HomeMy WebLinkAbout2019.08.00 - Wetland Delineation and Categorization Hill's Addition Block 14Olympic Wetland Resources, IRc.
Dixie Llewellin, Principal Biologist
856 50th Street
Port Townsend, WA 98368
360 385-6/.32
dixie@cablesoeed.com
February 4,2021
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Everett Sorensen
715 Grant Street
Port Townsend, WA 98368
Wetland Delineation Addendum
Kim meVDideu m/Sorensen
LUP20-007 Critical Area Permit and Restrictive Covenant
Parcels 959 7A1401, 959701403 (Block 14) and,95970150i (Block 15)
This is an addendum to the original Wetland Delineation conducted by Olympic Wetland Resourceso
LLC in August 2A19, At that time, a 660 sqft Category IV wetland was categorized. The wetland edge
was delineated and the 50' buffer established. This small, degraded wetland appears to have been a
result of past logging road construction in2004.
The proposed developments include the installation an asphalt driveway with utilities (water main,
hydrant, electric communications conduit, and stormwater management features) along the undeveloped
portion of Katherine Street. f"hese street improvements would service two proposed houses on Block l5
and the southem portion of Block 14 as shown on the Sorensen site plan.
As requested by the City, additional data is required during the wet season to determine if there is a
change in the wetland size or location, Field work was conducted on February 2,2021 after a significant
rain event of over one inch of precipitation the previous day. The focus of the field work was to
determine the proximity of the eastern wetland edge (if there were changes) in relationship to the
proposed Kathrine Street development. Although the entire area was observed for additional water
ponding, the focus was on the eastern porlion of Lots 7 and 8. Findings from this wet-season evaluation
determined there are no significant changes in the wetland size or location of boundaries. It is still
within the swale created by the logging road and a distinct vegetation change from sedge to upland
species (salal, Douglas fir, and Madrone). Once again using a hip chain the site was measured betweeu
the eastern edge of the wetland (Lots 7 and 8 Block 14 Parcels 959 70I40I) and the western edge of the
proposed Katherine Street development. The development is 96 feet from the wetland edge and well out
of the 50 foot buffer of this small Category IV roadside wetland. If more data is required, please do not
hesitate to call.
tted,
RE.CEIVE,D
Dixie Llewellin dixie@cablespeed.com
Principal Biologist, Olympic Wetland Resources, LLC
Certified for Wetland Delineation, WTI
Certified for Wetland Rating and Soil Analysis DOE, 2007,2012,2014
Sorensen Wetland Delineation Addendum
Report File #20210202
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60' tForestedt---rr--'\octiff st959700701 Forested-660 SF Wetland60't\_Proposed 10 ftWide AsphaltDriveway Apron95970060133'd Sfreef\-r--12',200't 60'I-_\r\ROWJ-r-\rr-\___-/>so9'x18' Gravel, -rZ-,8g Spaces./ExistingLogging RdForested1 0"FForestedForested<-tExistingPoint ofVehicleAccess,\200' .Proposed Gravel Driveway2a\?60(o(t(o!oJ(0oI(t'I50 ft WetlandProtectionBufferI/oUb6cndoTo{(o(tl(o{oJG)oN)o)oIoq95970140320,000 ft2/i/55Proposed 2-Block Asphalt Katherine Street Extension with Turnaroundincluding Water Main, Hydrant, SS Main, Electric & Comm Conduitand Permanent Stormwater Management Features/'IForestedEvergreen Engineering715 Grant StreetPort Townsend, WA 98368-2405360-82 1 -9960. January 21,2020i Revised September 21 ,2020rto)o3/d Sfreef ROW959701701 \.\959701601 ex.House & ADU60' I++\240 Ft600Scale at 8.5"x11": 1 inch = 60 ftDrawn By: EverettA. Sorensen, P.E.180Parcel Boundaries and Elevation Contoursfrom Jefferson County On-line GIS2ltolzoaConstruction Site PlanKi mmel/Di deu m/So ren se nHills Addition Blocks 14 and 15Port Townsend, WA 98368120xA)odHso)-rlol<, I--l@livot-t\-1\Proposed House<1,200 sF. -FF: -256'('rq>201-2% SloPe3l(tlOpaTwoLot2100'Block1X4200'Forestedr -6-l_-'Proposed Areato be Cleared6/rcels000-SFForestedLot 7taaa\tProoosedtorm'swalesProposed 10 ft WideAsphalt Driveway ApronS('lo4roposed House<1,800 sFFF=253'tttI100' 8ForestedExistino SurvevAtAll dlock C5r(PinnerssAFN 407225Block 15One Parcel959701 50140,000 ft2<1J27Golarage-&ADU <4OO SFz/Proposed20'x2OExisting 6'x10'Garden Shedposed Area tobe Cleared-6,000 s. gA.SJefferson County Parcels 959701403 and 959701501
