HomeMy WebLinkAbout801091011 Wetland Delineation Report
CENTER ROAD-VODDER
Center Road
Chimacum, WA
Prepared for
Andrew Vodder
191 Airport Road
Port Townsend, WA 98368
(360) 531-1487
September 27, 2021
Prepared by
Ecological Land Services
1157 3rd Avenue, Suite 220A • Longview, WA 98632
(360) 578-1371 • Project Number 3559.01
Vodder-Center Road Ecological Land Services, Inc.
Wetland Delineation Report i September 27, 2021
TABLE OF CONTENTS
INTRODUCTION ................................................................................................................................1
METHODOLOGY...............................................................................................................................1
PROPERTY DESCRIPTION ................................................................................................................1
VEGETATION ...................................................................................................................................2
SOILS ................................................................................................................................................2
HYDROLOGY ....................................................................................................................................3
CRITICAL AREAS INVENTORIES ......................................................................................................3
CONCLUSIONS ..................................................................................................................................3
WETLAND CATEGORIZATION ..................................................................................................... 3
WATER TYPING ........................................................................................................................... 4
CRITICAL AREA REGULATIONS .................................................................................................. 4
SITE DEVELOPMENT PROPOSAL AND BUFFER REDUCTION PROCESS ...................................... 4
LIMITATIONS ...................................................................................................................................4
REFERENCES ....................................................................................................................................5
FIGURES & PHOTOPLATES
Figure 1 Vicinity Map
Figure 2 Existing Conditions
Figure 3 Soil Survey
Figure 4 National Wetlands Inventory
Figure 5 Jefferson County Critical Areas
Figure 6 Wetland Rating Form – 150’Offset
Figure 7 Wetland Rating Form – 1 KM Offset
Figure 8 Wetland Rating Form – 303(d) and TMDL
Photoplates Site Photos
APPENDIX A
Wetland Determination Data Forms
APPENDIX B
Wetland Rating Form
Vodder-Center Road Ecological Land Services, Inc.
Wetland Delineation Report ii September 27, 2021
SIGNATURE PAGE
The information and data in this report were compiled and prepared under the supervision and
direction of the undersigned.
___________________________
Brenda Ruddick
Biologist
Vodder-Center Road Ecological Land Services, Inc.
Wetland Delineation Report 1 September 27, 2021
INTRODUCTION
Ecological Land Services, Inc. (ELS) was contracted by Andrew Vodder to conduct a critical areas
reconnaissance to determine presence of streams and/or wetlands for the property located at 5662
Center Road, Jefferson County Tax Parcel Number 801091011, in Chimacum, Washington. This
property is located in a portion of Section 9, Township 28 North, Range 1 West of the Willamette
Meridian (Figure 1). This report summarizes findings of the wetland according to the Jefferson
County Code (JCC), Chapter 18.22 Article VII Wetlands.
METHODOLOGY
The wetland determination followed the Routine Determination Method in the Western Mountains,
Valleys, and Coast Region according to the U.S. Army Corps of Engineers, Wetland Delineation
Manual (Environmental Laboratory 1987), and the Regional Supplement to the Corps of Engineers
Wetland Delineation Manual: Western Mountains, Valleys and Coast Region (Version 2.0) (U.S.
Army Engineer Research and Development Center 2010).
The Routine Determination Method examines three parameters—vegetation, soils, and
hydrology—to determine if wetlands exist in a given area. Hydrology is critical in determining
what is wetland but is often difficult to assess because hydrologic conditions can change
periodically (hourly, daily, or seasonally). Consequently, it is necessary to determine if
hydrophytic vegetation and hydric soils are present, which would indicate that water is present for
long enough duration to support a wetland plant community. By definition, wetlands are those
areas that are inundated or saturated by surface or ground water at a frequency and duration
sufficient to support, and that under normal circumstances do support, a prevalence of vegetation
typically adapted for life in saturated soil conditions. Wetlands are regulated as “Waters of the
United States” by the U.S. Army Corps of Engineers (USACE), as “Waters of the State” by the
Washington Department of Ecology (DOE), and locally by Jefferson County.
To delineate the wetland boundaries on the property, ELS biologists collected data on vegetation,
hydrology, and soils. The delineation site visit was conducted on July 8, 2021 during which one
wetland was identified and delineated. The wetland boundary was delineated using consecutively
numbered fluorescent flags labeled “WETLAND DELINEATION.” The wetland boundary was
determined through breaks in topography, changes in vegetation, and evidence of wetland
hydrology. Vegetation, hydrology, and soil data was collected at two test plots to verify the
wetland boundary (Appendix A). The wetland boundary was mapped using a handheld Global
Positioning System (GPS) unit to show the boundary on the site map (Figure 2).
PROPERTY DESCRIPTION
This 20.29-acre rectangular shaped property is located on the west side of Center Road north of
Highway 104 (Figure 1). The property is undeveloped (Figure 2). The western three quarters of
the property is composed of an open field with a fish bearing stream separating it from the forested
eastern portion of the property. The eastern quarter slopes quickly down to the west toward the
wetland and stream. The portion of the property west of the stream slopes gently down to the east
creating the depression in which the wetland resides. The property is currently adjacent to similarly
sized properties (some of which contain single family homes) and undeveloped Pope and Talbot
logging properties.
Vodder-Center Road Ecological Land Services, Inc.
Wetland Delineation Report 2 September 27, 2021
VEGETATION
The onsite portion of the wetland is composed of an emergent and forested community. The
emergent community was dominated by reed canary grass (Phalaris arundinacea, FACW). The
forested community was dominated by red alder (Alnus rubra, FAC), salmonberry (Rubus
spectabilis, FAC), and vine maple (Acer circinatum, FAC). The herbaceous layer was dominated
by false lily of the valley (Maianthemum dilatatum, FAC) with an occurrence of skunk cabbage
(Lysichiton americanus, OBL) and water parsley (Oenanthe sarmentosa, OBL). The hydrophytic
vegetation criterion is met at Test Plot 2 because of the dominance by FAC plant species.
The upland forested area was dominated by Douglas fir (Pseudotsuga menziesii, FACU) and
western red cedar (Thuja plicata, FAC), and red alder in the tree canopy (Photoplate 1). Low
shrub cover was present and included salmonberry, Indian plum (Oemleria cerasiformis, FACU),
and Oregon grape (Mahoina nervosa, FACU). The herbaceous layer was composed of youth on
age (Tolmiea menziesii, FAC), stinging nettle (Urtica dioica, FAC), and sword fern (Polystichum
munitum, FACU). In addition, there is a small area between the forested upland and the wetland
dominated by a dense cover of salmonberry (Photoplate 1). The hydrophytic vegetation criterion
is met at Test Plot 1 because of the dominance by FAC plant species.
The dominant vegetation found onsite is recorded on the attached wetland determination data
forms (Appendix A). The indicator status, following the common and scientific names, indicates
how likely a species is to be found in wetlands. Listed from most likely to least likely to be found
in wetlands, the indicator status categories are:
▪ OBL (obligate wetland) – Almost always occur in wetlands.
▪ FACW (facultative wetland) – Usually occur in wetlands but may occur in non-wetlands.
▪ FAC (facultative) – Occur in wetlands and non-wetlands.
▪ FACU (facultative upland) – Usually occur in non-wetlands but may occur in wetlands.
▪ UPL (obligate upland) – Almost never occur in wetlands.
▪ NI (no indicator) – Status not yet determined.
SOILS
As referenced on the Natural Resources Conservation Service website (NRCS 2020), Alderwood
gravelly sandy loam, 15 to 30 percent slopes is mapped across the eastern third of this property
with Semiahmoo muck (Se), Semiahmoo muck, moderately shallow variant (Sh), and Belfast silt
loam, heavy variant (Bh) mapped throughout the western two-thirds of the property (Figure 3).
Alderwood soils are moderately well-drained soils existing on glacially modified hills and ridges.
These soils formed in glacial drift and outwash over dense glaciomarine deposits. Semiahmoo
soils consist of very poorly drained organic soils that formed in well decomposed and disintegrated
plant remains in glacial basins or old displaced stream and river channel ponded areas. A typical
profile consists of a 10 to 15-inch-thick black muck surface layer and in most places two to four
layers of muck and mucky peat are above the mineral soil material. Underlying mineral soils
typically consist of loamy sand, sandy loam, sandy clay loam, sandy clay, and clay. Belfast soils
are deep, moderately well-drained soils that formed in stratified alluvium. They typically exist on
nearly level flood plains. Semiahmoo soils are classified as hydric because they are poorly drained
Vodder-Center Road Ecological Land Services, Inc.
