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HomeMy WebLinkAboutWetland Delineation Report 902264043 I I I I I I I I I I I I I I I I ~ I I I WETLAND DELINEATION AND ANALYSIS REPORT FRENCH PROPERTY WETLAND DELINEATION SECTION 26 TOWNSHIP 29N RANGE 02W DISCOVERY BA Y,W ASHINGTON Prepared for: Michael Jameson & Jean French PO Box 237 Chimacum, WA 98325-0237 May 10,2007 Project Number ACL07W368 Prepared by: ALKAI CONSULTANTS, LLC. 9465 Provost Road NW, Suite 202 Silverdale, Washington 98383 Phone: (360) 613-2407 Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I TABLE OF CONTENTS INTRODUCTION ".,.,.,.,."""""",.""""""""""""".,.,.,.,."".,.".,.",.,.""""""""""""."",""."",.", 1 GENERAL SITE CONDITIONS ...,............ .......... ..,.,.,...... ,....... ........., ........., ......................, ,. ...,.., 1 METHODOLOGY ",.,.,.,.""""""",...",.,."".""""""""",."""",.",.,.,."",.",.,."""".",.""",.,.,."",., 2 Review of Existing Information ....,................ ......,.....' .........,.,....., .....,.,......., ........ ....,.,......... 2 Field Delineation.,.,.""""",.",.,.",."..""""",."""".,."""..,.,."",.,.,.,.",.,.,."""".,.""",.,.,.,.,.,., 2 WETLAND EVALUATION ............, ..., ,................. ,.....,.... .......,.............,.....,.. ..............,...,.........,. 3 BACKGROUND INFORMATION ",."""""""""""""".,.""..",.,.,.",.,.",.,.,.,.,.""".""""",.,.,.,.", 3 Watershed "".""".,.""" ,. ",.",.,., "".,.,."""""", "" ",.,.,.", ".",.,.,.""",.,.,.,.,.,.,.", """., ",.,.,.""" 3 Jefferson County Soil Survey...,...,.. ...'...... ....., ,... ........, ........... ......................,.. .....,.. ..........,.. 3 National Wetlands Inventory "."",.,.,.,.,.,.,.,.,.,.", """",.,."""" "",."""" ",.,.,.,., ".",.,., "",.,.",. 3 Priority Species Listing and National Heritage Features...................................,.................., 4 WETLAND DELINEA nON RESULTS.........,.,.......,.. ..,.,.,.,.....,....... .........,.. .........., ...,...... ,... ...... 4 General Wetland Conditions""""""""""".",.,.",.""".,."""...",.""""""".,."",.,.,.,.,.,.""""" 4 Soils"", ,."""".""",.,.,.,.,.,.,."""""."""""",.",.,.,.,."""",.,.",.,.,.,.,.,."",.".,.""",.,.",.,. ,l:.,.,.", 4 Hydrology",',.," """.,.,.,.,.,.,.", """ """""',""" ,."",."", """.,.,.,.,.,.",.",.""", "",."""",.,.,.,.,.,. 4 Vegetation.",.,."""",.,.",.",.""",.,.""."",.""""",.,...,."",.,.,.,."",.,.,.",.,.""""""."""", .,.,.,.,., 5 WETLAND EV ALUA nON RESULTS ................ ,...............,.,.........,.,....................................,.,. 6 Wetland Categorization ,.,.,."", ".,."""""."""" '.,.",., ".",.,.,.,.,.,.,.,.,.",.,., "."", "",' """,.,.,.,.,.' 6 SUMMARy,."",.,., ,..".,.".,.,.,.,., ,..", ,.., "",.",.,."""",.,.,.,., ",."".,.,.,.,.,.,.,.,.,.,.,.,.""".,.,."",.,.,.,.,.,.,. 6 References Figures Figure 1. Site Vicinity Map Figure 2, Wetland Boundary Map Figure 3, Jefferson County Critical Areas Map Figure 4, Jefferson County Soil Survey Map Figure 5: National Wetland Inventory Map Appendices A Field Methodology B Routine Wetland Determination Data Forms C Washington State Wetland Rating System Form D Soil Survey Text E Photographs ALKAI Consultants, LLC . 9465 Provost Road NW, Suite 202 . Silverdale, Washington 98383 Phone: (360) 613-2407 . Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I ALKAI CONSULTANTS, LLC. Environmental Engineering. Geotechnical Engineering. Wetland Consulting May 10, 2007 ALKAI Project # ACL07W368 Page 1 of6 WETLAND DELINEATION AND ANALYSIS REPORT Michael Jameson & Jean French Chimacum, Washington INTRODUCTION ALKAI Consultants, LCC, (ALKAI) has been authorized by Michael Jameson and Jean French to perform a wetland delineation at the property located on West Uncas Road in Discovery Bay, Jefferson County, Washington (Tax Identification Number 902264043), The delineation was performed on April 19, 2007. The proposed project involves removing the current mobile home residence, decommissioning the existing septic system, and constructing a new single family residence and septic system. Because the best drained soils are close to the wetland edge, a delineation was required to determine the best location for the septic system, For the purposes of Federal, Washington State, and Jefferson County jurisdictional oversight, methodology used for the wetland delineation is consistent with the definition provided in paragraph 25a of the Washington State Wetlands Identification and Delineation Manual (Washington State Department of Ecology [Ecology] 1997). The sections below provide: (1) an introduction to the site; (2) a description of methods used in the field delineation; and (3) technical results, GENERAL SITE CONDITIONS The subject property is located in the southeast quarter of Section 26, Township 29 North, Range 02 West (Figure 1). The parcel is a 3-acre lot, roughly rectangular in shape, located at 1450 West Uncas Road in Discovery Bay, Washington, The parcel is primarily comprised of lawn and pasture plant communities dominated by black cottonwood, grasses and rushes, A wooded upland along West Uncas Road is dominated by big-leaf maple, red alder and Sitka spruce with an understory of osoberry, vine maple, red elderberry and sword fern, Approximately one third of the parcel is forested, The site contains a single family residence, outbuildings and horse pasture, The parcel is located in the Snow Creek valley with gentle east-facing slopes, except near West Uncas Road where approximately 15 percent slopes run north to the pasture, A wetland is located on the parcel, referred to here as Wetland A. The wetland is associated with an unnamed tributary to Snow Creek, and is located at the eastern edge of the property. Figure 2 illustrates the approximate wetland boundaries, ALKAI Consultants. LLC - 9465 Provost Road NW. Suite 202- Silverdale. Washington 98383 Phone: (360) 613-2407 - Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I Jameson/French Wetland Delineation ACL07W368 May 10, 2007 Page 2 of6 METHODOLOGY Review of Existing Information Consistent with procedures detailed in the Washington State Wetlands Identification and Delineation Manual (1997 Manual) (Ecology 1997), ALKAI gathered preliminary information on the project site prior to the field review and delineation. General information sources included: United States Geological Survey (USGS) topographic maps, United States Fish and Wildlife Service (USFWS) National Wetland Inventory (NWI) maps, Soil Survey of Jefferson County Area, Washington (United States Department of Agriculture [USDA] 1977), Washington State Department of Natural Resources (DNR) Resource maps, Jefferson County Critical Areas maps and Jefferson County's Critical Areas regulations - Title 18 of the Jefferson County Code (lCC), Field Delineation Methodology used for wetland delineation was consistent with the technical approaches articulated in the 1997 Manual. This document is the wetland delineation manual that is used in determining wetland areas when applying state and local government regulations under the Shoreline Management Act and the Growth Management Act in Washington State, The extent and location of project related wetlands were determined during fieldwork performed on April 19, 2007. Fieldwork was conducted under sunny skies with an ambient temperature of approximately 53 degrees Fahrenheit. The time of year and recent precipitation history were considered in assessing the type and extent of wetlands and stream typing presumed to exist on and in proximity to the site, Wetlands identified during fieldwork are considered potential wetlands until their presence is confirmed through Jefferson County or U,S, Army Corps of Engineers review, Specific field methodology used in determining the extent and location of wetland areas include: 1, As part of the initial project site reconnaissance, the site was walked to determine the general extent and location of potential wetland areas; 2. Wetland and upland sample plots were established in the identified potential wetland areas and in the adjacent upland area; and 3, Wetland boundaries were delineated with flagging by noting localized topography and vegetation patterns and comparing parameters of hydrology, soil, and vegetation with data collected at the wetland and upland sample plots, Specific field methodologies for plot sampling; hydrology, soil, and vegetation evaluation; and boundary delineation are described in Appendix A. Data collected at each sample plot were entered onto a Routine Wetland Determination Data Form (Ecology 1997), Copies of data forms for each sample plot are provided in Appendix B. ALKAI Consultants, LLC .9465 Provost Road NW, Suite 202. Silverdale, Washington 98383 Phone: (360) 613-2407. Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I JamesonIFrench Wetland Delineation ACL07W368 May 10, 2007 Page 3 of6 WETLAND EVALUATION The subject wetland was characterized using the wetland classes defined by the Cowardin system (Cowardin et al. 1979), The Cowardin system describes wetlands by the plant communities, soils and hydrologic regimes present. The naming convention was developed by the USFWS for the NWI maps, Wetlands were also classified and rated using the categories set forth in JCC 18.15,325, which defines wetland categories according to Washington State Wetland Rating System, Western Washington, 2nd Edition, (Ecology 1993). The rating forms completed for this wetland are provided in Appendix C. BACKGROUND INFORMATION Watershed This parcel is located approximately one-tenth of a mile west of Snow Creek at river mile 1.5. The Jefferson County Sensitive Areas map shows an unnamed Type 3 stream flowing past the northwest comer of the property, which joins Salmon Creek within one mile, A Type 5 stream is shown just to the northeast of the property on the Jefferson County Critical Areas map (Figure 3), During field work, the Type 3 stream was found running in a ditch along the western property boundary. The portion of the Type 5 stream near the French property is a shallow, ponded depression without a channel. Jefferson County Soil Survey The soil survey of Jefferson County indicates two onsite soil types: . AmD Alderwood gravelly loam, 15 to 20 percent slopes . Bh Belfast silt loam, heavy variant The southern portion is mapped as Alderwood gravelly loam. The Alderwood series consists of moderately well drained soils that have a very slowly permeable cemented layer at a depth of 20 to 40 inches, The northern portion of the subject parcel is mapped as Belfast silt loam heavy variant which is listed as a moderately well-drained soil with inclusions of Belfast silt loam, wet variant, which has poor drainage, Belfast silt loam is listed as a partially hydric soilin Jefferson County. A more detailed description ofthese soils is presented in Appendix D. Soil location is illustrated in Figure 4 - Jefferson Soil Survey map. National Wetlands Inventory The wetland delineated by ALKAI on this site is shown on the USFWS NWI map as a 14,9-acre PalustrinelEmergentlSeasonally Flooded (PEMC) wetland (Figure 5), Several other freshwater wetlands are listed on NWI maps within one-half mile of the project area, A O,5-acre pond is shown to the west along West Uncas Road, To the northwest, a 10,7-acre emergent wetland is shown. A O,5-acre emergent wetland is shown to the northeast. To the southeast, a 1,2-acre shrub-scrub wetland and a 2.3-acre emergent wetland are indicated. ALKAl Consultants, LLC . 9465 Provost Road NW, Suite 202 . Silverdale, Washington 98383 Phone: (360) 613-2407 . Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I Jameson/French Wetland Delineation ACL07W368 May 10, 2007 Page 4 of6 Priority Species Listing and National Heritage Features The Washington Department of Fish and Wildlife - Habitats and Species map for Jefferson County indicates that no priority species or national heritage features exist onsite, No other State Candidate Species, Threatened, Priority or Other Priority Habitats are located within one-half mile of the subject parcel. The National Heritage Features Associated with Wetlands data does not list this section of land for rare plant species, WETLAND DELINEATION RESULTS General Wetland Conditions ALKAI delineated the western boundary of a wetland referred to here as Wetland A. The wetland extends off of the subject parcel to the north and east. The proposed septic system location is the far southeastern portion of the property near West Uncas Road, Existing fences define the northern and eastern property boundaries of the parcel. The wetland is comprised of an emergent plant community that has been grazed, Dominant plant species include common rush, skunk-cabbage and creeping buttercup. In total, the wetland covers less than one-quarter of the parcel. A 200-foot transect was located running from the eastern property boundary southwest towards the proposed septic site, Data was collected at five points along this transect approximately 50 feet apart, The data points are referred to as DP 1, DP 2, etc. Completed data forms are included in Appendix B, The adjacent parcel to the north was delineated in February 2007 by Olympic Wetland Resources, Wetland boundaries to the east of the subject property were partially visible from the French property and from aerial photos, but the exact location of the boundary is not known, Soils Indicators of hydric conditions were found in soil pits at data points DP 1 through DP 4, Soil textures ranged from silt loam to silty clay, Texture and color were similar to the description of Belfast Silt Loam in the Soil Survey of Jefferson County Area (USDA 1977), Matrix chroma Munsell readings of two or less with prominent mottles, and the listing of Belfast silt loam as a partially hydric soil were positive indicators in all four pits, however the extent of mottling decreased with distance from the wetland, DP 5 exhibited characteristics similar to the description of Alderwood gravelly loam in the soil survey, Munsell readings were higher, no mottling was observed and soil textures were loam and gravelly loam, No hydric indicators were found at DP 5, In a nearby soil test pit dug by the septic designer Nathan Cleaver, soil texture changed to a mottled clay loam at approximately 48 inches below surface, Hydrology Free water was present in soil pits at DP 1 four inches below the surface at and DP 2 twelve inches below the surface, In addition, the low elevation ofDP 1 and DP 2 and the slow permeability of the soil was such that occasional inundation was likely, Innundation ALKAI Consultants. LLC . 9465 Provost Road NW, Suite 202 . Silverdale, Washington 98383 Phone: (360) 613-2407. Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I Jameson/French Wetland Delineation ACL07W368 May 10, 2007 Page 5 of6 was present slightly downslope of DP 1 at the time of field work, DP 1 had slight sediment deposits from earlier ponding, The strongly hydrophytic vegetation at DP 1 gave a FAC-Neutral test of 3:0, which was another positive indicator of hydrology, Soil survey mapping ofthe soil as partially hydric was the final indicator of hydrology, Positive indicators of wetland hydrology could not be found at data points DP 3 through DP 5. No water was found in pits, except near DP 5 where there was water at 48 inches in a test hole dug by Cleaver, There were slight elevation differences between DP 2 and DP 3, which were probably sufficient to result in better drainage at DP 3. Slope increased significantly between DP 4 and DP 5, Vegetation Heavy grazing on the French property and recent grazing on adjacent property to the north and east made identification of plant species difficult. Nevertheless, 18 species were identified along the transect, nine of these within the wetland, The wetland area surrounding DP 1 had vegetation consisting of black cottonwood, creeping buttercup, common rush, skunk-cabbage, and timothy. Greater than 50 percent of the dominant species were identified as facultative (F AC) or wetter and therefore met the wetland criteria for hydrophytic vegetation (Appendix B). In addition, the vegetation at DP 1 had a F AC-neutral ratio of 3 :0, indicating strongly hydrophytic vegetation, The percent of dominant vegetation that was hydrophytic declined steadily along the transect. At DP 2 it was 67 percent, indicating hydrophytic vegetation. At DP 3 and DP 4 only 40 percent of dominant vegetation was hydrophytic, DP 5 had one facultative species, Sitka spruce, present at the forest edge, The upland vegetation was distinct from the wetland vegetation, The upland area surrounding the test pit DP 5 had vegetation that included big-leaf maple, Sitka spruce, osoberry, vine maple, red elderberry, sword fern and Pacific waterleaf, Less than 50 percent of the dominant species in this area were identified as facultative (F AC) or wetter, and therefore did not meet the criteria for hydrophytic vegetation. dandelion white clover F AC soft rush F ACW ALKAI Consultants. LLC . 9465 Provost Road NW, Suite 202 . Silverdale, Washington 98383 . Phone: (360) 613-2407. Fax: (360) 613-2408 is a list FACU FAC FAC FAC FAC- FACU FACU FACU NI OBL FACW The Acer Alnus rubra Picea sitchensis red alder Sitka black cottonwood vine red Pacific waterleaf Tree Tree Tree Tree Shrub Shrub Shrub Shrub Herb Herb Herb Herb Herb I I I I I I I I I I I I I I I I I I I orchard Jameson/French Wetland Delineation ACL07W368 May 10, 2007 60f6 Grass Grass Grass Fern FACU FAC- FAC- FACU tall fescue western sword fern WETLAND EV ALUA TION RESULTS Wetland Categorization Wetland A was rated using the 1993 Wetland Rating System for Western Washington, The wetland is larger than the subject parcel and the estimated size of the wetland unit is 170 acres, based on verbal communication with Donna Frostholm, Jefferson County Wetland Specialist. Based on findings of significant habitat value, it scored 22 points on the state rating system, making it a Category II wetland. Wetland A has been previously rated on the adjacent Fenter parcel (902264042) by Olympic Wetland Resources in February, 2007. Olympic Wetland Resources rated it as a Category II wetland, All Category II wetlands larger than 2,500 square feet are regulated in Jefferson County, The standard buffer width for a delineated Category II wetland is 100 feet from the wetland boundary, Informal measurements were taken onsite and the approximate distance between the proposed septic location and the delineated wetland edge was 160 feet, plus or minus ten feet. SUMMARY This report documents the presence of a depressional wetland on parcel 902264043 located at 1450 West Uncas Road in Discovery Bay, Jefferson County, Washington, The property is owned by Jean French of Chimacum. Wetland boundaries on the subject parcel were found to be similar to what is shown on Jefferson County Sensitive Areas maps, The wetland is a Category II wetland with an associated buffer of 100 feet. CONFIRMATION Wetland status depicted in this report has not been confirmed by a government official, and therefore has no legal status. Agencies with jurisdictional authority over wetlands at the local, state and federal level need to be consulted for their signed agreement to our findings before there is any guarantee of no change. Our estimation for the accuracy of the unconfirmed wetland boundaries portrayed within this report is ~95%. Respectively Submitted, ALKAI Consultants, LLC, (~ Senior Wetland Specialist ~$/~ Michael Dawson Staff Wetland Specialist ALKAl Consultants, LLC . 9465 Provost Road NW, Suite 202 . Silverdale, Washington 98383 Phone: (360) 613-2407 . Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I REFERENCES Cowardin, L.M" v, Carter, F.C, Golet and E,T, LaRoe, 1979, Classification of Wetlands and Deepwater Habitats of the United States, U,S, Fish and Wildlife Service document FWS/OBS-79/31. 84 pp. Washington, D,C, Hitchcock, L.C, and A. Cronquist, 1973, Flora of the Pacific Northwest. University of Washington Press, 730 pp, Hruby, T" 2004, Washington State Wetland Rating System for Western Washington - Revised. Washington State Department of Ecology Publication #04-06-025, Olympia, Washington, Munsell Soil Color Charts, 2000 rev, GretagMacbeth, New Windsor, New York. Pojar, J, and A. MacKinnon, 1994. Plants of the Pacific Northwest Coast, Lone PinePublishing, 528 pp, Vancouver, British Columbia. Speare-Cooke, S" 1997, A Field Guide to the Common Wetland Plants of Western Washington and Northwestern Oregon. Seattle Audubon Society, 417 pp, Seattle, Washington, US Department of Agriculture (USDA), 1977, Soil Survey of Jefferson County Area, Washington, Soil Conservation Service, September, United States Fish and Wildlife Service (OSFW), 1993, National List of Plant Species that Occur in Wetlands Region 9 - Northwest. Resource Management Group. USFW, 1978, National Wetlands Inventory, http://wetlands.fws.gov/mappertoo1.htm Washington Department ofFish and Wildlife, 2004, Habitat and Species Map for Kitsap County and Vicinity, Habitat Program GIS, March 2, 2004, Washington Natural Heritage Program, 2005, National Heritage Features Associated with Wetlands. Olympia, Washington, November, 8,2005. Washington State Department of Ecology (Ecology), 1999, Methods for Assessing Wetland Functions for Riverine and Depressional Wetlands in the Lowlands of Western Washington. Ecology Publication #99-115, Olympia, Washington, Ecology, 1997, Washington State Wetland Identification and Delineation Manual, Ecology Publication #96-94, various pagination, Olympia, Washington, Ecology, 1993, Washington State Wetlands Rating System, Western Washington Second Edition, 61 pp, Ecology Publication #93-74, Olympia, Washington, ALKAI Consultants, LLC . 9465 Provost Road NW, Suite 202. Silverdale, Washington 98383 Phone: (360) 613-2407 . Fax: (360) 613-2408 I I I I I I I I I I I I I I I I I I I ALKAI CONSULTANTS, LLC. Environmental Engineering · Geotechnical Engineering · Wetland Consulting FIGURE 1 VICINITY MAP Project Name: Jameson/ French Wetland Delineation Location: Discovery Bay, Washington Project: ACL07 -W368 Client: Michael Jameson Date: 5/2007 ------------------- Legal Description: 525&26 T29N R2W Tax 64 Recording # 413100 Lot size: 2.74 acres Project Name: Jameson/ French Wetland Delineation Location: Discovery Bay, Washington Project: ACL07 -W368 Client: Michael Jameson Date: 5/2007 AtKAI CONSULTANTS, LLC. Figure 2: Site Plan Environmental Engineering · Geotechnical Engineering · Wetland Consulting I I I I I I I I I I I I I I I I I I I ~ ~,_ i ~, c' e ~ ~ ~,. .~ Q).", S,', .', ,~. ". lV". ..... ~ Q):t ~I' ~'m ' Vl;l;, 4l, ~ al " ~ l' ,'TJ,' ~ J j!ll III q . !Il i ! 1;. " i 1'" ~ l ~ · 1 t( m q] <l!l N" ~ jJ I t "'~: ~'~ 0 r ~; lllllllll.Q! 