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Everett Sorensen
Wetland Delineation and Catego rization
Parcels 9597 01401, 9597 01403 , 9597 01 50 1
July/August 2019
Prepared for:
Everett Sorensen
715 Crrarrt Street
Port Townsend, WA 98368
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Everett Sorensen
Wetland Delineation and Categorization
Parcels 9597 01401, 9597 01403, 959701 50 I
July/August 2019
Table of Contents
Introduction
Proposed Proiect
Site Description and Existing Conditions
Methodology
Background Information
Wetland Delineation Findings
Soils
Vegetation
Hydrology
Wetland Analysis and Critical Area Review
Categortzation and Buffers
Habitat and Species Assessment
Watershed and Hydrologic Assessment
Potential Impact of Proposed Development
Limitations
Summary
References
Figure I
Figure 2
Figure 3
Figure 4
Appendix
Location, Critical Area (City of Port Townsend)o Soils, and Elevations
F'indings
Photographs
I KM Polygon for Rating Form
Applied Methodology
Wetland Rating Field Data Form
Data Forms, Routine Determination, WA Wetland Rating System (DOE)
Everett Sorensen
Wetland Delineation and Categori zation
Parcels 9597 0140t, 9597 01403, 95970 I 501
July/August 2019
Introduction
Olympic Wetland Resources, LLC has been authorized by Everett Sorenson to perform a Wetland
netniation for the undeveloped parcels south of 33'd Street and east of Gibbs Street, Port Townsend,
Washington. The project consists of 3 parcels and is bisected by Katherine Street. Field work was
conducted on July 8th and August 7,2019 to determine the presence of wetlands, wetland rating, and
potential buffer restriction to proposed building envelopes.
Several subsequent updates in the rating system and City of Port Townsend Critical Area Code (May
201S) will regulate all wetlands no matter how small. Previous to the Code update wetlands under 1,000
sqft were exempt.
19.05.1 l0 (B. 4d) Category IV wetlands have the lowest levels of functions (scores less than 16 points) and are often
heavily disturbed. These are wetlands that are capable of being replaced, and in some cases improved. However,
experience has shown that replacement cannot be guaranteed in any specific case. These wetlands may provide some
important functions, and should be protected'
Project Proposal
The project includes the development of utilities to all parcels down the undeveloped portion of Kathrine
Street that runs between parcel 959701501 to the east and parcels 959701401and 95940140 to the west.
The parcels are in the planning phase to determine potential site location for single family homes in
relationship to the critical areas and buffer restrictions.
Site Description and Existing Conditions
o Legal Description: Parcels 959701401,959701403,959701501 Lots 13 and 14
Section 4 Township 4N Range lW
o Watershed: Basin 4,5,9 CityofPortTownsend, WRA17 SubBasin2014 QuimperPeninsula
r Soils: CmC Clallam gravelly sandy loam and TnC Townsend gravelly loam 0'15% slopes
o Location: South of 33'd Street and East of Gibbs Street.
This flat site is at the top of Basins 4o 5, and 9. No wetlands are indicated on the City of Port Townsend
Critical Areas map on any of these parcels, however wetlands are recorded within % mile. Wetland
vegetation has been identified along a ditch adjacent to the access driveway that was once an old logging
road from 2004. The wetland was identified by obligate vegetation and facultative vegetation dominating
the area.
Sorensen Wetland Delineation
Report File #20 l9-0710
The three parcels site is level in topography and consists of cleared areas for trails, parking areas, and, a
small garden shed near a proposed homesite on parcel 95970l50L The site consists of a dense understory
of young native trees and shrubs under 3'd growth Douglas firs.
1 July/August 2019
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The following Figures are located at the end of this report:
Figure 1: Location, Critical Atea, Soils, and Elevations
Figure 2: Findings
Figure 3: Photographs
Figure 4: lKM Polygon for Rating Form.