Wetland Delineation Report 3 September 27, 2021
and composed of organic material. Alderwood and Belfast soils are not classified as hydric
because they are moderately well-drained1 (NRCS 2016).
The soil profile within Test Plot 1 revealed a single layer of loam to 20 inches deep. The soil had a
dark brown (10YR 2/1) matrix color. The soil profile within Test Plot 2 was a black (Gley 1 2.5/N)
muck to 19 inches below the surface. This soil profile met the hydric soil indicator Histosol (A1)
because of the presence of organic material. The soil profile within Test Plot 1 did not meet any
hydric soil indicators because there was no organic material, a depleted matrix, or redoximorphic
features.
HYDROLOGY
The soil within the wetland was saturated to the surface (A3) and there was a high water table to 9
inches below the surface (A2) at the time of the site visit. A fish bearing stream flows south to
north through the center of the property and provides hydrology to the portion of the wetland
surrounding the stream. However, the majority of the wetland is within a depression where the
main source of hydrology appears to be surface water runoff, groundwater, and direct
precipitation. The wetland could possibly contribute to the hydrology of the stream. There was
flowing water within the stream at the time of the site visit. The wetland hydrology criterion is
met within the test plot location. There was no hydrology or evidence of wetland hydrology within
the upland areas.
CRITICAL AREAS INVENTORIES2
The U.S. Fish and Wildlife Service (USFWS) National Wetlands Inventory (NWI 2020) maps a
large forested, emergent, and scrub-shrub wetland system on the western two-thirds of the
property. It extends offsite to the north, west, and south. The stream is also mapped through the
east end of the wetland (Figure 4). The mapping of the wetland was consistent with the findings of
the ELS site visit.
The Jefferson County Tax Parcel Viewer maps the wetland system and the Type F stream in the
location mapped by the NWI (Figure 5). During the site visit, ELS biologists confirmed the
presence of the onsite portion of the large wetland system and the stream as mapped based on data
collected throughout the property.
CONCLUSIONS
WETLAND CATEGORIZATION
The identified wetland is a Category II. It was categorized according to functions using the
Washington State Wetlands Rating System for Western Washington, 2014 Update (Rating System)
(Hruby 2014) (Appendix B). The hydrogeomorphic classification for the wetland is depressional,
vegetation is forested and emergent communities, and the hydroperiods are saturated only and
seasonally flooded with a permanently flowing stream. The overall wetland rating score was 20.
1 Areas mapped as hydric soils do not necessarily mean that an area is or is not a wetland—hydrology, hydrophytic vegetation, and
hydric soils must all be present to classify an area as a wetland.
2 Critical area inventory maps are to be used with discretion because they are intended to gather general wetland information about
a regional area and therefore are limited in accuracy for smaller areas due to their large scale.
Vodder-Center Road Ecological Land Services, Inc.
Wetland Delineation Report 4 September 27, 2021
The water quality function score is 8, the hydrologic function score is 5, and the habitat score is 7.
The fish habitat stream within the wetland flows from the south to the north through the center of
the property.
WATER TYPING
The JCC specifies the use of the Washington Department of Natural Resources (WDNR) water
typing system (WDNR 2006) presented in Section 18.22.630 to determine the water type of
streams. The Jefferson County public land records map classified the onsite site stream as a Type
F water, which was confirmed during the field visit. It is a Type F water because the average
bankfull width is greater than 2 feet and the gradient is less than 16 percent.
CRITICAL AREA REGULATIONS
The JCC Chapter 18.22.730 specifies wetland buffers based on wetland category, proposed land
use intensity, and scores for habitat on the rating form. Because the wetland is a Category II
system, the habitat score is moderate, and the proposed project is of moderate intensity land use, a
buffer width of 110 feet is required from the edge of the wetland.
The JCC Chapter 18.22.630 specifies buffers based on Department of Natural Resources (DNR)
Water Typing System. The onsite stream is classified as a Type F (fish habitat) stream. Type F
streams require 150 feet of buffer with an additional building and impervious surface setback of 15
feet. The stream buffer supersedes the wetland buffer, providing greater habitat protection to the
critical areas. Therefore, the greater stream buffer will be used.
SITE DEVELOPMENT PROPOSAL AND BUFFER REDUCTION PROCESS
The JCC allows buffer reductions for projects that cannot be constructed outside the required
wetland and/or stream buffer widths. Buffer reduction options include buffer averaging, which
takes the amount of displaced buffer and increases the buffer in another location along the buffer.
This creates an average buffer width that matches the regulated buffer width. A second option is a
25-percent reduction, which requires improvement of the buffer through enhancement of
vegetation to provide equal or improved buffer function. No buffer reduction or averaging is
proposed at this time.
LIMITATIONS
ELS bases this report’s determinations on standard scientific methodology and best professional
judgment. In our opinion, local, state, and federal regulatory agencies should agree with our
determinations. However, the information contained in this report should be considered
preliminary and used at your own risk until it has been approved in writing by the appropriate
regulatory agencies. ELS is not responsible for the impacts of any changes in environmental
standards, practices, or regulations after the date of this report.
Vodder-Center Road Ecological Land Services, Inc.
Wetland Delineation Report 5 September 27, 2021
REFERENCES
Environmental Laboratory. 1987. Corps of Engineers Wetlands Delineation Manual, Technical
Report Y-87-1. U.S. Army Corps of Engineer Waterways Experiment Station, Vicksburg,
Mississippi.
Hruby, T (Hruby). August 2014. Washington State Wetland Rating System for Western
Washington-2014 Update. Washington State Department of Ecology Publication #14-06-029.
Olympia, Washington. Effective January 1, 2015.
Jefferson County Code (JCC). 2018. Chapter 18.22. Article VII. Wetlands.
Jefferson County Legacy Mapping Tools (jMAP). Environmentally Sensitive Areas.
http://maps.co.jefferson.wa.us/Website/mspub/viewer.htm?mapset=esa. Website accessed July
2021.
U.S. Army Corps of Engineers (USACE). 2010. Regional Supplement to the Corps of Engineers
Wetland Delineation Manual: Western Mountains, Valleys, and Coast Region (Version 2.0),
ed. J.S. Wakeley, R.W. Lichvar, and C.V. Noble. ERDC/EL TR-08-13. Vicksburg, MS: U.S.
Army Engineer Research and Development Center.
U.S. Fish & Wildlife Service (USFWS). 2020. National Wetlands Inventory (NWI). Online
document <http:www.wetlandsfws.er.usgs.gov/NWI/index.html>. Website accessed July 2021.
Natural Resource Conservation Service (NRCS). 2016. Washington Hydric Soils List.
<http://www.nrcs.usda.gov/wps/portal/nrcs/main/soils/use/hydric/>.
Natural Resource Conservation Service (NRCS). 2020. WA631 Jefferson County Area. Online
document < https://websoilsurvey.sc.egov.usda.gov/App/WebSoilSurvey.aspx>. Website
accessed July 2021
Washington Department of Fish and Wildlife (WDFW). 2021a. Priority Habitats and Species -
PHS on the Web. http://apps.wdfw.wa.gov/phsontheweb/. Website accessed July 2021.
Washington Department of Fish and Wildlife (WDFW). 2021b. SalmonScape.
http://apps.wdfw.wa.gov/salmonscape/map.html. Website Accessed July 2021.
FIGURES & PHOTOPLATES
47.9358° Latitude
-122.8046° Longitude
SITE
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:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 1VICINITY MAP9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET0200040001157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.comLOCATION MAP
WASHINGTON
SITE
NOTE:
Quadrangle topographic map from USGS.
PROJECT
VICINITY MAP
SCALE IN MILES
520
Mt. St.