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C QI E ...I c 0 <C s.. -s C LLI j .J I I I I I I I I I I I I I I I I I I I Onsite Soil Conditions based on Jefferson County Soil Survey Alderwood gravelly loam, 15 to 30 percent slopes (AmD).-This moderately steep soil is.in areas where the rolling upland glacial terraces converge with the steep drainage way ravines. The surface layer and subsoil are gravelly loam. This soil holds 3 to 6 inches of water available for plants. Permeability is moderate. Runoff is medium to rapid, and the hazard of erosion is moderate to severe. This soil is used mainly for tree production and for wildlife habitat and recreation areas. Capability unit VIe-I; woodland group 3d2. Belfast silt loam, heavy variant (Bh).- This nearly level soil is on flood plains. The upper 26 inches is dominantly dark brown or dark yellowish-brown, slightly acid to neutral silt loam. Below this, to a depth of more than 60 inches, is mostly dark grayish-brown or dark-brown, neutral heavy silt loam and silty clay loam mottled with dark red and dark reddish brown. Included with this soil in mapping are small areas having poor drainage. This soil is moderately well drained. Permeability is moderately slow. This soil holds about 11 to 13 inches of water available for plants. A seasonal water table is at a depth of2 to 4 feet. Most of the acreage of this . soil is used for permanent pasture, hay, or silage and for many berry, fruit, and vegetable crops. Capability unit Ilw-l; woodland group 302. A detailed soil description can be found in Appendix D Jefferson County Soil Survey Text. FIGURE 4 SOIL SURVEY Project Name: Jameson/.French Wetland Delineation Location: Discovery Bay, Washington Project: ACL07-W368 Client: Michael Jameson Date: 5/2007 ALKAI CONSULTANTS, LLC. 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" . ..~ ~ .?;: c o :.;::; CO Q) C Q) o "'0 C CO ~c Q) 0 ~rn ..c: . ~ o..c: 'c en Q) CO U:~ c:>- c ~~~ffi~ :i ~ ~~ E -coQ)>CO ::>-,>~-' > 0 - Z..oOQ) Q)en...Jcol'- E .- U ..c: 0 "'coO<(oO ~Z C ..~~ y. t5 .2 t5 .. ::J Q) +-' Q) C .. ,n .~ CO .~ Q) Q) ~ege~Cii LLCL...JCLUO ~ N ~, Itl, Z' 11' .0 '1.0, ~ 1.0, ., '..... ""*, b.O e -.;:: -S '" e 0 u -a e ftS ':;: QI . ~ U C ...J b.O ...J e 0 -t: -f-I " QI en \.ra QI ]. e :2J+' c r- -;0 ..:C Z e CJ' fri w 'f/) '.~. ro ~ -; 5$ u -2 .c :....J u :::> QI ..., 0 \.ra QI Z \:) ~ ~ 0 b.O e Z -t: 8 Q) U QI ~ QI .~ e 0 rJ:l I ~ .,D - -50 Q) e "'0 ~ c( w Q) $-4 -; ~ ~ Q) ..., ~ ~ e I "'0 ~ QI ro c: E Q) ::E (J) 0 ..I e $-4 ro~ 0 ;::::$ E ~ I. bI} c( -:; .~ .- 0 ~ X-.J e I o_ w '- (J) 0.0 0.,- <3::m a.. I I I I I I I I I I I I I I I I I I I I :!1> ~-a o..-a $m ~z 50 0..- 2.)( o ~> I I I I I I I I I I I I I I I I I I I Plot Sampline: A 200- foot transect was located running from the eastern property boundary southwest towards the proposed septic site. Data was collected at five points along this transect approximately 50 feet apart. The data points are referred to as DP 1, DP 2, DP 3, DP 4, and DP 5. The locations of these sample plots are indicated in Figure 2. These sampling locations were used as sites for the collection of hydrologic, soil, and vegetative data in accordance with the methodologies set forth in the 1997 Manual. Data collected at each sample plot were entered onto a Routine Wetland Determination Data Form (Washington State Department of Ecology 1997). Copies of data forms for each sample plot are appended to this delineation report. Hvdroloe:v Evaluation According to the 1997 Manual, wetland hydrology is present in areas that are inundated and/or saturated to the surface for a consecutive number of days greater than 12.5 percent of the growing season (approximately 2 weeks in Western Washington). Saturation to the surface is assumed when the water table - the level at which standing water is found in an unlined hole - is found within 12 inches of the surface in a non-sandy soil or within 6 inches of the soil surface in sandy soils. A small soil test pit was excavated to a depth of 18 to 20 inches at the center of each sample plot. The extent of soil inundation and saturation as well as the depth to free water in the test pit were recorded on the Routine Wetland Determination Data Forms as an indication of potential wetland hydrology. Other recorded potential field indicators of wetland hydrology, as listed in the 1997 Manual, include oxidized channels (rhizospheres) associated with living roots, water marks on vegetation or fixed objects, drift lines, sediment deposition on vegetation and other objects, water-stained leaves, wetland drainage patterns, and hydric soil characteristics. Soil Evaluation The presence of hydric soils was determined consistent with the 1997 Manual. Fulfillment of the technical criteria for soil can be inferred by using a combination of published soils information and field indicators. A soil profile to a depth of 16 inches was extracted from each sample plot test pit and the depth and character of each distinct soil horizon was recorded. A Munsell soil color chart (Munsell Color, 2000 rev.) was used to characterize the soil. In accordance with the 1997 Manual field protocol, soil color, hue, and chroma was recorded for each soil profile immediately below the "A" horizon or at a depth of 10 inches, whichever is shallower. All information collected on field soil profiles was recorded on the Routine Wetland Determination Data Form for each sample plot. I I I I I I I I I I I I I I I I I I I Vee:etation Evaluation At each sample plot, vegetation was characterized by determining the percent aerial cover of each plant species occurring' within the herb, shrub, and tree stratum. Dominant species in each of the three strata ~tree, sapling/shrub, and herb) were identified and recorded on the Routine Wetland Determination Data Form for each sample plot. The wetland indicator status of the dominant species' within each vegetation stratum was used to determine the presence of hydrophytic wetland vegetation. Each species' indicator status was defined according to Reed (1993). According to the 1997 Manual an area meets the hydrophytic vegetation criteria when, under normal circumstances, more than 50 percent of the dominant species from each stratum are obligate wetland (OBL), facultative wetland (F ACW), and/or facultative (F AC) species. Boundary Delineation After characteristics of hydrology, soil, and vegetation were compared between the confirmed upland and wetland sample plots, a boundary determination was made in the field. The wetland boundary was determined by first noting likely areas of topographic and vegetative distinction between wetlands and uplands, and then using soil borings to determine the boundary between hydric and non-hydric soils. The wetland boundary was marked with flagging spaced at a distance of approximately 20 feet. I I I I I I I I I I I I I I I I I I I ;0 o C .-to -. :J (() ~ (() ~> [-a o-a (() m ~Z 2. C :J - ~)( -. g m o Q) .