Methodology
Methodology used for this delineation and buffer categorization include the May 2018 update ofthe Port
Townsend Municipal Code and current state and federal jurisdictions. The characteristics of an area that
result in its classification as "wetland" have been formally defined by federal and state agencies. Al1
wetland delineations must be prepared in accordance with the U.S. Army Corps of Engineers Regional
Supplement to the Corps of Engineers Wetland Delineation Manual: Western Mountains, Valleys, and
Coast Region, Version 2.0 (MaY 2010
Background Information
The following resources were consulted prior to field work for this project:
o City of Port Townsend Municipal Code. Title 19 Environmental Protection Chapter 19.05 Critical
Areas (19.05) May 21,2018
o Clty of Port Townsend Critical Areas Map (2016)
o Aerial Photographs (Google lntemet)
o Soil Survey (https://websoilsurvey.sc.egov.usda.gov/App/tlomePage.htm)
o Washinglon State Wetland Identification and Delineation Manual (1997)
o National List ofPlant Species That Occur in Wetlands: Northwest (Region 9) (2019)
Wetland Delineation Findings
A small -660 sqft wetland was identified along the access driveway (logging road) east of Cliff Street and
on Parcel 959701401at the top of Basin 4. The Findings Map (Figure 2) includes property boundaries,
delineated wetland edge, associated buffers, and data point locations overlaid on a site plan prepared by
Everett Sorensen, PE. This small wetland is defined by a slight drop in topography potentially caused by
road construction. Once the wetland boundary was established it was flagged at l0 foot intervals (A1-
A4).
The wetland edge was determined by examining soils (redoximorphic features), vegetation layers
(Obligate and Facultative wetland vegetation), and hydrology. Wetlands are often located in the glacial
soils of the Clallam soil types throughout Port Townsend due to the lateral movement of stormwater on
the compact glacial cement layer. This delineation was conducted in July/August after below average
rainfall in the spring and summer and hydrology was not present. To confirm hydrology a wet season
evaluation could be done in the early spring months.
Soils
NRCS Soil Survey (internet) lists all soils on the parcels as CmC Clallam gravelly sandy loam and TnC
Townsend gravelly loam. Finding were relatively consistent with this soil description.
The Soil matrix color in Data Point I (DP 1) was dark greyish brown (Munsell soil color 10YR 312)wtth
redoximorphic features in the lower parts (1OYR 416). The vegetation layer was dominated by upland plant
communities in all vegetation layers.
Sorensen Wetland Delineation
Report File #2019-0710 2 July/August 2019
Data Point 2 (DP 2) was adjacent to the access driveway and consisted of matrix dark gray brown
(Munsell 10yR 4l2abovesoilscolors 10YR 5l2andredoximorphic 10YR4i6). Thisdatapointiswithinthe
wetland supported by the dominance of wetland vegetation in all plant communities.
Soils in Data Point 3 (DP 3) conesponded with findings in DP 1. and were dry and is also dominated by
upland vegetation. Redoximorphic features were observed in all data points under 2'7 inches below the top
layer and above the cement layer (photograph Figure 3).
Vegetation
The majority of the three parcels are dominated by upland vegetation unable to tolerate regular saturated
conditions. The plant community is dominated by an overstory of Douglas fir, Madrone, and red cedal
with a very dense understory of salal, oceanspray and bracken fern. Scouler's willow is scattered in both
upland wetland sites.
The small wetland had over 90Yo wefiland vegetation in a plant community that included slough sedge,
Nootka rose, spirea, and willow. Below is a list of vegetation identified on the three parcels.
Scientific Name Common name Status
Agrostis capillaris Colonial bentgrass FAC
Alnus rubra Alder FAC
Arbuttts menziesii Madrona NI
Arctostaohvlos colunbi ana Bristly manzanita NI
Bellardia viscosa Yellow oarentucellia FAC
Carex Sloush sedee OBL
Gaultheria shallon Salal FACU
Holodisctrs discolor Ocean-sorav FACU
Juncus effusus Soft rush FACW
Mahonia nerrosa Dull Oreson erape FACU
Malus fusca Western crabapple FACW
Oemleria cerasiformis Indian plum FACU
Pseudolsusa menziesii Douglas'fir FACU
Pteridium aqulinum Bracken fern FACU
Rosa nutkana Nootka rose FAC
Rubus bifrons Himalayan blackberry FAC
Rubus tu'sinus Trailins blackberrv FACU
Salix scouleriana Scouler willow FAC
Spiraea dottelasii Hardhack FACW
Thtia plicata Western red cedar FAC
UPL Upland Species
FACU Facultative Upland Species
FAC FacultativeSpecies
FACW Facultative Wetland Species
OBL Obligate Wetland Species
NI No Indicator Assigned
NWPL 2018 Coros of Eneineers. WA State
Sorensen Wetland Delineation
Report File #2019-0710 J July/August 2019
Hydrology
Hydrology was not present even within the wetland data point which is common this time of year.
Hydrology can be assumed where obligate and facultative vegetation are identified. The majority of the
thr.ee parcels are dominated by upland vegetation. It is common in disturbed or excavated areas for
stormwater to flow laterally and create ponding during the wet season.