Helens
SKAMANIA
N. Bonneville
Stevenson
Carson
14
WashougalCamas
Vancouver
Battle
Ground
Woodland
Ridgefield
CLARK
5
500
503
205
Kalama
Longview
ToutleCastle
Rock
COWLITZ
504
4Cathlamet
WAHKIAKUM
6
101
401
103
105
PACIFIC
Ilwaco
Long Beach
Ocean Park
South
Bend
Raymond
101Westport
Ocean Shores
Copalis Beach
Pacific Beach
Taholah
Quinalt
Aberdeen
MontesanoElma
Oakville
12
8
105
109
101
GRAYS
HARBOR
Queets
101
Kalaloch
Port
Townsend
Port Ludlow
Quilcene
Brinnon
101
19
104
20
JEFFERSON
CLALLAMForks110
101
113 112
101
112
Port
Angeles
Sequim
Neah Bay
Clallam Bay
Friday Harbor
Blaine
Ferndale
Bellingham
542
542
9
Lynden5
539
SAN
JUAN
WHATCOM
ConcreteAnacortes
Mount Vernon
Sedro-Woolley
5
20
11
530
SKAGIT
Lynnwood
MulkiteoEverett
Marysville
Monroe
Arlington
Darrington
5
9
2522
SNOHOMISH
Mt St Helens
KING
Seattle
Shoreline
90
Carnation
North Bend
Redmond
Enumclaw
Auburn
Issaquah
Burien
Kent
Renton
405
18
169
410
169
202
Mt. Rainier
Eatonville
4
Puyallup
Tacoma
Gig Harbor
165
162
164
161
7
702
507
Roy
DuPont Carbonado
5
5 Olympia
Shelton
Yelm
Tenino
508
Centralia
Chehalis
Pe Ell Morton 12
Toledo
7
505
Winlock
PIERCE
LEWIS
THURSTON
5
5
KITSAP
Poulsbo
3
16
Bremerton
SITE
TP-1TP-2Center RoadWetland ACategory IIDepressionalForestedEmergentStreamType F(150' Buffer)110'9/27/2021 12:24 PM c:\Users\right\Box\ELS\WA\jefferson\County\3559-vodder\3559.01-center road property\3559.01-figures cad only\3559.01_DL.dwg right N6:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:1157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.comDATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 2EXISTING CONDITIONS9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET0300600NOTE(S):1.Aerial from Google Earth™2.Wetland and test plots located using handheld GPS with submeter accuracy.LEGEND:Site BoundaryWetland BoundaryApprox. Wetland BoundaryWetland BufferStream w/ Flow DirectionTest Plot LocationTP-1
NOTE(S):
1.Map provided on-line by NRCS at web address:
http://websoilsurvey.nrcs.usda.gov/app/9/27/2021 12:24 PM c:\Users\right\Box\ELS\WA\jefferson\County\3559-vodder\3559.01-center road property\3559.01-figures cad only\3559.01_DL.dwg right SITE
N
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:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 3NRCS SOIL SURVEY9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET050010001157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.comLEGEND:
Site Boundary
AlD Alderwood gravelly sandy loam, 15 to 30 percent slopes. Not hydric.
Bh Belfast silt loam, heavy variant. Not hydric.
Se Semiahmoo muck. Hydric.
Sh Semiahmoo muck, moderately shallow variant. Hydric.
PUBHx
NOTE(S):
1.Map provided on-line by US Fish & Wildlife Service at web address: http://www.fws.gov/wetlands/data/index.html9/27/2021 12:24 PM c:\Users\right\Box\ELS\WA\jefferson\County\3559-vodder\3559.01-center road property\3559.01-figures cad only\3559.01_DL.dwg right N
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:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 4USFWS NATIONAL WETLANDS INVENTORY9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET050010001157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.comPEM1C Palustrine, emergent, persistent, seasonally flooded.
PEM1Cd Palustrine, emergent, persistent, seasonally flooded, partially drained/ditched.
PSSCd Palustrine, scrub-shrub, seasonally flooded, partially drained/ditched.
PUBHx Palustrine, unconsolidated bottom, permanently flooded, excavated.
Freshwater Emergent Wetland
Freshwater Forested/Shrub Wetland
Freshwater Pond
Riverine
LEGEND:
Site Boundary
Wetlands
SITEPEM1Cd
PEM1Cd
PSSCdPEM1C
PUBHx
NOTE(S):
1.Map provided on-line by Jefferson
County at web address:
https://jeffcowa.maps.arcgis.com/home/index.html
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:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 5JEFFERSON COUNTY CRITICAL AREAS9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET060012001157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.com
9/27/2021 12:24 PM c:\Users\right\Box\ELS\WA\jefferson\County\3559-vodder\3559.01-center road property\3559.01-figures cad only\3559.01_DL.dwg right SITE
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:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 6WETLAND RATING FORM-150' OFFSET9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET0100020001157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.comCowardin Classes:
EM Emergent
FO Forested
Hydroperiods:
SF Seasonally flooded
SO Saturated only
Rating
Question
Description Answer - Wetland A
D 1.1, D 4.1 Location of Outlet Wetland has an unconstructed surface outlet that is permanently flowing
D 1.3 Distribution of persistent plants Wetland has persistent plants >1/2 the area
D. 1.4 Area of seasonally flooded Area seasonally ponded >1/2 of area
D 2.2 Boundary of area w/in 150’ of
the wetland in land uses that
generate pollutants
<10% of the area within 150’ in land uses that generate pollutants
D 5.2 Boundary of area w/in 150’ of
the wetland in land uses that
generate excess runoff
<10% of the area within 150’ in land use that generate excess runoff
D 4.3 Contributing
Basin-Contribution of wetland
to storage in the watershed
Area of the basin is 10 to 100 times the area of the wetland
D 5.3 Contributing Basin covered in
intensive land uses
<25% of the area of the basin covered with intensive land uses
H 1.1 Cowardin Plant Classes Emergent
H 1.2 Hydroperiods Seasonally ponded
H 1.4 Interspersion of habitats No interspersion of habitats
LEGEND:
Site Boundary
Wetland Unit Boundary
Vegetation Class Division
Hydroperiod Division
150' Wetland Offset
Impervious Surfaces - 6.6%
SF
EM
FO
FO
EM
FO
SF
SF
SO
SO
SO
SO
Wetland A
Category II
Depressional
Forested
Emergent
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:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 7WETLAND RATING FORM-1 KM OFFSET9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET0200040001157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.comH 2.1. Accessible Habitat Equation
% A-U habitat 01.0% + [(% A-M/L intensity land uses)/2] 02.4%= 03.4%
H 2.2. Total Undisturbed Habitat Equation
% A-U + % U habitat 01.5% + [(% A-M/L + % M/L land uses)/2] 19.9%= 21.4%
H2.1 Accessible Habitat
A-U (01.0%)
A-M/L (04.7%)A-M/L
A-U
H2.2 Undisturbed Habitat
U (00.5%)
M/L (35.1%)
H2.3 Land Use Intensity
H (58.8%)
M/L
U
H
LEGEND:
Site Boundary
Wetland Unit Boundary
Contributing Basin
19.8x area of Wetland A
SITE
A-UA-M/L
U
H H
H
M/L
M/L
M/L M/L
M/L
A-M/L
A-M/L
A-M/L
Wetland A
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:(DATE:DWN:REQ. BY:PRJ. MGR:CHK:PROJECT NO:Figure 8WETLAND RATING FORM-303(d) and TMDLs9/27/213559.01Vodder-Center RdAndrew VodderSection 9, Township 28N, Range 1W, W.M. Jefferson County, WashingtonJLLBRSCALE IN FEET0200040001157 3rd Ave., Suite 220ALongview, WA 98632Phone: (360) 578-1371Fax: (360) 414-9305www.eco-land.comSITE
WQ Improvement Projects
Approved
In Development
NOTE(S):
1.Map provided on-line by Washington State
Department of Ecology at web address:
https://fortress.wa.gov/ecy/waterqualityatlas/map.aspx?
Assessed Waters/Sediment
Water
Category 5 - 303d
Category 4C
Category 4B
Category 4A
Category 2
Category 1
Sediment
Category 5 - 303d
Category 4C
Category 4B
Category 4A
Category 2
Category 1
Subbasins
12 Digit HUC Boundary
SITE
1157 3rd Ave., Suite 220A
Longview, WA 98632
(360) 578-1371
Fax: (360) 414-9305
DATE: 8/30/21
DWN: BR
PRJ. MGR: BR
PROJ.#: 3559.01
Photoplate 1
Project Name: Center Road
Client: Andrew Vodder
Chimacum, Washington
Photo 1 was taken of Test Plot 2.
It is taken within the southern
half of the onsite wetland.
Photo 2 was taken just east of the
wetland boundary. This
demonstrates the dense cover of
salmonberry along the edge of the
wetland in the northern half of the
property.
Photo 3 was taken east of the
wetland. It demonstrates the
upland forested community.
APPENDIX A
US Army Corps of Engineers Western Mountains, Valleys, and Coast – Version 2.0
WETLAND DETERMINATION DATA FORM – Western Mountains, Valleys, and Coast Region
VEGETATION – Use scientific names of plants
Tree Stratum (Plot size: 30' diameter) Absolute % Cover Dominant Species? Indicator Status Dominance Test Worksheet:
1. Pseudotsuga menziesii 20 yes FACU Number of Dominant Species
That Are OBL, FACW, or FAC: 3 (A) 2. Thuja plicata 15 yes FAC
3. Alnus rubra 5 no FAC Total Number of Dominant
Species Across All Strata: 5 (B) 4.