-to Q) ." o -s 3 V\ I I I I I I I I I I I I I I I I I I I Routine Wetland Determination OAT A FORM 1 (Revised) WA State Wetland Delineation Manual or 1987 Corps Wetland Delineation Manual) Project/Site: French property Date: 2007/04/19 Applicant/owner: Michael Jameson/Donna French County: Jefferson I nvestigator( s): Michael Dawson/Alkai Consultants State: WA SIT /R: 26/29N/2W Do normal circumstances exist on the site? ~Yes DNo Community ID:Wetland A Is the site significantly disturbed (atypical situation)? DYes ~No Transect ID: Is the area a potential problem area? DYes ~No Plot ID: DP 1 Explanation of atypical or problem area: At eastern property boundary. VEGETATION' (For *strata, indicate T = tree; S = shrub; H = herb; V = vine) Dominant Plant Species *Stratum % cover Indicator Dominant Plant Species *Stratum % cover Indicator Populus balsamifera T 5 FAC Ranunculus repens H 90 FACW Juncus effusus H 35 FACW grazed grasses H 30 Lysichiton americanum H 5 OBL Phleum pratense H 5 FAC- HYDROPHYTIC VEGETATION INDICATORS: % of dominants OBL, FACW, & FAC: 4/5 80% Check all indicators that apply and explain below: D Visual observation of plant species growing in D Physiological/reproductive adaptations areas of prolonged inundation/saturation ~ Wetland plant database D Morphological adaptations ~ Personal knowledge of regional plant communities D Technical Literature D Other (explain) Hydrophytic vegetation present? ~Yes DNo Rationale for decision/Remarks: Greater than 50% of dominants hydrophytic. HYDROLOGY Is it the growing season? ~Yes DNo Water Marks: DYes ~No Sediment Deposits: ~Yes DNo on Based on: D Soil temp (record temp) Drift Lines: DYes ~No Drainage Patterns: ~Yes DNo (air temp 530) ~ Other (explain) time of year Depth of inundation: 0 inches Oxidized Root (live roots) Local Soil Survey: ~Yes DNo Channels <12 in.: D Yes ~ No Depth to free water in pit: 4 inches FAC Neutral: ~Yes DNo Water-stained Leaves: DYes ~No Depth to saturated soil: 3 inches 3:0 Check all that apply & explain below: Other (explain): D Stream, lake or gage data ~ Aerial photographs D Other Wetland hydrology present? ~ Yes D No Rationale for decision/remarks: Water in pit, sediment deposits, drainage patterns, soil survey, positive FAC-neutral test. I I I I I I I I I I I I I I I I I I I SOILS Map Unit Name (Series and Phase): Bh Belfast silt loam, Drainage Class: Moderately well drained. Included with this heavy variant soil in mapping are small areas having poor drainage. Taxonomy (subgroup): Typic Udifluvents Field observations confirm mapped type? ~Yes ONo Profile Description Depth Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile (inches) Horizon (Munsell moist) (Munsell moist) size and contrast structure, etc. (match description) 0-5" 10YR 4/1 10YR 4/4 Common, medium, silt distinct 5 - 16" 10YR 4/1 10YR 4/6 Many, coarse, Silty clay prominent Hydric Soil Indicators: (check all that apply) o Histosol ~ Matrix chroma::; 2 with mottles o Histic Epipedon o Mg or Fe Concretions o Sulfidic Odor o High Organic Content in Surface Layer of Sandy Soils ~ Aquic Moisture Regime o Organic Streaking in Sandy Soils o Reducing Conditions ~ Listed on National/Local Hydric Soils List ~ Gleyed or Low-Chroma (=1) matrix o Other (explain in remarks) Hydric soils present? ~Yes ONo Rationale for decision/Remarks: Low chroma w/mottles, listed hydric soil, aquic moisture regime. Wetland Determination Hydrophytic vegetation present? ~Yes ONo Hydric soils present? ~Yes ONo Wetland hydrology present? ~Yes ONo Is the sampling point within a wetland? ~ Yes ONo Rationale/Remarks: Strong indicators for all three parameters. NOTES: Revised 4/97 I I I I I I I I I I I I I I I I I I I Routine Wetland Determination OAT A FORM 1 (Revised) WA State Wetland Delineation Manual or 1987 Corps Wetland Delineation Manual) Project/Site: French property Date: 2007/04/19 Applicant/owner: Michael Jameson/Donna French County: Jefferson I nvestigator( s): Michael Dawson/Alkai Consultants State: WA SIT /R: 26/29N/2W Do normal circumstances exist on the site? ~Yes DNo Community ID:Wetland A Is the site significantly disturbed (atypical situation)? DYes ~No Transect ID: Is the area a potential problem area? DYes ~No Plot ID: DP2 Explanation of atypical or problem area: Near flag A2. VEGETATION (For *strata, indicate T = tree; S = shrub; H = herb; V = vine) Dominant Plant Species *Stratum % cover Indicator Dominant Plant Species *Stratum % cover Indicator Trifolium repens H 80 FAC grazed grasses H 80 Ranunculus repens H 40 FACW Taraxacum officinale H 5 FACU HYDROPHYTIC VEGETATION INDICATORS: % of dominants OBL, FACW, & FAC: 2/3 67% Check all indicators that apply and explain below: o Visual observation of plant species growing in o Physiological/reproductive adaptations areas of prolonged inundation/saturation ~ Wetland plant database o Morphological adaptations ~ Personal knowledge of regional plant communities o Technical Literature o Other (explain) Hydrophytic vegetation present? ~Yes DNo Rationale for decision/Remarks: Greater than 50% of dominants hydrophytic. HYDROLOGY Is it the growing season? ~Yes DNo Water Marks: DYes ~No Sediment Deposits: DYes ~No on Based on: 0 Soil temp (record temp) Drift Lines: DYes ~No Drainage Patterns: ~Yes DNo (air temp 530) ~ Other (explain) time of year Depth of inundation: 0 inches Oxidized Root (live roots) Local Soil Survey: ~Yes DNo Channels <12 in.: 0 Yes ~ No Depth to free water in pit: 12 inches FAC Neutral: DYes ~No Water-stained Leaves: DYes ~No Depth to saturated soil: 12 inches Check all that apply & explain below: Other (explain): o Stream, lake or gage data ~ Aerial photographs o Other Wetland hydrology present? ~ Yes o No Rationale for decision/remarks: Water in pit, drainage patterns, soil survey. I I I I I I I I I I I I I I I I I I I SOILS Map Unit Name (Series and Phase): Bh Belfast silt loam, Drainage Class: Moderately well drained. Included with this heavy variant soil in mapping are small areas having poor drainage. Taxonomy (subgroup): Typic Udifluvents Field observations confirm mapped type? IZI Yes ONo Profile Description Depth Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile (inches) Horizon (Munsell moist) (Munsell moist) size and contrast structure, etc. (match description) 0-4 10YR 4/2 10YR 4/4 common, medium, silt prominent 4-16 10YR 4/2 10YR 4/6 many, coarse, silt prominent Hydric Soil Indicators: (check all that apply) o Histosol IZI Matrix chroma ~ 2 with mottles o Histic Epipedon o Mg or Fe Concretions o Sulfidic Odor o High Organic Content in Surface Layer of Sandy Soils o Aquic Moisture Regime o Organic Streaking in Sandy Soils o Reducing Conditions IZI Listed on National/Local Hydric Soils List o Gleyed or Low-Chroma (=1) matrix o Other (explain in remarks) Hydric soils present? IZI Yes ONo Rationale for decision/Remarks: Low chroma w/ mottles, listed hydric soil. Wetland Determination Hydrophytic vegetation present? IZI Yes ONo Hydric soils present? IZI Yes ONo Wetland hydrology present? IZI Yes ONo Is the samplinQ point within a wetland? IZI Yes ONo Rationale/Remarks: Indicators less strong than in DP 1, but still positive. NOTES: Revised 4/97 I I I I I I I I I I I I I I I I I I I Routine Wetland Determination DATA FORM 1 (Revised) WA State Wetland Delineation Manual or 1987 Corps Wetland Delineation Manual) Project/Site: French property Date: 2007/04/19 Applicant/owner: Michael Jameson/Donna French County: Jefferson I nvestigator( s): Michael Dawson/Alkai Consultants State: WA SIT /R: 26/29N/2W Do normal circumstances exist on the site? [gI Yes DNo Community ID:Wetland A Is the site significantly disturbed (atypical situation)? DYes [gI No Transect ID: Is the area a potential problem area? DYes [gI No Plot ID: DP3 Explanation of atvpical or problem area: Near flaQ A2. VEGETATION (For *strata, indicate T = tree; S = shrub; H = herb; V = vine) Dominant Plant Species *Stratum % cover Indicator Dominant Plant Species *Stratum % cover Indicator Ranunculus repens H 60 FACW Trifolium repens H 40 FAC Schedonorus phoenix H 15 FAC- Dactylis glomerata H 5 FACU other grazed grasses H 70 Taraxacum officinale H 10 FACU HYDROPHYTIC VEGETATION INDICATORS: % of dominants OBL, FACW, & FAC: 2/5 40% Check all indicators that apply and explain below: D Visual