Wetland Analysis and Critical Areas Review
Categori zation a nd Buffers
The standard buffer width for a delineated Category IV Wetlands for parcels under 1 acre is 50' as
highlighted in the table below. The wetland was categorized using the standard wetland analysis that
examines Water Quality, Hydrologic Function, and Habitat features. The Wetland Rating Form is
included in the Appendix at the end of this report.
A single-family residence is considered "high impact land-use'o when it is on a parcel smaller than one
acre. The rating for Improving Water Quality is 4 points, Hydrologic Function 4 points, and Habitat 3
points (total of l1 points). All buffers are measured perpendicular from the delineated edge.
Habitat and Species Assessment
Washington Department of Fish and Wildlife Priority Habitat and Species were evaluated within 1i3 of a
mile of this parcel. All threatened or endangered plant or animal species were recorded and if possible
surveyed during the October 2018 assessment. The only listing is Freshwater Emergent Wetlands near
this parcel.
Watershed and Hydrologic Assessment
Since these parcels are at the top of 3 basins as defined by the City of Port Townsend all water will drain
downslope. The small wetland is within Basin 4 where many wetlands are identified. Since there is no
outlet there is no chance of downslope flooding. It is in the WRA Quimper Peninsula Sub Basin 2014
wRrA #17.
Sorensen Wetland Delineation
Report File #2019-0710 4
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Potential Impact of Proposed Development
Cunently only utilities are proposed to the site. Large trees along the undeveloped Katherine Street will
be avoided as much a possible when installing water, sewer and other utilities. Short-term impacts during
the installation of the utilities will be minimized by careful construction practices.
All proposed construction will be located outside the 50' buffer of the delineated wetland. There will be
"No Net Loss" of any ecological functions during or after construction. Due to the flat landscape there
will be no potential for erosion or siltation to the wetland. Best Management Practices (BMPs) should be
followed during and after construction. There will be no alteration of surface water flows since the site is
well drained and final contours should follow the original landscape.
Limitations
The final authority over approval of this Wetland Delineation and Categorization will be the City of Port
Townsend Development Services Department. Final jurisdictional authority over wetland, shorelineo and
buffer determinations rests with the local, state and federal agencies. If there are further questions or
planning requirements for this project, please do not hesitate to call.
Summary
A 660 sqft wetland was categorized and delineated in July/August 2019 to determine development
restrictions for the installation of utilities (down the undeveloped portion of Katherine Street) and the
construction of homes on the undeveloped parcels owned by Everett Sorensen. The parcels are transected
by social trails and contained cleared areas for easy assessment of potential wetland conditions. The only
wetland identified was a ditch associated with the current access driveway off of Cliff Street. This was
once a logging road constructed in 2004 and potentially contributed to the soil disturbance and water
accumulation for this small wetland.
Wetland soils were identified throughout the site as indicated by redoximorphic features below the top
layer of soil from 2to 7 inches within the soil test pits. The only area with a dominance of wetland
vegetation was along the driveway and was delineated and flagged. It qualifies as a Category IV wetland
with 50 foot buffers.
Respectfully Submitted,L
Dixie Llewellin dixie@cablespeed.com
Principal Biologist, Olympic Wetland Resources, LLC
Certified for Wetland Delineation, WTI
Certified for Wetland Rating and Soil Analysis DOE, 2007,2012,2014
Sorensen Wetland Delineation
Report File#2019-0710 5 July/August 2019
Title:
Location, Critical Areas, Soils, and Elevations
Parcel 95907 010401,9597 01403, 95970 I 50 I
Port Townsend, WA 98368
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Elevations and Soils
33rd St (undeveloped)
Basin 5
Basin 9
City of Port Townsend Critical Area Map
March 2016 Green is Wetland
Red Lines are Basin Boundaries
Cmc Clallam gravelly sandy loam 0-15% Slopes
TnC Townsend gravelly loam 0-t5% Slopes
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Site Location
Scale:
As Indicated
Date:
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Job #:
2019- 0710
Figure
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Everett Sorensen
715 Grant Street
Port Townsend, WA 98368
Client:
0lympic Welland Resources, LLC
856 50Ur Slreet
Port Toumssnd, WA 98368
360 385-6432
dixie@cablespeed,com