50% = 20, 20% = 8 40 = Total Cover Percent of Dominant Species
That Are OBL, FACW, or FAC: 60 (A/B) Sapling/Shrub Stratum (Plot size: 20' diameter)
1. Mahonia nervosa 30 yes FACU Prevalence Index worksheet:
2. Rubus spectabilis 15 yes FAC Total % Cover of: Multiply by:
3. OBL species x1 =
4. FACW species x2 =
5. FAC species x3 =
50% = 22.5, 20% = 9 45 = Total Cover FACU species x4 =
Herb Stratum (Plot size: 10' diameter) UPL species x5 =
1. Tolmiea menziesii 85 yes FAC Column Totals: (A) (B)
2. Polystichum munitum 15 no FACU Prevalence Index = B/A =
3. Urtica dioica 2 no FAC Hydrophytic Vegetation Indicators:
4. 1 – Rapid Test for Hydrophytic Vegetation
5. 2 - Dominance Test is >50%
6. 3 - Prevalence Index is <3.01
7. 4 - Morphological Adaptations1 (Provide supporting
data in Remarks or on a separate sheet) 8.
9. 5 - Wetland Non-Vascular Plants1
10. Problematic Hydrophytic Vegetation1 (Explain)
11. 1Indicators of hydric soil and wetland hydrology must
be present, unless disturbed or problematic. 50% = 51, 20% = 20.4 102 = Total Cover
Woody Vine Stratum (Plot size: )
1.
Hydrophytic
Vegetation
Present?
Yes No 2.
50% = , 20% = = Total Cover
% Bare Ground in Herb Stratum 0
Remarks: The hydrophytic vegetation criterion is met because there is greater than 50% dominance by FAC species.
Project Site: Center Road City/County: Chimacum/Jefferson Sampling Date: 7/8/21
Applicant/Owner: Andrew Vodder State: WA Sampling Point: TP 1
Investigator(s): Brenda Ruddick Section, Township, Range: S09, T28, R1W WM
Landform (hillslope, terrace, etc.): hillslope Local relief (concave, convex, none): concave Slope (%): none
Subregion (LRR): MLRA 2 Lat: 47.935775 Long: -122.801153 Datum: NAD83
Soil Map Unit Name: Alderwood gravelly sandy loam, 15 to 30 percent slopes NWI classification: None
Are climatic / hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.)
Are Vegetation , Soil , or Hydrology , significantly disturbed? Are “Normal Circumstances” present? Yes No
Are Vegetation , Soil , or Hydrology , naturally problematic? (If needed, explain any answers in Remarks.)
SUMMARY OF FINDINGS – Attach site map showing sampling point locations, transects, important features, etc.
Hydrophytic Vegetation Present? Yes No
Is the Sampled Area
within a Wetland? Yes No Hydric Soil Present? Yes No
Wetland Hydrology Present? Yes No
Remarks:
The property is located in Jefferson County north of Highway 104 on Center Road. There is a stream that flows northerly through the property. A wetland system surrounds the of the stream onsite. Test Plot 1 was conducted east of the onsite wetland within the upland area
US Army Corps of Engineers Western Mountains, Valleys, and Coast – Version 2.0
SOIL Sampling Point: TP 1
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color (moist) % Color (moist) % Type1 Loc2 Texture Remarks
0-20 10YR 2/1 100 loam
1Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix, RC=Root Channel
Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3:
Histosol (A1) Sandy Redox (S5) 2 cm Muck (A10)
Histic Epipedon (A2) Stripped Matrix (S6) Red Parent Material (TF2)
Black Histic (A3) Loamy Mucky Mineral (F1) (except MLRA 1) Very Shallow Dark Surface (TF12)
Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Other (Explain in Remarks)
Depleted Below Dark Surface (A11) Depleted Matrix (F3)
3Indicators of hydrophytic vegetation and
wetland hydrology must be present,
unless disturbed or problematic.
Thick Dark Surface (A12) Redox Dark Surface (F6)
Sandy Mucky Mineral (S1) Depleted Dark Surface (F7)
Sandy Gleyed Matrix (S4) Redox Depressions (F8)
Restrictive Layer (if present):
Hydric Soils Present? Yes No
Type:
Depth (inches):
Remarks: The soil profile does not meet hydric soil indicators because the soil matrix is not depleted or gleyed and there are no redoximorphic features
HYDROLOGY
Wetland Hydrology Indicators:
Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required)
Surface Water (A1) Water-Stained Leaves (B9) Water-Stained Leaves (B9)
High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) (MLRA 1, 2, 4A, and 4B)
Saturation (A3) Salt Crust (B11) Drainage Patterns (B10)
Water Marks (B1) Aquatic Invertebrates (B13) Dry-Season Water Table (C2)
Sediment Deposits (B2) Hydrogen Sulfide Odor (C1) Saturation Visible on Aerial Imagery (C9)
Drift Deposits (B3) Oxidized Rhizospheres along Living Roots (C3) Geomorphic Position (D2)
Algal Mat or Crust (B4) Presence of Reduced Iron (C4) Shallow Aquitard (D3)
Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) FAC-Neutral Test (D5)
Surface Soil Cracks (B6) Stunted or Stresses Plants (D1) (LRR A) Raised Ant Mounds (D6) (LRR A)
Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) Frost-Heave Hummocks (D7)
Sparsely Vegetated Concave Surface (B8)
Field Observations:
Surface Water Present? Yes No Depth (inches):
Wetland Hydrology Present?
Yes
No
Water Table Present? Yes No Depth (inches):
Saturation Present?
(includes capillary fringe) Yes No Depth (inches):
Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks: Wetland hydrology criteria are not met because thesoil was not saturated and there was not a high water table present.
Project Site: Center Road
US Army Corps of Engineers Western Mountains, Valleys, and Coast – Version 2.0
WETLAND DETERMINATION DATA FORM – Western Mountains, Valleys, and Coast Region
VEGETATION – Use scientific names of plants
Tree Stratum (Plot size: 30' diameter) Absolute % Cover Dominant Species? Indicator Status Dominance Test Worksheet:
1. Alnus rubra 20 yes FAC Number of Dominant Species
That Are OBL, FACW, or FAC: 4 (A) 2.
3. Total Number of Dominant
Species Across All Strata: 4 (B) 4.
50% = 10, 20% = 4 20 = Total Cover Percent of Dominant Species
That Are OBL, FACW, or FAC: 100 (A/B) Sapling/Shrub Stratum (Plot size: 20' diameter)
1. Rubus spectabilis 30 yes FAC Prevalence Index worksheet:
2. Acer circinatum 20 yes FAC Total % Cover of: Multiply by:
3. Oemleria cerasiformis 5 no FACU OBL species x1 =
4. FACW species x2 =
5. FAC species x3 =
50% = 27.5, 20% = 11 55 = Total Cover FACU species x4 =
Herb Stratum (Plot size: 10' diameter) UPL species x5 =
1. Maianthemum dilatatum 50 yes FAC Column Totals: (A) (B)
2. Lysichiton americanus 10 no OBL Prevalence Index = B/A =
3. Oenanthe sarmentosa 2 no OBL Hydrophytic Vegetation Indicators:
4. 1 – Rapid Test for Hydrophytic Vegetation
5. 2 - Dominance Test is >50%
6. 3 - Prevalence Index is <3.01
7. 4 - Morphological Adaptations1 (Provide supporting
data in Remarks or on a separate sheet) 8.
9. 5 - Wetland Non-Vascular Plants1
10. Problematic Hydrophytic Vegetation1 (Explain)
11. 1Indicators of hydric soil and wetland hydrology must
be present, unless disturbed or problematic. 50% = 31, 20% = 12.4 62 = Total Cover
Woody Vine Stratum (Plot size: )
1.
Hydrophytic
Vegetation
Present?
Yes No 2.
50% = , 20% = = Total Cover
% Bare Ground in Herb Stratum 0
Remarks: The hydrophytic vegetation criterion is met because there is greater than 50% dominance by FAC species.