observation of plant species growing in D Physiological/reproductive adaptations areas of prolonged inundation/saturation [gI Wetland plant database D Morphological adaptations [gI Personal knowledge of regional plant communities D Technical Literature D Other (explain) Hydrophytic vegetation present? DYes [gI No Rationale for decision/Remarks: Less than 50% of dominants hydrophytic. HYDROLOGY Is it the growing season? [gI Yes DNo Water Marks: DYes [gI No Sediment Deposits: DYes [gI No on Based on: D Soil temp (record temp) Drift Lines: DYes [gI No Drainage Patterns: DYes [gI No (air temp 530) [gI Other (explain) time of year Depth of inundation: 0 inches Oxidized Root (live roots) Local Soil Survey: [gI Yes DNo Chan nels <12 n.: D Yes [gI No Depth to free water in pit: none FAC Neutral: DYes [gI No Water-stained Leaves: DYes [gI No Depth to saturated soil: none Check all that apply & explain below: Other (explain): D Stream, lake or gage data [gI Aerial photographs D Other Wetland hydrology present? DYes [gI No Rationale for decision/remarks: No indicators other than mapped hydric soil. I I I I I I I I I I I I I I I I I I I SOILS Map Unit Name (Series and Phase): Bh Belfast silt loam, Drainage Class: Moderately well drained. Included with this heavy variant soil in mapping are small areas having poor drainage. Taxonomy (subgroup): Typic Udifluvents Field observations confirm mapped type? ~Yes ONo Profile Description Depth Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile (inches) Horizon (Munsell moist) (Munsell moist) size and contrast structure, etc. (match description) 0-4 10YR 3/2 none silt 4-14 10YR 4/2 1 OYR 4/6 common, fine, silt loam prominent 14 - 16 10YR 4/1 10YR 5/8 few, medium, silty clay prominent 10YR 4/6 common, medium, prominent Hydric Soil Indicators: (check all that apply) o Histosol ~ Matrix chroma::; 2 with mottles o Histic Epipedon o Mg or Fe Concretions o Sulfidic Odor o High Organic Content in Surface Layer of Sandy Soils o Aquic Moisture Regime o Organic Streaking in Sandy Soils o Reducing Conditions ~ Listed on National/Local Hydric Soils List o Gleyed or Low-Chroma (=1) matrix o Other (explain in remarks) Hydric soils present? ~Yes ONo Rationale for decision/Remarks: Low chroma w/ mottles, listed hydric soil. Wetland Determination Hydrophytic vegetation present? DYes ~No Hydric soils present? ~Yes ONo Wetland hydrology present? DYes ~No Is the samplinq point within a wetland? 0 Yes ~No Rationale/Remarks: Vegetation not hydrophytic and hydrology not present. NOTES: Revised 4/97 I I I I I I I I I I I I I I I I I I I Routine Wetland Determination DATA FORM 1 (Revised) WA State Wetland Delineation Manual or 1987 Corps Wetland Delineation Manual) ProjecUSite: French property Date: 2007/04/19 ApplicanUowner: Michael Jameson/Donna French County: Jefferson Investigator(s): Michael Dawson/Alkai Consultants State: WA SIT /R: 26/29N/2W Do normal circumstances exist on the site? [8J Ves DNo Community ID:Wetland A Is the site significantly disturbed (atypical situation)? DVes [8J No Transect 10: Is the area a potential problem area? DVes [8J No Plot 10: DP4 Explanation of atypical or problem area: Near forest edQe. VEGETATION (For *strata, indicate T = tree; S = shrub; H = herb; V = vine) Dominant Plant Species *Stratum % cover Indicator Dominant Plant Species *Stratum % cover Indicator Rubus armeniacus S 40 FACU Ranunculus repens H 65 FACW grazed grasses H 30 Trifolium repens H 15 FAC Taraxacum officinale H 5 FACU Polystichum munitum H 5 FACU . HYDROPHYTIC VEGETATION INDICATORS: % of dominants OBL, FACW, & FAC: 2/5 40% Check all indicators that apply and explain below: o Visual observation of plant species growing in o Physiological/reproductive adaptations areas of prolonged inundation/saturation [8J Wetland plant database o Morphological adaptations [8J Personal knowledge of regional plant communities o Technical Literature o Other (explain) Hydrophytic vegetation present? DVes [8J No Rationale for decision/Remarks: Less than 50% of dominants hydrophytic. HYDROLOGY Is it the growing season? [8J Ves DNo Water Marks: DVes [8J No Sediment Deposits: DVes [8J No on Based on: 0 Soil temp (record temp) Drift Lines: DVes [8J No Drainage Patterns: DVes [8J No (air temp 530) [8J Other (explain) time of year Depth of inundation: 0 inches Oxidized Root (live roots) Local Soil Survey: [8J Ves DNo Channels <12 in.: 0 Ves [8J No Depth to free water in pit: none FAC Neutral: DVes [8J No Water-stained Leaves: DVes [8J No Depth to saturated soil: none Check all that apply & explain below: Other (explain): o Stream, lake or gage data [8J Aerial photographs o Other Wetland hydrology present? DYes [8J No Rationale for decision/remarks: No indicators except for mapped hydric soil. I I I I I I I I I I I I I I I I I I I SOILS Map Unit Name (Series and Phase): Bh Belfast silt loam, Drainage Class: Moderately well drained. Included with this heavy variant soil in mapping are small areas having poor drainage. Taxonomy (subgroup): Typic Udifluvents Field observations confirm mapped type? ~Yes ONo Profile Description Depth Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile (inches) Horizon (Munsell moist) (Munsell moist) size and contrast structure, etc. (match description) 0-4 10YR 3/2 10YR 4/6 few, fine, prominent silty clay 4 -12 10YR 3/2 10YR 4/6 common, coarse, silt loam prominent 12 -16 10YR 5/1 10YR 5/6 many, coarse, fine sandy clay prominent 7.5YR 5/8 few, medium, prominent Hydric Soil Indicators,: (check all that apply) o Histosol ~ Matrix chroma ~ 2 with mottles o Histic Epipedon o Mgor Fe Concretions o Sulfidic Odor o High Organic Content in Surface Layer of Sandy Soils o Aquic Moisture Regime o Organic Streaking in Sandy Soils o Reducing Conditions o Listed on National/Local Hydric Soils List o Gleyed or Low-Chroma (=1) matrix o Other (explain in remarks) Hydric soils present? ~Yes ONo Rationale for decision/Remarks: Low chroma w/ mottles. Wetland Determination Hydrophytic vegetation present? DYes ~No Hydric soils present? ~Yes ONo Wetland hydrology present? DYes ~No Is the sampling point within a wetland? 0 Yes ~No Rationale/Remarks: Vegetation not hydrophvtic and hydrology not present. NOTES: Revised 4/97 I I I I I I I I I I I I I I I I I I I Routine Wetland Determination DATA FORM 1 (Revised) WA State Wetland Delineation Manual or 1987 Corps Wetland Delineation Manual) Project/Site: French property Date: 2007/04/19 Applicant/owner: Michael Jameson/Donna French County: Jefferson Investigator(s): Michael Dawson/Alkai Consultants State: WA SIT /R: 26/29N/2W Do normal circumstances exist on the site? ~Ves DNo Community ID:Wetland A Is the site significantly disturbed (atypical situation)? DVes ~No Transect ID: Is the area a potential problem area? DVes ~No Plot ID: DP5 Explanation of atypical or problem area: Near perc hole on slope. VEGETATION (For *strata, indicate T = tree; S = shrub; H = herb; V = vine) Dominant Plant Species *Stratum % cover Indicator Dominant Plant Species *Stratum % cover Indicator Acer macrophyllum T 60 FACU Hydrophyllum tenuipes H 25 NI Pice a sitchensis T 20 FAC Oenanthe cerasiformis S 75 FACU Acer circinatum S 10 FAC- Sambucus racemosa S 5 FACU Polystichum munitum H 25 FACU HYDROPHYTIC VEGETATION INDICATORS: % of dominants OBL, FACW, & FAC: 1/7 14% Check all indicators that apply and explain below: D Visual observation of plant species growing in D Physiological/reproductive adaptations areas of prolonged inundation/saturation ~ Wetland plant database D Morphological adaptations ~ Personal knowledge of regional plant communities