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856 50lh Street
Port Townsend, WA 9B3E8
360 385.6432
dixie@cablespeed,com
Scale:
As Indicated
Figure
2
Client:Everett Sorensen
715 Grant Street
Port Townsend, WA 98368
Date:
July/August
20t9
Job #:
2019- 0710
Title:
Findings
Parcel 95907 010401,9597 01403, 95970 1 50 1
Port Townsend, WA 98368
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Photographs
Parcel 95907 010401,9597 01403, 95970 I 50 I
Port Townsend, WA 98368
Dense Salal in Upland
Typical Hydric Soil Found in
Upland and Wetland Data Points
Delineated Roadside Wetland
Upland Vegetation Directly
Behind Roadside Wetland
Olympic Wetland Resources, LLC
856 50th Steet
Port Townsend, WA 9836B
360385.M32
dixie@cablespeed,com
\
Scale:
As Indicated
Figure
3
Client:Everett Sorensen
715 Grant Street
Port Townsend, WA 98368
Date:
July 2019
Job #:
20t9- 07t0
Title:IKM Polygon for Rating Form
Parcel 95907 010401,9597 A1403, 95970 1 50
Port Townsend, WA 98368
10lympic Wetland Resources, LLC
856 50th Steet
Port Townsend, WA 98368
360 385-6432
dixie@cablespeed.com
Scale:
As Indicated
Figure
4
Client:Everett Sorensen
715 Grant Street
Port Townsend, WA 98368
Date:
July 2019
Job #:
2019- 0710
Undeveloped lJ -5%
Low Intensity Land Use L (open or agricultural land) -25%
Moderate Intensity Land Use [/ (less than one dwelling unit/acre) -20%
High Intensity Land Use H (more than one dwelling unit/acre) -50%
Applied Methodology for Wetland Delineation
City of Port Townsend
2018
PTMC 19.05.020 o'Wetland edge" means the boundary of a wetland as delineated based on the definitions
contained in the Washington State Wetland Identification and Delineation Manual (Ecology publication No. 96-
94, adopted under WAC 173-22-080). The characteristics of anareathatresult in its classification as "wetland"
have been formally defined by federal and state agencies. All wetland delineations must be prepared in
accordance with the U.S. Army Corps of Engineers Regional Supplement to the Corps of Engineers Wreiland
Delineation Manual: Western Mountains, Valleys, and Coast Region, Version 2.0 (May 2010).
The wetland delineation report will include how the wetland boundary was determined and include a map of the
delineated wetland, data sheets, and descriptions of site characteristics in both upland andwetland. The
methodology outlined in the Corps Manual is based upon three essential characteristics of wetlands: (l)
hydrophytic vegetation; (2) hydric soils; and (3) wetland hydrology. Field indicators of these three
characteristics must all be present in order to determine that an area is a wetland (unless problem areas or
atypical situations are encountered). All wetlands identified using this methodology may be regulated regardless
of size.
Determining Wetland Edges
Wetland edges were determined by establishing pairs of data points. ln general, the wetland edge falls between the
sampling plot with all three positive wetland requirements and where one or all ofthe requirements were not
present. Other difficult situations encountered in identi$ing wetlands are described in greater detail in the Corps
Regional Supplement.
Hy drop hytic Vegetatio n
Hydrophytic vegetation decisions are based on cornmunities of species that tolerate prolonged inundation or soil
saturation during the growing season. Vegetation sampling will follow the guidance outlined in the Corps
Manual. Several methods can be applied; however one method includes recording vegetation of a sampling
point to determine if more than 50o/o of the dominant species have a wetland indicator status of OBL, FACW, or
FAC. Dominance of plant species is determined by calculating actual aerial cover within an appropriate radius for
trees, shrubs, and herbaceous species at each data point. Commonly occurring plant species have been rated by the
U.S. Army Corps of Engineers National Wetland Plant List (NWPL). 2014 COE Western Mountains. Vallq)s, and
Coast. During the fieldwork, each species was recorded and given a rating based on indicator status and percent
cover. The2014 NWPL will be used in any wetland delineations or determinations performed after May 1,
2014.
Key to Wetland Indicator Status codes - Northwest Region (Source: USFWS, 1988, 1993):
OBL Obligate: species that almost always occur in wetlands under natural conditions (est. probability >gg%).
FACW Facultative wetland: species that usually occur in wetlands (est. probability 67 to 99%o), but are
occasionally found in non-wetlands.
FAC Facultative: species that are equally likely to occur in wetlands or non-wetlandS (est. probability 34 to
66%).
FACU Facultative upland: species that usually occur in non-wetlands (est. probability 67 to 99Yo), but are
occasionally found in wetlands.
UPL Upland: species that almost always occur in non-wetlands under normal conditions (est. probability
>99o/o).
