.htm. VV✓bsite last visited on June 3, 2013. Wetlands & Wfldlife, Inc. Revised Repot Date: May 23, 2014 Veber Property — Critical Areas Repot & Proposed Mitigation Plan City of Yelm, Vshington (Tax Parcel #22719240300) Page 13 Wetland name or number Wet A WETLAND RATING FORM — WESTERN WASHINGTON Version 2 - Updated July 2006 to increase accuracy and reproducibility among users Updated Oct 2008 with the new WDFW defi nitions for priority habitats Name of wetland (if known): Weber Property (Yelm) - Wet land A Date of site visit: 5/ 9/ 13 Rated by Scott Spooner (W &W, Inc.) Trained by Ecology? YesE:]No_E]_ Date of training 10/ 2005 SEC: 19 TWNSHP:17N RNGE: 02E Is S /T /R in Appendix D? Yeses No s❑ Map of wetland unit: Figure CA1 Estimated size 740 SF SUMMARY OF RATING Category based on FUNCTIONS provided by wetland I II III 5 IV Category I = Score > =70 Category II = Score 51 -69 Category III = Score 30 -50 Category IV = Score < 30 Score for Water Quality Functions Score for Hydrologic Functions Score for Habitat Functions TOTAL score for Functions Category based on SPECIAL CHARACTERISTICS of wetland I II Does not Apply _5 Final Category (choose the "highest" category from above) Summary of basic information about the wetland unit 14 16 15 45 Wetland Unit has Special Characteristics Wetland HGM Class used for Rating Estuarine De ressional Natural Heritage Wetland Riverine 5 Bog Lake-fringe Mature Forest Slope Old Growth Forest Flats Coastal Lagoon Freshwater Tidal Interdunal None of the above 5 Check if unit has multiple HGM classes pre sent Wetland Rating Form — western Washington 1 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 Wetland name or number Wet A R Riverine and Freshwater Tidal Fringe Wetlands Points WATER QUALITY FUNCTIONS - Indicators that wetland functions to improve (only t score water quality per box) R R 1. Does the wetland unit have the potential to improve water quality? (see p.52) R R 1.1 Area of surface depressions within the riverine wetland that can trap sediments Figure during a flooding event: ❑ Depressions cover >3/4 area of wetland points = 8 0 Depressions cover > 1/2 area of wetland points = 4 8 If depressions >'/z of area of unit draw polygons on aerial photo or map 0 Depressions present but cover < 1/2 area of wetland points = 2 ❑No depressions present points = 0 R R 1.2 Characteristics of the vegetation in the unit (areas with >90% cover at person height): Figure =Trees or shrubs > 2/3 the area of the unit points = 8 =Trees or shrubs > 1/3 area of the unit points = 6 6 ❑ Ungrazed, herbaceous plants > 2/3 area of unit points = 6 ❑ Ungrazed herbaceous plants > 1/3 area of unit points = 3 ❑ Trees, shrubs, and ungrazed herbaceous < 1/3 area of unit points = 0 Aerial photo or map showing polygons of different vegetation types R Add the points in the boxes above 14 R R 2. Does the wetland unit have the opportunity to improve water quality? (see p.53) Answer YES if you know or believe there are pollutants in groundwater or surface water coming into the wetland that would otherwise reduce water quality in streams, lakes or groundwater downgradient from the wetland? Note which of the following conditions provide the sources of pollutants. A unit may have pollutants coming from several sources, but any single source would qualify as opportunity. ❑ Grazing in the wetland or within 150ft ❑ Untreated stormwater discharges to wetland ❑ Tilled fields or orchards within 150 feet of wetland ❑ A stream or culvert discharges into wetland that drains developed areas, residential areas, farmed fields, roads, or clear -cut logging ❑ Residential, urban areas, golf courses are within 150 ft of wetland ❑ The river or stream linked to the wetland has a contributing basin where human activities have raised levels of sediment, toxic compounds or nutrients in the river water above