Project Site: Center Road City/County: Chimacum/Jefferson Sampling Date: 7/8/21
Applicant/Owner: Andrew Vodder State: WA Sampling Point: TP 2
Investigator(s): Brenda Ruddick Section, Township, Range: S09, T28, R1W WM
Landform (hillslope, terrace, etc.): hillslope Local relief (concave, convex, none): concave Slope (%): none
Subregion (LRR): MLRA 2 Lat: 47.935775 Long: -122.801153 Datum: NAD83
Soil Map Unit Name: Semiahmoo muck NWI classification: None
Are climatic / hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.)
Are Vegetation , Soil , or Hydrology , significantly disturbed? Are “Normal Circumstances” present? Yes No
Are Vegetation , Soil , or Hydrology , naturally problematic? (If needed, explain any answers in Remarks.)
SUMMARY OF FINDINGS – Attach site map showing sampling point locations, transects, important features, etc.
Hydrophytic Vegetation Present? Yes No
Is the Sampled Area
within a Wetland? Yes No Hydric Soil Present? Yes No
Wetland Hydrology Present? Yes No
Remarks:
The property is located in Jefferson County north of Highway 104 on Center Road. There is a stream that flows northerly through the property. A wetland system surrounds the of the stream onsite. Test Plot 2 was conducted within the wetland southern half of the property
US Army Corps of Engineers Western Mountains, Valleys, and Coast – Version 2.0
SOIL Sampling Point: TP 2
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(inches) Color (moist) % Color (moist) % Type1 Loc2 Texture Remarks
0-19 Gley1 2.5/N 100 muck
si - silt
lo - loam
1Type: C= Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains. 2Location: PL=Pore Lining, M=Matrix, RC=Root Channel
Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3:
Histosol (A1) Sandy Redox (S5) 2 cm Muck (A10)
Histic Epipedon (A2) Stripped Matrix (S6) Red Parent Material (TF2)
Black Histic (A3) Loamy Mucky Mineral (F1) (except MLRA 1) Very Shallow Dark Surface (TF12)
Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Other (Explain in Remarks)
Depleted Below Dark Surface (A11) Depleted Matrix (F3)
3Indicators of hydrophytic vegetation and
wetland hydrology must be present,
unless disturbed or problematic.
Thick Dark Surface (A12) Redox Dark Surface (F6)
Sandy Mucky Mineral (S1) Depleted Dark Surface (F7)
Sandy Gleyed Matrix (S4) Redox Depressions (F8)
Restrictive Layer (if present):
Hydric Soils Present? Yes No
Type:
Depth (inches):
Remarks: The soil profile does meets hydric soil indicators because the soil is a muck orgamic material.
HYDROLOGY
Wetland Hydrology Indicators:
Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required)
Surface Water (A1) Water-Stained Leaves (B9) Water-Stained Leaves (B9)
High Water Table (A2) (except MLRA 1, 2, 4A, and 4B) (MLRA 1, 2, 4A, and 4B)
Saturation (A3) Salt Crust (B11) Drainage Patterns (B10)
Water Marks (B1) Aquatic Invertebrates (B13) Dry-Season Water Table (C2)
Sediment Deposits (B2) Hydrogen Sulfide Odor (C1) Saturation Visible on Aerial Imagery (C9)
Drift Deposits (B3) Oxidized Rhizospheres along Living Roots (C3) Geomorphic Position (D2)
Algal Mat or Crust (B4) Presence of Reduced Iron (C4) Shallow Aquitard (D3)
Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) FAC-Neutral Test (D5)
Surface Soil Cracks (B6) Stunted or Stresses Plants (D1) (LRR A) Raised Ant Mounds (D6) (LRR A)
Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) Frost-Heave Hummocks (D7)
Sparsely Vegetated Concave Surface (B8)
Field Observations:
Surface Water Present? Yes No Depth (inches):
Wetland Hydrology Present?
Yes
No
Water Table Present? Yes No Depth (inches): 9
Saturation Present?
(includes capillary fringe) Yes No Depth (inches): 0
Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks: Wetland hydrology criteria are met because the soil is saturated to the surface and there is a high water table.
Project Site: Center Road
APPENDIX B
Wetland name or number:
Wetland Rating System for Western WA: 2014 Update Rating Form – Effective January 1, 2015
1
RATING SUMMARY – Western Washington
Name of wetland (or ID #): Vodder Property Date of site visit: 7/8/21
Rated by: Brenda Ruddick Trained by Ecology? X Yes No Date of training: 03/21
HGM Class used for rating: Depressional Wetland has multiple HGM classes? _Y X N
NOTE: Form is not complete without the figures requested (figures can be combined).
Source of base aerial photo/map: Google Earth
OVERALL WETLAND CATEGORY II (based on functions X or special characteristics _)
1. Category of wetland based on FUNCTIONS
Category I – Total score = 23 – 27
X Category II – Total score = 20 – 22
Category III – Total score = 16 – 19
Category IV – Total score = 9 – 15
FUNCTION Improving
Water Quality
Hydrologic Habitat
Circle the appropriate ratings
Site Potential H M L H M L H M L
Landscape Potential H M L H M L H M L
Value H M L H M L H M L TOTAL
Score Based on
Ratings
8 5 7 20
2. Category based on SPECIAL CHARACTERISTICS of wetland
Score for each function based on three ratings (order of ratings is not important)
9 = H,H,H
8 = H,H,M
7 = H,H,L
7 = H,M,M
6 = H,M,L
6 = M,M,M
5 = H,L,L
5 = M,M,L
4 = M,L,L
3 = L,L,L
CHARACTERISTIC CATEGORY
Estuarine I II
Wetland of High Conservation Value I
Bog I
Mature Forest I
Old Growth Forest I
Coastal Lagoon I II
Interdunal I II III IV
None of the above N/A
Wetland name or number:
Wetland Rating System for Western WA: 2014 Update Rating Form – Effective January 1, 2015
2
Maps and figures required to answer questions correctly for
Western Washington
Depressional Wetlands
Map of: To answer questions: Figure #
Cowardin plant classes D 1.3, H 1.1, H 1.4 6
Hydroperiods D 1.4, H 1.2 6
Location of outlet (can be added to map of hydroperiods) D 1.1, D 4.1 6
Boundary of area within 150 ft of the wetland (can be added to another figure) D 2.2, D 5.2 6
Map of the contributing basin D 4.3, D 5.3 6
1 km Polygon: Area that extends 1 km from entire wetland edge - including
polygons for accessible habitat and undisturbed habitat
H 2.1, H 2.2, H 2.3 7
Screen capture of map of 303(d) listed waters in basin (from Ecology website) D 3.1, D 3.2 8
Screen capture of list of TMDLs for WRIA in which unit is found (from web) D 3.3 8
Riverine Wetlands
Map of: To answer questions: Figure #
Cowardin plant classes H 1.1, H 1.4
Hydroperiods H 1.2
Ponded depressions R 1.1
Boundary of area within 150 ft of the wetland (can be added to another figure) R 2.4
Plant cover of trees, shrubs, and herbaceous plants R 1.2, R 4.2
Width of unit vs. width of stream (can be added to another figure) R 4.1
Map of the contributing basin R 2.2, R 2.3, R 5.2
1 km Polygon: Area that extends 1 km from entire wetland edge - including
polygons for accessible habitat and undisturbed habitat
H 2.1, H 2.2, H 2.3
Screen capture of map of 303(d) listed waters in basin (from Ecology website) R 3.1
Screen capture of list of TMDLs for WRIA in which unit is found (from web) R 3.2, R 3.3
Lake Fringe Wetlands
Map of: To answer questions: Figure #
Cowardin plant classes L 1.1, L 4.1, H 1.1, H 1.4
Plant cover of trees, shrubs, and herbaceous plants L 1.2
Boundary of area within 150 ft of the wetland (can be added to another figure) L 2.2
1 km Polygon: Area that extends 1 km from entire wetland edge - including
polygons for accessible habitat and undisturbed habitat
H 2.1, H 2.2, H 2.3
Screen capture of map of 303(d) listed waters in basin (from Ecology website) L 3.1, L 3.2
Screen capture of list of TMDLs for WRIA in which unit is found (from web) L 3.3
Slope Wetlands
Map of: To answer questions: Figure #
Cowardin plant classes H 1.1, H 1.4
Hydroperiods H 1.2
Plant cover of dense trees, shrubs, and herbaceous plants S 1.3
Plant cover of dense, rigid trees, shrubs, and herbaceous plants
(can be added to figure above)
S 4.1
Boundary of 150 ft buffer (can be added to another figure) S 2.1, S 5.1
1 km Polygon: Area that extends 1 km from entire wetland edge - including
polygons for accessible habitat and undisturbed habitat
H 2.1, H 2.2, H 2.3
Screen capture of map of 303(d) listed waters in basin (from Ecology website) S 3.1, S 3.2
Screen capture of list of TMDLs for WRIA in which unit is found (from web) S 3.3
Wetland name or number:
Wetland Rating System for Western WA: 2014 Update Rating Form – Effective January 1, 2015
3
HGM Classification of Wetlands in Western Washington
For questions 1-7, the criteria described must apply to the entire unit being rated.