D Technical Literature D Other (explain) Hydrophytic vegetation present? DVes ~No Rationale for decision/Remarks: Less than 50% of dominants hydrophytic. HYDROLOGY Is it the growing season? ~Ves DNo Water Marks: DVes ~No Sediment Deposits: DVes ~No on Based on: D Soil temp (record temp) Drift Lines: DVes ~No Drainage Patterns: DVes ~No (air temp 530) ~ Other (explain) time of year Depth of inundation: 0 inches Oxidized Root (live roots) Local Soil Survey: DVes ~No Channels <12 in.: D Ves ~ No Depth to free water in pit: 48 inches in perc FAC Neutral: DVes ~No Water-stained Leaves: hole DVes ~No Depth to saturated soil: 48 inches Check all that apply & explain below: Other (explain): D Stream, lake or gage data ~ Aerial photographs D Other Wetland hydrology present? DYes ~ No Rationale for decision/remarks: No indicators. I I I I I I I I I I I I I I I I I I I SOilS Map Unit Name (Series and Phase): AmD Alderwood Drainage Class: Moderately well drained gravelly loam, 15 to 20 percent slopes Taxonomy (subgroup): Vitrandic Durochrept Field observations confirm mapped type? [gI Yes ONo Profile Description Depth Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile (inches) Horizon (Munsell moist) (Munsell moist) size and contrast structure, etc. (match description) 0-5 10YR 2/2 none loam 5-19 10YR 4/3 none gravelly loam Hydric Soil Indicators: (check all that apply) o Histosol o Matrix chroma::; 2 with mottles o Histic Epipedon o Mg or Fe Concretions o Sulfidic Odor o High Organic Content in Surface Layer of Sandy Soils o Aquic Moisture Regime o Organic Streaking in Sandy Soils o Reducing Conditions o Listed on National/Local Hydric Soils List o Gleyed or Low-Chroma (=1) matrix o Other (explain in remarks) Hydric soils present? DYes [gI No Rationale for decision/Remarks: No indicators. Wetland Determination Hydrophytic vegetation present? DYes [gI No Hydric soils present? DYes [gI No Wetland hydrology present? DYes [gI No Is the samplinQ point within a wetland? 0 Yes [gI No Rationale/Remarks: No indicators present. NOTES: Revised 4/97 I I I I I I I I I I I I I I I I I I I ~ Q) V\ ::T -. =' OQ """'" o =' V'\ ~> ro " ~" ro m ~z 5.0 ;0- ~>C -. cfdn V'\ ~ V\ """'" ro 3 -n o -s 3 I I I I I I I I I I I I I I I I I I I Wetlands Rating Field Data Form Background Information: Name of Rater: MID ttWSoy\ Affiliation: A-{v..a.i COt5t<11",,1s Date:"2-0c.r/~4/1'1 Name of wetland (if known): we-+(ClA.-tc1 A 'Fr~cA frope~ Government Jurisdiction of wetland: ::r-~ ~C/~ Cot..\.'lf.t{ Location: 1/4 Section: S ~ of 1/4 S:_ Section: 2&, Township: Z q kJ Range: 2- IN Sources of Information: (Check all sources that apply) Site visit: /' USGS Topo Map: V NWI map: /' Aerial Photo: j' Soils survey: J Other: /' Describe:::::r ~ ~ C-V\, C01.Vl ~ S ~S;..j, 'we.. AvetLfl 'MtL(J I lAS F--w 5. P n'uv-; -h.z Sfec..;oes M4-f I "D N ~ W a..-kr R~$clA...-c-e$ t"-'l.t<-{' When The Field Data form is complete enter Category here: ]I. Q.1. High Quality Natural Wetland Circle Answers Answer this question if you have adequate information or experience to do so. If not fmd someone with the expertise to answer the questions. Then, if the answer to questions la, Ib and lc are all NO, contact the Natural Heritage program of DNR. la. Human caused disturbances, Is there significant evidence of human-caused changes to topography or hydrology of the wetland as indicated by any of the following conditions? Consider only changes that may have taken place in the last 5 decades. The impacts of changes done earlier have probably been stabilized and the wetland ecosystem will be close to reaching some new equilibrium that may represent a high quality wetland. la.l Upstream watershed> 12% impervious. la2. Wetland is ditched and water flow is not obstructed. la3. Wetland has been graded, filled, logged. la4. Water in wetland is controlled by dikes, weirs, etc. la5. Wetland is grazed. la6. Other indicators of disturbance (list below) Yes: go to Q.2 Yes: go to Q.2 Yes: go to Q.2 Yes: go to Q.2 Yes: go to Q.2 Yes: go to Q:21 No: go to lb. 25 I I I I I I I I I I I I I I I I I I I 2a.3. Is the vegetation a mixture of only herbaceous plants and Sphagnum mosses with no scrub/shrub or forested classes? Is the area of herbaceous plants, Sphagnum, and deep organic soils> 1/2 acre? Is the area of herbaceous plants, Sphagnum, and deep organic soils If4-1/2 acre? Q.2b. Mature forested wetland. 2b.l. Does 50% of the cover of upper forest canopy consist of evergreen trees older than 80 years or deciduous trees older than 50 years? Note: The size of trees is often not a measure of age, and size cannot be used as a surrogate for age (see guidance). 2b.2. Does 50% of the cover of forest canopy consist of evergreen trees older than 50 years, AND is the structural diversity of the forest high as characterized by an additional layer of trees 20'-49' tall, shrubs 6'_ 20', tall, and a herbaceous groundcover? 2b.3. Does < 25% of the areal cover in the herbaceous/groundcover or the shrub layer consist of invasive/exotic plant species from the list on P. 19? Q.2c. Estuarine wetlands. 2c.1. Is the wetland listed as National Wildlife Refuge, National Park, National Estuary Reserve, Natural Area Preserve, State Park, or Educational, Environmental or Scientific Reserves designated under WAC 332-30-151? 2c.2. Is the wetland> 5 acres; ........................................ ................. Note: If an area contains patches of salt tolerant vegetation that are 1) less than 600 feet apart and that are separated by mudflats that go dry on a Mean Low Tide, or 2) separated by tidal channels that are less than 100 feet wide; all the vegetated areas are to be considered together in calculating the wetland area. or is the wetland 1-5 acres; ......................................................... or is the wetland < 1 acre? ... ...... ... ... ... ...... ... ... ...... ...... ... ... ... ... .... YES: Category I YES: Category II NO: Go to Q.3. YES: Category I NO: Go to 2b.2 YES: Go to 2b.3 NO: Go to Q.3 YES: Category I NO: Go to Q.3 YES: Category I NO: Go to 2c.2 YES: Category I YES: Go to 2c.3 YES: Go to 2cA 27 I I I I I I I I I I I I I I I I I I I Q.4. Significant habitat value. Answer all questions and enter data requested. 4a. Total wetland area Estimate area, select from choices in the near-right column, and score in the far column: Enter acreage of wetland here: (70 acres, and source: p, M-o~d\1l( 4b. Wetland classes: Circle the wetland classes below that qualify: Open Water: if the area of open water is > 1/4 acre Aquatic Beds: if the area of aquatic beds> 1/4 acre, /Emergent: if the area of emerg~nt class is> 1/4 acre.) Scrub-Shrub: if the area of scrub-shrub class is> 1/4 acre, /'i-- . . _ Forested: if area of forested class is > 1/4 acre) Add the number of wetland classes, above, that qualify, and then Score according to the columns at right. e.g. If there are 4 classes (aquatic beds, open water, emergent & Scrub-shrub), vou would circle 8 points in the far right column. 4c. Plant species diversity. For each wetland class (at right) that qualifies in 4b above, count the number of different plant species you can find that cover more than 5% of the ground. You do not have to name them. Class Aquatic Score in column at far right: e.g. If a wetland has an aquatic bed class with 3 species, an Emergent emergent class with 4 species and a scrub-shrub class with 2 species you would circle 2, 2, and 1 in the far column. Note: Any plant species with a cover of> 5% qualifies for points within a class, even those Scrub-Scrub that are not of that class. Forested Circle scores that qualify acres points >200 6 ~ 40-200 5) 10-40 4 5-103 1-5 2 0.1-1 I <0.10 #of classes Points 1 ............ 