standards for water quality multiplier ❑ Other ❑YES multiplier is 2 ONO multiplier is 1 1 R TOTAL - Water Quality Functions Multiply the score from R 1 by R 2 14 Add score to table on p. 1 Comments Wetland Rating Form — western Washington 7 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 Wetland name or number Wet A R Riverine and Freshwater Tidal Fringe Wetlands Points HYDROLOGIC FUNCTIONS - Indicators that wetland functions to reduce (only 1 score flooding and stream erosion per box) R 3. Does the wetland unit have the potential to reduce flooding and erosion? (see p.54) R R 3.1 Characteristics of the overbank storage the unit provides: Figure Estimate the average width of the wetland unit perpendicular to the direction of the flow and the width of the stream or river channel (distance between banks). Calculate the ratio: ( average width of unit)1( average width of stream between banks). ❑ If the ratio is more than 20 points = 9 1 ❑ If the ratio is between 10 — 20 points = 6 ❑ If the ratio is 5 - <10 points = 4 ❑If the ratio is 1 - <5 points = 2 s❑ If the ratio is < 1 points = 1 Aerial photo or map showing average widths R R 3.2 Characteristics of vegetation that slow down water velocities during floods: Treat Figure large woody debris as 'forest or shrub". Choose the points appropriate for the best description. (polygons need to have >90% cover at person height NOT Cowardin classes): s❑ Forest or shrub for >1/3 area OR herbaceous plants > 2/3 area points = 7 7 ❑Forest or shrub for > 1 /10 area OR herbaceous plants > 1/3 area points = 4 ❑ Vegetation does not meet above criteria points = 0 Aerial photo or map showing polygons of different vegetation types R Add the points in the boxes above 1 g R R 4. Does the wetland unit have the opportunity to reduce flooding and erosion? (see p.57) Answer YES if the unit is in a location in the watershed where the flood storage, or reduction in water velocity, it provides helps protect downstream property and aquatic resources from flooding or excessive and /or erosive flows. Note which of the following conditions apply. ❑ There are human structures and activities downstream (roads, buildings, bridges, farms) that can be damaged by flooding. ❑ There are natural resources downstream (e.g. salmon redds) that can be damaged by flooding 0 Other multiplier (Answer NO if the major source of water to the wetland is controlled by a reservoir or the wetland is tidal fringe along the sides of a dike) 2 ❑ YES multiplier is 2 ❑NO multiplier is 1 R TOTAL - Hydrologic Functions Multiply the score from R 3 by R 4 Add score to table on p. 1 16 Comments Wetland Rating Form — western Washington 8 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 Wetland name or number Wet A These questions apply to wetlands of all HGM classes. Points (only 1 score HABITAT FUNCTIONS - Indicators that unit functions to provide important habitat perbox) H 1. Does the wetland unit have the potential to provide habitat for many species? H 1.1 Vegetation structure (seep. 72) Figure Check the types of vegetation classes present (as defined by Cowardin)- Size threshold for each class is % acre or more than 10% of the area if unit is smaller than 2.5 acres. =Aquatic bed =Emergent plants ❑ Scrub /shrub (areas where shrubs have >30% cover) =Forested (areas where trees have >30% cover) If the unit has a forested class check if 0 ❑ The forested class has 3 out of 5 strata (canopy, sub - canopy, shrubs, herbaceous, moss /ground- cover) that each cover 20% within the forested polygon Add the number of vegetation structures that qualify. If you have: 0 4 structures or more points = 4 Map of Cowardin vegetation classes 03 structures points = 2 0 2 = 1 structures points 0 1 structure points = 0 H 1.2. Hydroperiods (seep. 73) Figure Check the types of water regimes (hydroperiods) present within