If the hydrologic criteria listed in each question do not apply to the entire unit being rated, you
probably have a unit with multiple HGM classes. In this case, identify which hydrologic criteria in
questions 1-7 apply, and go to Question 8.
1. Are the water levels in the entire unit usually controlled by tides except during floods?
NO – go to 2 YES – the wetland class is Tidal Fringe – go to 1.1
1.1 Is the salinity of the water during periods of annual low flow below 0.5 ppt (parts per thousand)?
NO – Saltwater Tidal Fringe (Estuarine) YES – Freshwater Tidal Fringe
If your wetland can be classified as a Freshwater Tidal Fringe use the forms for Riverine wetlands. If it
is Saltwater Tidal Fringe it is an Estuarine wetland and is not scored. This method cannot be used to
score functions for estuarine wetlands.
2. The entire wetland unit is flat and precipitation is the only source (>90%) of water to it. Groundwater
and surface water runoff are NOT sources of water to the unit.
NO – go to 3 YES – The wetland class is Flats
If your wetland can be classified as a Flats wetland, use the form for Depressional wetlands.
3. Does the entire wetland unit meet all of the following criteria?
The vegetated part of the wetland is on the shores of a body of permanent open water (without any
plants on the surface at any time of the year) at least 20 ac (8 ha) in size;
At least 30% of the open water area is deeper than 6.6 ft (2 m).
NO – go to 4 YES – The wetland class is Lake Fringe (Lacustrine Fringe)
4. Does the entire wetland unit meet all of the following criteria?
The wetland is on a slope (slope can be very gradual),
The water flows through the wetland in one direction (unidirectional) and usually comes from
seeps. It may flow subsurface, as sheetflow, or in a swale without distinct banks, The water leaves the wetland without being impounded.
NO – go to 5 YES – The wetland class is Slope
NOTE: Surface water does not pond in these type of wetlands except occasionally in very small and
shallow depressions or behind hummocks (depressions are usually <3 ft diameter and less than 1 ft
deep).
5. Does the entire wetland unit meet all of the following criteria?
The unit is in a valley, or stream channel, where it gets inundated by overbank flooding from that
stream or river, The overbank flooding occurs at least once every 2 years.
Wetland name or number:
Wetland Rating System for Western WA: 2014 Update Rating Form – Effective January 1, 2015
4
NO – go to 6 YES – The wetland class is Riverine
NOTE: The Riverine unit can contain depressions that are filled with water when the river is not
flooding
6. Is the entire wetland unit in a topographic depression in which water ponds, or is saturated to the
surface, at some time during the year? This means that any outlet, if present, is higher than the interior
of the wetland.
NO – go to 7 YES – The wetland class is Depressional
7. Is the entire wetland unit located in a very flat area with no obvious depression and no overbank
flooding? The unit does not pond surface water more than a few inches. The unit seems to be
maintained by high groundwater in the area. The wetland may be ditched, but has no obvious natural
outlet.
NO – go to 8 YES – The wetland class is Depressional
8. Your wetland unit seems to be difficult to classify and probably contains several different HGM
classes. For example, seeps at the base of a slope may grade into a riverine floodplain, or a small
stream within a Depressional wetland has a zone of flooding along its sides. GO BACK AND IDENTIFY
WHICH OF THE HYDROLOGIC REGIMES DESCRIBED IN QUESTIONS 1-7 APPLY TO DIFFERENT
AREAS IN THE UNIT (make a rough sketch to help you decide). Use the following table to identify the
appropriate class to use for the rating system if you have several HGM classes present within the
wetland unit being scored.
NOTE: Use this table only if the class that is recommended in the second column represents 10% or
more of the total area of the wetland unit being rated. If the area of the HGM class listed in column 2
is less than 10% of the unit; classify the wetland using the class that represents more than 90% of the
total area.
HGM classes within the wetland unit
being rated
HGM class to
use in rating
Slope + Riverine Riverine
Slope + Depressional Depressional
Slope + Lake Fringe Lake Fringe
Depressional + Riverine along stream
within boundary of depression
Depressional
Depressional + Lake Fringe Depressional
Riverine + Lake Fringe Riverine
Salt Water Tidal Fringe and any other
class of freshwater wetland
Treat as
ESTUARINE
If you are still unable to determine which of the above criteria apply to your wetland, or if you have
more than 2 HGM classes within a wetland boundary, classify the wetland as Depressional for the
rating.
Wetland name or number:
Wetland Rating System for Western WA: 2014 Update Rating Form – Effective January 1, 2015
5
DEPRESSIONAL AND FLATS WETLANDS
Water Quality Functions - Indicators that the site functions to improve water quality
D 1.0. Does the site have the potential to improve water quality?
D 1.1. Characteristics of surface water outflows from the wetland:
Wetland is a depression or flat depression (QUESTION 7 on key) with no surface water leaving it (no outlet).
points = 3
Wetland has an intermittently flowing stream or ditch, OR highly constricted permanently flowing outlet.
points = 2
Wetland has an unconstricted, or slightly constricted, surface outlet that is permanently flowing points = 1
Wetland is a flat depression (QUESTION 7 on key), whose outlet is a permanently flowing ditch. points = 1
1
D 1.2. The soil 2 in below the surface (or duff layer) is true clay or true organic (use NRCS definitions).Yes = 4 No = 0 4
D 1.3. Characteristics and distribution of persistent plants (Emergent, Scrub-shrub, and/or Forested Cowardin classes):
Wetland has persistent, ungrazed, plants > 95% of area points = 5
Wetland has persistent, ungrazed, plants > ½ of area points = 3
Wetland has persistent, ungrazed plants > 1/ of area points = 1 10
Wetland has persistent, ungrazed plants <1/ of area points = 0 10
5
D 1.4. Characteristics of seasonal ponding or inundation:
This is the area that is ponded for at least 2 months. See description in manual.
Area seasonally ponded is > ½ total area of wetland points = 4
Area seasonally ponded is > ¼ total area of wetland points = 2
Area seasonally ponded is < ¼ total area of wetland points = 0
2
Total for D 1 Add the points in the boxes above 12
Rating of Site Potential If score is: X 12-16 = H 6-11 = M 0-5 = L Record the rating on the first page
D 2.0. Does the landscape have the potential to support the water quality function of the site?
D 2.1. Does the wetland unit receive stormwater discharges? Yes = 1 No = 0 0
D 2.2. Is > 10% of the area within 150 ft of the wetland in land uses that generate pollutants? Yes = 1 No = 0 0
D 2.3. Are there septic systems within 250 ft of the wetland? Yes = 1 No = 0 1
D 2.4. Are there other sources of pollutants coming into the wetland that are not listed in questions D 2.1 -D 2.3?
Source Yes = 1 No = 0
0
Total for D 2 Add the points in the boxes above 1
Rating of Landscape Potential If score is: 3 or 4 = H X 1 or 2 = M 0 = L Record the rating on the first page
D 3.0. Is the water quality improvement provided by the site valuable to society?
D 3.1. Does the wetland discharge directly (i.e., within 1 mi) to a stream, river, lake, or marine water that is on the
303(d) list? Yes = 1 No = 0
1
D 3.2. Is the wetland in a basin or sub-basin where an aquatic resource is on the 303(d) list? Yes = 1 No = 0 1
D 3.3. Has the site been identified in a watershed or local plan as important for maintaining water quality (answer YES
if there is a TMDL for the basin in which the unit is found)? Yes = 2 No = 0
0
Total for D 3 Add the points in the boxes above 2
Rating of Value If score is: X 2-4 = H 1 = M 0 = L Record the rating on the first page
Wetland name or number:
Wetland Rating System for Western WA: 2014 Update Rating Form – Effective January 1, 2015
6
DEPRESSIONAL AND FLATS WETLANDS
Hydrologic Functions - Indicators that the site functions to reduce flooding and stream degradation
D 4.0. Does the site have the potential to reduce flooding and erosion?