Hydric Soil
A hydric soil is a soil that forms under conditions of saturation, flooding, or ponding lasting long enough during
the growing season to result in an anaerobic upper layer (USDA-NRCS 1995). Hydric soils favor the growth and
regeneration ofhydrophytic vegetation. The Natural Resources Conservation Service (NRCS), in cooperation
with the National Technical Committee for Hydric Soils, has compiled lists of hydric soils. It is common,
however, for a map unit of non-wetland (non-hydric) soil to have inclusions of hydric.soil, and vice versa.
Therefore, field examination of soil conditions is important to determine if hydric soil conditions exist.
In general, anaerobic conditions create certain characteristics irihydric soils, collectivply known as
"redoximorphic features" and include low chrom4 depletions, gleying, sulfidic material (rotten egg odor) and/or
high organic content within the soil immediately below the A-horizon. Holes were dug on the site and soil colors
were described by texture, color name, value, and chroma (Munsell Color 2000). Soils were categorized in
accordancewithNRCs FieldlndicatorsofHydricsoilsoftheUnitedStates(VersionT.0,20l0withupdates).
This manual further defines organic soils, sandy soils, loamy and clayey soils with anumeric value.
.,. Wetland Hydrology
Water must be present in order for wetlands to exist; however, it need not be present throughout the entire year.
The standard requires 14 or more consecutive days of flooding, or ponding or a water table 12" or less below
the soil surface during the growing season. The growing season has begun when two or more different non-
evergreen vascular plants are identified.
Indicators of hydrology may include, but are not necessarily limited to, ponded water, drainage pattems, drift lines,
sediment deposition, historic records, water'stained leaves, cracking of the soil surface, oxidized root channels,
and/or sediment deposits. The Regional Supplements provide methods for evaluating situations in wetlands that
periodically lack indicators of wetland hydrology but where hydric soils and hydrophytic vegetation are present
Categorization
Wetland categoization is determined using the Washington State Department of Ecologt (DOE) Wetland Rating
System Revised (Ecologt Publication#14-06-029, Effective January 2015 and as amended), according to type and
category of wetland. The wetland is assigned a score of High, Medium, or Low for wetland values; including water
quality frrnction, hydrologic firnction, andhabitat function. The total rating determines the category of wetland.
Wetlands are rated as entire systems and quite often exceed project boundaries. Ratings range from Category I to
Category IV. Bufferb are assigned according to intensity of land use for specific parcel size using final numeric
scores. Category I indicates wetlands with the highest quality of function for improving water qualrty, preventing
flooding problems, and providing habitat. These are not replaceable and therefore receive the largest bufler and
highest protection.
Classification
Two classification systems are commonly used to describe wetlands. The hydrogeomorphic (HGM) system
describes wetlands,in terms of their position in the landscape and the movement of water in the wetland
(Brinson, 1993). The U.S. Fish and Wildlife Service classification system (Cowardin et al., 1979) describes
wetlands in terms of their vegetation communities; for example, emergent (PEM), scrub-(PSS) shrub, and
forested (PFO) community tYPes.
Wetland name or number
RATING SUMMARY - Western Washington
Name of wetland (or tD #): AJte};Tf gOBatFU Date of site visit: il d A ,
nateuovD,fuuod4,Trainedbyrcology{ves-NoDateoftr.aining0lzDlt
HGMClassusedforratingDtM't-WetlandhasmultipleHGMclasses?-Yvz1
NOTE: Form is not complete wlthout the figures requested (figures can be combined).
Source of base aerial photo/maP
OVERALL WETTAND CATEGORY (based on functions- or special characteristics-)
1. Category of wetland based on FUNCTIONS
-Category
l-Total score = 23 -27
-Category
ll-Total score = 20 -22
-Category
lll-Total score = 16 - 19
^-{. category lV - Total score = 9 - 15--
2. Category based on SPECIAL CHARACTERISTICS of wetland
CHARACTERISTIC CATEGORY
Estuarine III
Wetland of High Conservation Value I
Bog I
Mature Forest I
Old Growth Forest I
Coastal Lagoon I II
lnterdunal III M W
None of the above
Wetland Rating System for Western WA:2074 Update
Rating Form - Effective |anuary t,20Ls
Score for each
function based
on three
ratinss
(orde7 of rotings
is not
importont)
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 = MrLrL
3 = L,L,L
I
FUNCIION lmprovlng
Water Quallty
Hydrologlc Habltet
Circle the approprlate ratings
Site Potential H M6)H M@'H M (D'
Landscape Potential H @)L H @, 1 H M(9
Value H M62 H Mp H MV TOTAT
Score Based on
Ratings t +5 tl
D 1.0. Does the site have the potentlal to improve water quallty?