the wetland. The water regime has to cover more than 10% of the wetland or % acre to count. (see text for descriptions of hydroperiods) =Permanently flooded or inundated ❑4 or more types present points = 3 ❑ Seasonally flooded or inundated ❑ 3 types present points = 2 ❑ Occasionally flooded or inundated :]2 types present point = 1 1 0 Saturated only ❑ 1 type present points = 0 = Permanently flowing stream or river in, or adjacent to, the wetland Q Seasonally flowing stream in, or adjacent to, the wetland = Lake fringe wetland = 2 points =Freshwater tidal wetland = 2 points Map of hydroperiods H 1.3. Richness of Plant Species (seep. 75) Count the number of plant species in the wetland that cover at least 10 W. (different patches of the same species can be combined to meet the size threshold) You do not have to name the species. Do not include Eurasian Milfoil, reed canarygrass, urple loosestrife, Canadian Thistle If you counted: > 19 species points = 2 List species below if you want to: 5❑ 5 - 19 species points = 1 1 ❑ < 5 species points = 0 Total for page Wetland Rating Form — western Washington 13 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 Wetland name or number Wet A H 1.4. Interspersion of habitats (seep. 76) Figure Decide from the diagrams below whether interspersion between Cowardin vegetation classes (described in H 1.1), or the classes and unvegetated areas (can include open water or mudflats) is high, medium, low, or none. C) O 42 None = 0 points =Low = 1 point DModerate = 2 points 1 [riparian braided channels] ❑ High = 3 points NOTE: If you have four or more classes or three vegetation classes and open water the rating is always "high". Use map of Cowardin vegetation classes H 1.5. Special Habitat Features: (seep. 77) Check the habitat features that are present in the wetland. The number of checks is the number of points you put into the next column. =Large, downed, woody debris within the wetland ( >4in. diameter and 6 ft long). =Standing snags (diameter at the bottom > 4 inches) in the wetland =Undercut banks are present for at least 6.6 ft (2m) and /or overhanging vegetation extends at least 3.3 ft (lm) over a stream (or ditch) in, or contiguous with the unit, for at least 33 ft (1 Om) 1 =Stable steep banks of fine material that might be used by beaver or muskrat for denning ( >30degree slope) OR signs of recent beaver activity are present (cut shrubs or trees that have not yet turned grey /brown) =At least' /4 acre of thin- stemmed persistent vegetation or woody branches are present in areas that are permanently or seasonally inundated. (structures for egg- laying by amphibians) = Invasive plants cover less than 25% of the wetland area in each stratum of plants NOTE: The 20% stated in early printings of the manual on page 78 is an error. H 1. TOTAL Score - potential for providing habitat 4 Add the scores rom H1.1, H1.2, H1.3, H1.4, H1.5 Comments Wetland Rating Form — western Washington 14 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 Wetland name or number Wet A H 2. Does the wetland unit have the opportunity to provide habitat for many species? H 2.1 Buffers (seep. 80) Figure Choose the description that best represents condition of buffer of wetland unit. The highest scoring criterion that applies to the wetland is to be used in the rating. See text for definition of "undisturbed. " ❑ 100 m (330ft) of relatively undisturbed vegetated areas, rocky areas, or open water >95% of circumference. No structures are within the undisturbed part of buffer. (relatively undisturbed also means no- grazing, no landscaping, no daily human use) Points = 5 5❑ 100 m (330 ft) of relatively undisturbed vegetated areas, rocky areas, or open water > 50% circumference. Points = 4 ❑ 50 m (170ft) of relatively undisturbed vegetated areas, rocky areas, or open water >95% circumference. Points = 4 ❑ 100 m (330ft) of relatively undisturbed vegetated areas, rocky areas, or open water > 25% 4 circumference, . Points = 3 ❑ 50 m (170ft) of relatively undisturbed vegetated areas, rocky areas, or open water for > 50% circumference. Points = 3 If buffer does not meet any of the criteria above ❑ No paved areas (except paved trails) or buildings within 25 m (80ft) of wetland > 95% circumference. Light to moderate grazing, or lawns are OK. Points = 2 ❑ No paved areas or buildings within 50m of wetland for >50% circumference. Light to moderate grazing, or lawns are OK. Points = 2 ❑ Heavy grazing in buffer. Points = I ❑ Vegetated buffers are <2m wide (6.6ft) for more than 95% of the circumference (e.g. tilled fields, paving, basalt bedrock extend to edge of wetland Points = 0. ❑ Buffer does not meet any of the criteria above. Points = I Aerial photo showing buffers H 2.2 Corridors and Connections (seep. 81) H 2.2.1 Is the wetland part of a relatively undisturbed and unbroken vegetated corridor (either riparian or upland) that is at least 150 ft wide, has at least 30% cover of shrubs, forest or native undisturbed prairie, that connects to estuaries, other wetlands or undisturbed uplands that are at least 250 acres in size? (dams in riparian corridors, heavily used gravel roads, paved roads, are considered breaks in the corridor). ❑ YES = 4 points (go to H 2.3) 5❑ NO = go to H 2.2.2 H 2.2.2 Is the wetland part of a relatively undisturbed and unbroken vegetated corridor (either riparian or upland) that is at least 50ft wide, has at least 30% cover of shrubs or 1 forest, and connects to estuaries, other wetlands or undisturbed uplands that are at least 25 acres in size? OR a Lake - fringe wetland, if it does not have an undisturbed corridor as in the question above? ❑YES = 2 points (go to H2.3) 5❑NO = H 2.2.3 H 2.2.3 Is the wetland: ❑ within 5 mi (8km) of a brackish or salt water estuary OR 5❑ within 3 mi of a large field or pasture ( >40 acres) OR ❑ within 1 mi of a lake greater than 20 acres? 5 YES =1 point NO = 0 points Total for page Wetland Rating Form — western Washington 15 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 Wetland name or number Wet A H 2.3 Near or adjacent to other priority habitats listed by WDFW (see new and complete descriptions of WDFWpriority habitats, and the counties in which they can be found, in the PHS report http : / /Wdfw.wa. ,-ovlhablphslist.htm ) Which of the following priority habitats are within 330ft (100m) of the wetland unit? NOTE: the connections do not have to be relatively undisturbed. R Aspen Stands: Pure or mixed stands of aspen greater than 0.4 ha (1 acre). Biodiversity Areas and Corridors: Areas of habitat that are relatively important to various species of native fish and wildlife (full descriptions in WDFWPHS report p. 152). =Herbaceous Balds: Variable size patches of grass and forbs on shallow soils over bedrock. =Old- growth/Mature forests: (Old - growth west of Cascade crest) Stands of at least 2 tree species, forming a multi - layered canopy with occasional small openings; with at least 20 trees/ha (8 trees /acre) > 81 cm (32 in) dbh or > 200 years of age. (Mature forests) Stands with average diameters exceeding 53 cm (21 in) dbh; crown cover may be less that 100 %; crown cover may be less that 100 %; decay, decadence, numbers of snags, and quantity of large downed material is generally less than that found in old- growth; 80 - 200 years old west of the Cascade crest. =Oregon white Oak: Woodlands Stands of pure oak or oak/conifer associations where canopy coverage of the oak component is important (full descriptions in WDFW PHS report p. 158). =Riparian: The area adjacent to aquatic systems with flowing water that contains elements of both aquatic and terrestrial ecosystems which mutually influence each other. =Westside