D 4.1. Characteristics of surface water outflows from the wetland:
Wetland is a depression or flat depression with no surface water leaving it (no outlet) points = 4
Wetland has an intermittently flowing stream or ditch, OR highly constricted permanently flowing outletpoints = 2
Wetland is a flat depression (QUESTION 7 on key), whose outlet is a permanently flowing ditch points = 1
Wetland has an unconstricted, or slightly constricted, surface outlet that is permanently flowing points = 0
0
D 4.2. Depth of storage during wet periods: Estimate the height of ponding above the bottom of the outlet. For wetlands
with no outlet, measure from the surface of permanent water or if dry, the deepest part.
Marks of ponding are 3 ft or more above the surface or bottom of outlet points = 7
Marks of ponding between 2 ft to < 3 ft from surface or bottom of outlet points = 5
Marks are at least 0.5 ft to < 2 ft from surface or bottom of outlet points = 3
The wetland is a “headwater” wetland points = 3
Wetland is flat but has small depressions on the surface that trap water points = 1
Marks of ponding less than 0.5 ft (6 in) points = 0
5
D 4.3. Contribution of the wetland to storage in the watershed: Estimate the ratio of the area of upstream basin
contributing surface water to the wetland to the area of the wetland unit itself.
The area of the basin is less than 10 times the area of the unit points = 5
The area of the basin is 10 to 100 times the area of the unit points = 3
The area of the basin is more than 100 times the area of the unit points = 0
Entire wetland is in the Flats class points = 5
3
Total for D 4 Add the points in the boxes above 8
Rating of Site Potential If score is: 12-16 = H X 6-11 = M 0-5 = L Record the rating on the first page
D 5.0. Does the landscape have the potential to support hydrologic functions of the site?
D 5.1. Does the wetland receive stormwater discharges? Yes = 1 No = 0 0
D 5.2. Is >10% of the area within 150 ft of the wetland in land uses that generate excess runoff? Yes = 1 No = 0 0
D 5.3. Is more than 25% of the contributing basin of the wetland covered with intensive human land uses (residential at
>1 residence/ac, urban, commercial, agriculture, etc.)? Yes = 1 No = 0
0
Total for D 5 Add the points in the boxes above 0
Rating of Landscape Potential If score is: 3 = H 1 or 2 = M X 0 = L Record the rating on the first page
D 6.0. Are the hydrologic functions provided by the site valuable to society?
D 6.1. The unit is in a landscape that has flooding problems. Choose the description that best matches conditions around
the wetland unit being rated. Do not add points. Choose the highest score if more than one condition is met.
The wetland captures surface water that would otherwise flow down-gradient into areas where flooding has
damaged human or natural resources (e.g., houses or salmon redds):
• Flooding occurs in a sub-basin that is immediately down-gradient of unit. points = 2
• Surface flooding problems are in a sub-basin farther down-gradient. points = 1
Flooding from groundwater is an issue in the sub-basin. points = 1
The existing or potential outflow from the wetland is so constrained by human or natural conditions that the
water stored by the wetland cannot reach areas that flood. Explain why points = 0
There are no problems with flooding downstream of the wetland. points = 0
1
D 6.2. Has the site been identified as important for flood storage or flood conveyance in a regional flood control plan?
Yes = 2 No = 0
0
Total for D 6 Add the points in the boxes above 1
Rating of Value If score is: 2-4 = H X 1 = M 0 = L Record the rating on the first page
Wetland name or number:
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These questions apply to wetlands of all HGM classes.
HABITAT FUNCTIONS - Indicators that site functions to provide important habitat
H 1.0. Does the site have the potential to provide habitat?
H 1.1. Structure of plant community: Indicators are Cowardin classes and strata within the Forested class. Check the
Cowardin plant classes in the wetland. Up to 10 patches may be combined for each class to meet the threshold
of ¼ ac or more than 10% of the unit if it is smaller than 2.5 ac. Add the number of structures checked.
Aquatic bed 4 structures or more: points = 4
X Emergent 3 structures: points = 2
Scrub-shrub (areas where shrubs have > 30% cover) 2 structures: points = 1
X Forested (areas where trees have > 30% cover) 1 structure: points = 0
If the unit has a Forested class, check if:
X 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
2
H 1.2. Hydroperiods
Check the types of water regimes (hydroperiods) present within the wetland. The water regime has to cover
more than 10% of the wetland or ¼ ac to count (see text for descriptions of hydroperiods).
Permanently flooded or inundated 4 or more types present: points = 3
X Seasonally flooded or inundated 3 types present: points = 2
Occasionally flooded or inundated 2 types present: points = 1
X Saturated only 1 type present: points = 0
X Permanently flowing stream or river in, or adjacent to, the wetland
Seasonally flowing stream in, or adjacent to, the wetland
Lake Fringe wetland 2 points
Freshwater tidal wetland 2 points
2
H 1.3. Richness of plant species
Count the number of plant species in the wetland that cover at least 10 ft2.
Different patches of the same species can be combined to meet the size threshold and you do not have to name
the species. Do not include Eurasian milfoil, reed canarygrass, purple loosestrife, Canadian thistle
If you counted: > 19 species points = 2
5 - 19 species points = 1
< 5 species points = 0
1
H 1.4. Interspersion of habitats
Decide from the diagrams below whether interspersion among Cowardin plants classes (described in H 1.1), or
the classes and unvegetated areas (can include open water or mudflats) is high, moderate, low, or none. If you
have four or more plant classes or three classes and open water, the rating is always high.
None = 0 points Low = 1 point Moderate = 2 points
All three diagrams
in this row
are HIGH = 3points
1
Wetland name or number:
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H 1.5. Special habitat features:
Check the habitat features that are present in the wetland. The number of checks is the number of points.
X Large, downed, woody debris within the wetland (> 4 in diameter and 6 ft long).
Standing snags (dbh > 4 in) within the wetland
X Undercut banks are present for at least 6.6 ft (2 m) and/or overhanging plants extends at least 3.3 ft (1 m)
over a stream (or ditch) in, or contiguous with the wetland, for at least 33 ft (10 m)
Stable steep banks of fine material that might be used by beaver or muskrat for denning (> 30 degree
slope) OR signs of recent beaver activity are present (cut shrubs or trees that have not yet weathered
where wood is exposed)
X At least ¼ ac of thin-stemmed persistent plants 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 every stratum of plants (see H 1.1 for list of
strata)
3
Total for H 1 Add the points in the boxes above 9
Rating of Site Potential If score is: 15-18 = H X 7-14 = M 0-6 = L Record the rating on the first page
H 2.0. Does the landscape have the potential to support the habitat functions of the site?
H 2.1. Accessible habitat (include only habitat that directly abuts wetland unit).
Calculate: % undisturbed habitat 1 + [(% moderate and low intensity land uses)/2] 2.4 = 3.4 %
If total accessible habitat is:
> 1/ (33.3%) of 1 km Polygon points = 3 3
20-33% of 1 km Polygon points = 2
10-19% of 1 km Polygon points = 1
< 10% of 1 km Polygon points = 0
0
H 2.2. Undisturbed habitat in 1 km Polygon around the wetland.
Calculate: % undisturbed habitat 1.5 + [(% moderate and low intensity land uses)/2] 19.9 = 21.4 %
Undisturbed habitat > 50% of Polygon points = 3
Undisturbed habitat 10-50% and in 1-3 patches points = 2
Undisturbed habitat 10-50% and > 3 patches points = 1
Undisturbed habitat < 10% of 1 km Polygon points = 0
1
H 2.3. Land use intensity in 1 km Polygon: If
> 50% of 1 km Polygon is high intensity land use points = (- 2)
≤ 50% of 1 km Polygon is high intensity points = 0
-2
Total for H 2 Add the points in the boxes above -1
Rating of Landscape Potential If score is: 4-6 = H 1-3 = M X < 1 = L Record the rating on the first page
H 3.0. Is the habitat provided by the site valuable to society?
H 3.1. Does the site provide habitat for species valued in laws, regulations, or policies? Choose only the highest score
that applies to the wetland being rated.
Site meets ANY of the following criteria: points = 2
⎯ It has 3 or more priority habitats within 100 m (see next page)
⎯ It provides habitat for Threatened or Endangered species (any plant or animal on the state or federal lists) ⎯ It is mapped as a location for an individual WDFW priority species ⎯ It is a Wetland of High Conservation Value as determined by the Department of Natural Resources ⎯ It has been categorized as an important habitat site in a local or regional comprehensive plan, in a
Shoreline Master Plan, or in a watershed plan
Site has 1 or 2 priority habitats (listed on next page) within 100 m points = 1
Site does not meet any of the criteria above points = 0
Rating of Value If score is: 2 = H X 1 = M 0 = L Record the rating on the first page
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Wetland name or number:
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WDFW Priority Habitats
Priority habitats listed by WDFW (see complete descriptions of WDFW priority habitats, and the counties in which they can
be found, in: Washington Department of Fish and Wildlife. 2008. Priority Habitat and Species List. Olympia, Washington.