3D 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
Wegand 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
flowi ditch.ESTION 7 on whose outlet is aWetland is a flat ints = 1an o1,2.Thesoil2inbelo@istrueclayortrueorganic/useNRCS definitions).Yes = 4 No'= 0D
,l
D 1.3. Characteristics and distribution of persistent olants (Emergent, Scrub-shrub, and/or Forested Cowardin classes
Wetland has persistent, ungrazed, plants > 95%of area
Wetland has persistent, ungrazed, plants > /, of area
Wetland has persistent, ungrazed plants > rf toof area
Wetland has persistent, ungrazed plants <1/16 of area
points = 5
points = 3
points = 1
points = 0
)
4
D 1.4. Characteristics of seasonal oondins or inundation:
This is the area that is ponded for ot ledst 2 months. See description in manuol.
Area seasonally ponded is > % total area of wetland
Area seasonally ponded is > % total area of wetland
Area onded is <%total area of wetland =!
points = 4
points = 2
fAdd the in the boxes aboveTotal for D 1
Wetland name or number
Rating of Site Potential lf score is:-12'16 = H
-6-Xl
= M = f. Record the rating on the first page
Rating of Landscape Potential lf score is:-3 or 4 = H or 2 = M _0 = L Record the rating on the first pdge
Rating of Value lf score is:-2-4 = H
-X
= M Record the rating on the first pdge
Wetland Rating System for Western Wk 2074 Update
Rating Form - Effective January 1,2075
r/l
L
5
D 2.0. Does the landscape have the to support the water qualitv functlon of the site?
ID 2.1. Does the wetland unit receive stormwater dlscharges?Yes=1 No=0
aD 2.2.1s > 10% of the area within 150 ft of the wetland in land uses that generate pollutants? Yes = 1 No = 0
oD 2.3. Are there septic systems within 250 ft of the wetland?Yes=1 No=0
oD 2.4, Are there other sources of pollutants comlng into the wetland that are not listed in questions D 2.1-D 2'3?
Yes=1 No=0
tlAdd the points in the boxes aboveTotal for D 2
D 3.0. ls the water quality lmprovement provlded by the site valuable to soclety?
oD 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=O
oD 3.2. ls the wetland in a basin or sub-basin where an aquatic resource is on the 303(Yes=1 No=0list?
oD 3.3. Has the site been identified in a watershed or local plan as important for maintaining water quality (answer YES
Yes=2 No=O?the basin in which the unit isif there is o oAdd the points in the boxes aboveTotal for D 3
=l
D 4.0. Does the site have the potentlalto reduce floodlng and eroslon?
+
D 4,1, Characteristlcs 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
Llsitchdpointson7whoseoutletWetlandsatflresstonESTIONflowingpermanentlykev),(qudep
0owtflusoutlrfacethatettssoruannncohWetlandas
o
D 4.2, Depth of storaee durine wet periodsr Estimate the height of ponding above the bottom of the outlet. For wetlands
with no outlet, measure from the surface of permanent woter or if dry, the deepest part.
Marks of ponding are 3 ft or more above the surface or bottom of outlet
Marks of ponding between 2 ft to < 3 ft from surface or bottom of outlet
Marks are at least 0,5 ft to < 2 ft from surface or bottom of outlet
The wetland is a "headwater" wetland
Wetland ls flat but has small depressions on the surface that trap water
Points = 7
Points = 5
Points = 3
Points = 3
Points = 1
Pollts = 0tvtarki of ponding less than 0.5 ft (6 in)
,o
D 4.3. Contribution of the wetland to storaee in the watershed : Estimate the ratio of the area of upstream bosin
contributing surface wdter 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
The area of the basin is 10 to 100 times the area of the unit
The area of the basin is more than 100 times the a'rea of the unit
Entire wetland is in the Flats class
V#htt
nts=5
points = 5
points = 3
points = 0
+Add the points in the boxes aboveTotal for D 4
Wetland name or number
Rating of Site Potential lf score is:-12'16 = H
-6-11
= M =l
Rating of landscape Potential lf score is: 3 = H or2=M
-0=L
Record the rating on the first page
L
rA
Record the rating on the lirst poge
{
0-
Ratingofvaluelfscorels: 2'4=H
-1=M
=L
Wetland Rating System for Western W/e20L4 Update
Rating Form - Effective Januaryl, 2015
Record the rating on the first page
6
D 5.0. Does the landscape have the potentlal to hvdrologlc functions of the slte?