Prairies: Herbaceous, non - forested plant communities that can either take the form of a dry prairie or a wet prairie (full descriptions in WDFW PHS report p. 161). =Instream: The combination of physical, biological, and chemical processes and conditions that interact to provide functional life history requirements for instream fish and wildlife resources. = Nearshore: Relatively undisturbed nearshore habitats. These include Coastal Nearshore, Open Coast Nearshore, and Puget Sound Nearshore. (full descriptions of habitats and the definition of relatively undisturbed are in WDFW report: pp. 167 -169 and glossary in Appendix A). =Caves: A naturally occurring cavity, recess, void, or system of interconnected passages under the earth in soils, rock, ice, or other geological formations and is large enough to contain a human. =Cliffs: Greater than 7.6 in (25 ft) high and occurring below 5000 ft. =Talus: Homogenous areas of rock rubble ranging in average size 0.15 - 2.0 in (0.5 - 6.5 ft), composed of basalt, andesite, and/or sedimentary rock, including riprap slides and mine tailings. May be associated with cliffs. =Snags and Logs: Trees are considered snags if they are dead or dying and exhibit sufficient decay characteristics to enable cavity excavation/use by wildlife. Priority snags have a diameter at breast height of > 51 cm (20 in) in western Washington and are > 2 in (6.5 ft) in height. Priority logs are > 30 cm (12 in) in diameter at the largest end, and > 6 in (20 ft) long. 3 =If wetland has 3 or more priority habitats = 4 points F5 If wetland has 2 priority habitats = 3 points DIf wetland has 1 priority habitat =1 point =No habitats = 0 points Note: All vegetated wetlands are by definition a priority habitat but are not included in this list. Nearby wetlands are addressed in question H 2.4) Wetland Rating Form — western Washington 16 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 Wetland name or number Wet A H 2.4 Wetland Landscape (choose the one description of the landscape around the wetland that best fits) (seep. 84) Q There are at least 3 other wetlands within %2 mile, and the connections between them are relatively undisturbed (light grazing between wetlands OK, as is lake shore with some boating, but connections should NOT be bisected by paved roads, fill, fields, or other development. points = 5 0 The wetland is Lake -fringe on a lake with little disturbance and there are 3 other lake -fringe wetlands within %2 mile points = 5 3 50 There are at least 3 other wetlands within %2 mile, BUT the connections between them are disturbed points = 3 0 The wetland is Lake - fringe on a lake with disturbance and there are 3 other lake -fringe wetland within %2 mile points = 3 0 There is at least 1 wetland within %2 mile. points = 2 0 There are no wetlands within %2 mile. points = 0 H 2. TOTAL Score - opportunity for providing habitat 11 Add the scores rom H2. 1,H2.2, H2.3, H2.4 TOTAL for H 1 from page 14 4 Total Score for Habitat Functions — add the points for H 1, H 2 and record the result on 15 P. 1 Wetland Rating Form — western Washington 17 August 2004 version 2 Updated with new WDFW definitions Oct. 2008 X FUIVBOE!EFUFSN OBU.PO!EBUB!GPSN! =!X ft Lf so!Npvotbjot - !V\brrhzt - !boe!Dpbt LlSf hjpo! CgpIf drOfjrf j Cbsdf n$3382: 351411 !! DjrzGDpvorz;!! 1�4VRq44R!! PjMlPgT!fll!!! III III !!!!!!!!!Tbn goh!EbLf ;! 1601: C24 i BggobodPx of E;! Sboez boe Moeb X f cf s !!TLbLf;!A!P!!!!!!!!!!!!!Tbn q*h!QpjogA!R!!!!!!!!!!! !!! ,bdtyhb�ps)t *;!!T puTpr traAf!itw�!!W!PRRi!!'i!!v��IRfl nr# J( li!!!!!!!!!!!!!!!!!!!!!!!! Tfdypo-! Upxofijq- !Sbohf;!T2:- U28O- S13F -X /N/ i IWoeg)si !)i jn(mrpgf Af ssbdf -!f uj / *;! G rppegrbjo OTu# bn di boof m !!P,)dbrt$f O j)dpodbd -!dpod y -!opof ! Tvcsfhjpo!) N8S*; IIk 5F? Ia5!!! III !!!!!!!!!!!!!!!!!!!!!!!! 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