177 pp. http://wdfw.wa.gov/publications/00165/wdfw00165.pdf or access the list from here:
http://wdfw.wa.gov/conservation/phs/list/)
Count how many of the following priority habitats are within 330 ft (100 m) of the wetland unit: NOTE: This question is
independent of the land use between the wetland unit and the priority habitat.
⎯ Aspen Stands: Pure or mixed stands of aspen greater than 1 ac (0.4 ha). ⎯ Biodiversity Areas and Corridors: Areas of habitat that are relatively important to various species of native fish and
wildlife (full descriptions in WDFW PHS report).
⎯ 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 8 trees/ac (20 trees/ha ) > 32 in (81 cm) dbh or > 200
years of age. Mature forests – Stands with average diameters exceeding 21 in (53 cm) dbh; crown cover may be less
than 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: Woodland 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 – see web link above). X 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 – see web link above).
X 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 –
see web link on previous page).
⎯ 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 25 ft (7.6 m) high and occurring below 5000 ft elevation. ⎯ Talus: Homogenous areas of rock rubble ranging in average size 0.5 - 6.5 ft (0.15 - 2.0 m), 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 > 20 in (51 cm) in western
Washington and are > 6.5 ft (2 m) in height. Priority logs are > 12 in (30 cm) in diameter at the largest end, and > 20 ft
(6 m) long.
Note: All vegetated wetlands are by definition a priority habitat but are not included in this list because they are addressed
elsewhere.
Wetland name or number:
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Wetland Type
Check off any criteria that apply to the wetland. Circle the category when the appropriate criteria are met.
Category
SC 1.0. Estuarine wetlands
Does the wetland meet the following criteria for Estuarine wetlands?
⎯ The dominant water regime is tidal,
⎯ Vegetated, and
⎯ With a salinity greater than 0.5 ppt Yes –Go to SC 1.1 No= Not an estuarine wetland
SC 1.1. Is the wetland within a National Wildlife Refuge, National Park, National Estuary Reserve, Natural Area
Preserve, State Park or Educational, Environmental, or Scientific Reserve designated under WAC 332 -30-151?
Yes = Category I No - Go to SC 1.2
Cat. I
SC 1.2. Is the wetland unit at least 1 ac in size and meets at least two of the following three conditions?
⎯ The wetland is relatively undisturbed (has no diking, ditching, filling, cultivation, grazing, and has less
than 10% cover of non-native plant species. (If non-native species are Spartina, see page 25)
⎯ At least ¾ of the landward edge of the wetland has a 100 ft buffer of shrub, forest, or un-grazed or un-
mowed grassland.
⎯ The wetland has at least two of the following features: tidal channels, depressions with open water, or
contiguous freshwater wetlands. Yes = Category I No = Category II
Cat. I
Cat. II
SC 2.0. Wetlands of High Conservation Value (WHCV)
SC 2.1. Has the WA Department of Natural Resources updated their website to include the list of Wetlands of High
Conservation Value? Yes – Go to SC 2.2 No – Go to SC 2.3
SC 2.2. Is the wetland listed on the WDNR database as a Wetland of High Conservation Value?
Yes = Category I No = Not a WHCV
SC 2.3. Is the wetland in a Section/Township/Range that contains a Natural Heritage wetland?
http://www1.dnr.wa.gov/nhp/refdesk/datasearch/wnhpwetlands.pdf
Yes – Contact WNHP/WDNR and go to SC 2.4 No = Not a WHCV
SC 2.4. Has WDNR identified the wetland within the S/T/R as a Wetland of High Conservation Value and listed it on
their website? Yes = Category I No = Not a WHCV
Cat. I
SC 3.0. Bogs
Does the wetland (or any part of the unit) meet both the criteria for soils and vegetation in bogs? Use the key
below. If you answer YES you will still need to rate the wetland based on its functions.
SC 3.1. Does an area within the wetland unit have organic soil horizons, either peats or mucks, that compose 16 in or
more of the first 32 in of the soil profile? Yes – Go to SC 3.3 No – Go to SC 3.2
SC 3.2. Does an area within the wetland unit have organic soils, either peats or mucks, that are less than 16 in deep
over bedrock, or an impermeable hardpan such as clay or volcanic ash, or that are floating on top of a lake or
pond? Yes – Go to SC 3.3 No = Is not a bog
SC 3.3. Does an area with peats or mucks have more than 70% cover of mosses at ground level, AND at least a 30%
cover of plant species listed in Table 4? Yes = Is a Category I bog No – Go to SC 3.4
NOTE: If you are uncertain about the extent of mosses in the understory, you may substitute that criterion by
measuring the pH of the water that seeps into a hole dug at least 16 in deep. If the pH is less than 5.0 and the
plant species in Table 4 are present, the wetland is a bog.
SC 3.4. Is an area with peats or mucks forested (> 30% cover) with Sitka spruce, subalpine fir, western red cedar,
western hemlock, lodgepole pine, quaking aspen, Engelmann spruce, or western white pine, AND any of the
species (or combination of species) listed in Table 4 provide more than 30% of the cover under the canopy?
Yes = Is a Category I bog No = Is not a bog
Cat. I
CATEGORIZATION BASED ON SPECIAL CHARACTERISTICS
Wetland name or number:
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SC 4.0. Forested Wetlands
Does the wetland have at least 1 contiguous acre of forest that meets one of these criteria for the WA
Department of Fish and Wildlife’s forests as priority habitats? If you answer YES you will still need to rate
the wetland based on its functions.
⎯ Old-growth forests (west of Cascade crest): Stands of at least two tree species, forming a multi-layered
canopy with occasional small openings; with at least 8 trees/ac (20 trees/ha) that are at least 200 years of
age OR have a diameter at breast height (dbh) of 32 in (81 cm) or more.
⎯ Mature forests (west of the Cascade Crest): Stands where the largest trees are 80- 200 years old OR the
species that make up the canopy have an average diameter (dbh) exceeding 21 in (53 cm).
Yes = Category I No = Not a forested wetland for this section
Cat. I
SC 5.0. Wetlands in Coastal Lagoons
Does the wetland meet all of the following criteria of a wetland in a coastal lagoon?
⎯ The wetland lies in a depression adjacent to marine waters that is wholly or partially separated from
marine waters by sandbanks, gravel banks, shingle, or, less frequently, rocks
⎯ The lagoon in which the wetland is located contains ponded water that is saline or brackish (> 0.5 ppt)
during most of the year in at least a portion of the lagoon (needs to be measured near the bottom)
Yes – Go to SC 5.1 No = Not a wetland in a coastal lagoon
SC 5.1. Does the wetland meet all of the following three conditions?
⎯ The wetland is relatively undisturbed (has no diking, ditching, filling, cultivation, grazing), and has less
than 20% cover of aggressive, opportunistic plant species (see list of species on p. 100).
⎯ At least ¾ of the landward edge of the wetland has a 100 ft buffer of shrub, forest, or un-grazed or un-
mowed grassland.
⎯ The wetland is larger than 1/ ac (4350 ft2) 10
Yes = Category I No = Category II
Cat. I
Cat. II
SC 6.0. Interdunal Wetlands
Is the wetland west of the 1889 line (also called the Western Boundary of Upland Ownership or WBUO)? If
you answer yes you will still need to rate the wetland based on its habitat functions.
In practical terms that means the following geographic areas:
⎯ Long Beach Peninsula: Lands west of SR 103
⎯ Grayland-Westport: Lands west of SR 105
⎯ Ocean Shores-Copalis: Lands west of SR 115 and SR 109
Yes – Go to SC 6.1 No = not an interdunal wetland for rating
SC 6.1. Is the wetland 1 ac or larger and scores an 8 or 9 for the habitat functions on the form (rates H,H,H or H,H,M
for the three aspects of function)? Yes = Category I No – Go to SC 6.2
SC 6.2. Is the wetland 1 ac or larger, or is it in a mosaic of wetlands that is 1 ac or larger?
Yes = Category II No – Go to SC 6.3
SC 6.3. Is the unit between 0.1 and 1 ac, or is it in a mosaic of wetlands that is between 0.1 and 1 ac?
Yes = Category III No = Category IV
Cat I
Cat. II
Cat. III
Cat. IV
Category of wetland based on Special Characteristics
If you answered No for all types, enter “Not Applicable” on Summary Form
N/A
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Wetland name or number:
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