0 (j ............ 3j 3............ 6 4............ 8 5............ 10 # species in class Points 1 0 2 1 3 2 >3 3 1 0 2-3 1 (4-5 2--" >5 3 1 0 2 I 3-4 2 >4 3 1 0 G ~ 3-4 2 .>4 3 I / 29 I I I I I I I I I I I I I I I I I I I 4g. Connection to streams, (Score one answer only.) 4g.1. Does the wetland provide habitat for fish at any time of the year AND YES = 6 does it have a perennial surface water connection to a fish-bearing stream. 4g.2 Does the wetland provide fish habitat seasonally AND does it have YES = 4} a seasonal surface water connection to a fish-bearing stream. 4g.3 Does the wetland function to export organic matter through a surface YES=4 water connection at all times of the year to a perennial stream. 4g.4 Does the wetland function to export organic matter through a surface YES=2 water connection to a stream on a seasonal basis? 4h. Buffers. Score the existing buffers on a scale of 1-5 based on the following four descriptions. If the condition of the buffers do not exactly match the description, score either a point higher or lower depending on whether the buffers are less or more degraded. Forest, scrub, native grassland or open water buffers are present for more than 100'around 95% of the circumference. Score = 5 Forest, scrub, native grassland, or open water buffers wider than 100' for more than 1/2 of the wetland circumference, or a forest, scrub, grasslands, or open water buffers for more than 50' around 95 % of the circumference. Score = 3 Forest, scrub, native grassland, or open water buffers wider than 100' for mote than 1/4 of the wetland circumference, or a forest, scrub, native grassland, or open water buffers wider than 50' for more than 1/2 of the wetland circumference. Score = 2 No roads, buildings or paved areas within 100' of the wetland for more than 95% of the wetland circumference. Score = 2 No roads, buildings or paved areas within 25' of the wetland for more than 95% of the circumference, or No roads buildings or paved areas within 50' of the wetland for more than 1/2 of the wetland circumference. Score = 1 Paved areas, industrial areas or residential construction (with less than 50' between houses) are less than 25 feet from the wetland for more than 95 % of the circumference of the wetland. Score = 0 5'"' 31 I I I I I I I I I I I I I I I I I I I )>- o-a =-a V'\m ~ Z ~o -I- ll) )( x ~o I I Alderwood Series The Alderwood series consists of moderately well drained soils that have a very slowly permeable cemented layer at a depth of20 to 40 inches. Slopes range from 0 to 50 percent. Elevation ranges from 100 to 800 feet. These soils formed in glacial till under a forest of mixed coniferous and broadleaved vegetation. Annual precipitation ranges from 25 to 50 inches. The average annual air temperature is about 49'F. The above 32'F growing season ranges from 160 to 260 days, and the above 280F growing season ranges from 220 to 320 days. These soils are associated mainly with Beausite, Casey, Clallam, Dick, Everett, Hoypus, Indianola, Sinclair, and Whidbey soils. In a representative profile a thin layer of organic litter covers the surface. The top 1 inch of the soil is very dark grayish-brown gravelly fme sandy loam. Below this, to a depth of 12 inches, is dark yellowish-brown gravelly sandy loam. Beneath this layer, and continuing to a depth of 30 inches, is gravelly sandy loam that is brown in the upper part and dark grayish brown and prominently mottled in the lower part. The next layer is a dark grayish-brown cemented layer that formed in very compact glacial till. Rounded pebbles, cobblestones, and stones are on the surface and throughout the profile. Alderwood soils are used mainly for tree production and for wildlife habitat and recreation areas. Less than 30 percent of the acreage is used for growing pasture plants, hay plants, and diversified farm crops, Alderwood gravelly loam, 15 to 30 percent slopes (AmD).- This moderately steep soil is in areas where the rolling upland glacial terraces converge with the steep drainage way ravines. The surface layer and subsoil are gravelly loam. This soil holds 3 to 6 inches of water available for plants. Permeability is moderate. Runoff is medium to rapid, and the hazard of erosion is moderate to severe. This soil is used mainly for tree production and for wildlife habitat and recreation areas, Capability unit Vie-I; woodland group 3d2. I I I I I I I Belfast Series The Belfast series consists of well-drained soils on flood plains. Slopes range from 1 to 2 percent. Elevation ranges from 30 to about 300 feet. These soils formed in alluvium under a forest consisting mostly of Douglas-fir, western red cedar, Sitka spruce, red alder, maple, willow, cottonwood, salmonberry, and Sword fern. Annual precipitation ranges from 30 to 70 inches. The average annual air temperature is about 500F, The above 320F growing season ranges from 160 to 200 days, and the above 28'F growing season ranges from 210 to 250 days. These soils are associated mainly with Lummi and Swantown soils., In a representative profile in a typical cultivated area, the upper 15 inches is silt loam that is very dark grayish brown in the upper part and dark grayish brown in the lower part. Below this are dark grayish-brown stratified layers ranging in texture from fme sandy loam to silt loam. All soil layers are slightly acid except the surface layer, which is medium acid. Belfast soils are used for growing pasture plants, hay, home garden crops, bulbs, rhododendrons, and azaleas and for summer home sites. Belfast silt loam, heavy variant (Bh).- This nearly level soil is on flood plains. The upper 26 inches is dominantly dark brown or dark yellowish-brown, slightly acid to neutral silt loam. Below this, to a depth of more than 60 inches, is mostly dark grayish-brown or dark-brown, neutral heavy silt loam and silty clay loam mottled with dark red and dark reddish brown. Included with this soil in mapping are small areas having poor drainage. This soil is moderately well drained. Permeability is moderately slow. This soil holds about 11 to 13 inches of water available for plants. A seasonal water table is at a depth of 2 to 4 feet. Most of the acreage of this soil is used for permanent pasture, hay, or silage and for many berry, fruit, and vegetable crops. Capability unit IIw-l; woodland group 302. Belfast silt loam, wet variant (Bk).-This nearly level soil is on flood plains. The upper 9 inches of the soil is dominantly very dark brown or very dark grayish-brown, slightly acid or neutral silt loam. Below this, to a depth of20 inches, is dark-gray or dark grayish-brown, slightly acid or neutral silt loam, fme sandy loam, or loam mottled with strong brown and dark yellowish brown. Beneath this, and extending to a depth of more than 40 inches, is dominantly dark-gray or olive-gray, neutral or slightly acid, stratified fme sandy loam, silt loam, and clay loam. Gravel content ranges from 2 to 25 percent, increasing with depth. Included with this soil in mapping are small areas where the surface. layer is fine sandy loam or loam. This soil is poorly drained. Permeability is moderately slow. The soil holds 10 to 12 inches of water available for plants. A seasonal water table is at a depth of 1/2 to 1 foot. Most of the acreage of this soil is in pasture, but small areas are used for growing diversified home garden crops. Capability unit IIw-l; woodland group 4w2. 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