ID 5.1, Does the wetland receive stormwater discharges?Yes=1 No=0
oD 5.2. ls >10% of the area within 150 ft of the wetland in land uses that generate excess Yes=1 No=0runoff?
oD 5.3, ls more than 25% of the contributing basin of the wetland covered
>1 residence/ac, urban, commercial, agriculture, etc.)?
with intenslve human land uses (residential at
Yes=1 No=0
(Add the polnts ln the boxes aboveTotal for D 5
D 6.0. Are the hydrologlc functlons provlded bv the site valuable to soclety?
t'o
D 6.1. The unit is in a landscape that has floodine problems , Choose the descriptian that best matches conditions around
the wetland unit belng rated. Do not add points. Choose-the hiahest 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):
r Flooding occurs in a sub-basin that is immediately down-gradient of unit. points = 2
o Surface flooding problems are ln a sub-basin farther down-gradient. points = 1
Flooding from groundwater is an lssue in the sub-basln. polnts = 1
The exlstlng gr potentlal outflow from the wetland is so constrained by human or natural conditlons that the
waterstoredbythewetlandcannotreachareasthatflood'ExplolnWhy-points=0
There are no problems with floodlng downstream of the wetland. points = 0
oD 6.2, Has the slte been identified as important for flood storage or flood conveyance in a regional fl ood control plan?
Yes=2 No=0 nTotal for D 5 Add the points ln the boxes above
Wetland name or number
Wetland Rating System for Western W At 20!4 Update
Rating Form - Effective January 7,20L5
These questlons apply to wetlands of all HGM classes.
HABITAT FUNCIIONS - lndicators that site functions to portant habitat
H 1,0. Does the site have the potentialto provide habitat?
H 1.1, Structure of plant community: lndicators are Cowardin classes and strota within the Forested c/oss. Check the
Cowardin plant classes in the wetlan d. lJp to 10 patches may be combined for each class to meet the threshold
of % ac or more than 70% 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
)L er"rg"nt 3 structures: points = 2
__Scrub-shrub (areas where shrubs have > 30% cover) 2 structures: points = 1
_Forested (areas where trees have > 30% cover) l structure: points = 0
lf the unit has a Forested class, check if:
The Forested class has 3 out of 5 strata (canopy, sub-canopy, shrubs, herbaceous, moss/Sround-cover)
that each cover20/o within the Forested polygon
o
H 1.2. Hydroperiods
Check the types of water regimes (hydroperiods) present within the wetland, The water regime has to cover
more than I0% of lhe wetland or % ac to count (see text for descriptions of hydroperiodsl,
_Permanently flooded or inundated 4 or more types present: points = 3
_ Seasonally flooded or inundated 3 types present: points = 2
{ Occasionally flooded or inundated 2 types present: points = 1
-saturated
only l type present: points = 0
-Permanently
flowing stream or river in, or adjacent to, the wetland
-seasonally
flowing stream in, or adjacent to, the wetland
-!ake
Fringe wetland 2 Points
Freshwater tidal wetland 2 Points
o
H 1.3, Richness of plant sPecies
Count the number of plant species in the wetland that cover at least L0 ft2.
Different patches of the same species can be combined to meet the size threshold and you do not have to nome
the species, Do not include Euraslan milfoll, reed canarygrass, purple loosestrife, Conodian thistle
lf you counted: > 19 species Points : 2
5 - 19 species Points = 1
< 5 species points = 0
o
H 1.4, lnterspersion 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. lf you
hove four or more plant classes or three c/osses and open water, the roting is always high,
None = 0 points Low = 1 point Modeiate = 2 points
All three diagrams
in this row
are HIGH = 3points
I
13
I
H 1.5, Special habitatfeatures:
Check the habitat features that are present in the wetlan d, The number of checks ls the number of polnts'
-Large,
downed, woody debris within the wetland (> 4ln diameter and 6 ft long).
Standing snags (dbh > 4 in)wlthin the wetland
_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 leist 33 ft (10 m)
_stable steep banks of fine material that might be used by beaver or muskrbt for denning (> 30 degree
slope) OR signs of recent beaver activlty are present (cut shrubs or trees thqt hqve not yet weuthered
where wood ls exPosed)
_At least/a ac of thin-stemmed persistent plants or woody branches are present in areas that are
permanently or seasonally inundated (structures for egg-laylng by omphibians)
* lnvasive plants cover less than 25% of thewetland area in every stratum of plants (see H 7.7for list of
aa-Add the points ln the boxes aboveTotal for H 1
Wetland name or number
Rating of Slte Potential lf score is:-15'18 = H
-7'14
= M =L
Ratlng of Landscape Potentlal lf score is:-4'5 = H
-1-3
= M 1=L
RatlngofValue lf score is:-z= H
-1
= M =L
Wetland Rating System for Western WAz 20L4 Update
Rating Form - Effective fanuary l,20Ls
+l
Record the ratlng on the flrst poge
Record the ratlng on the flrst poge
V
L
L
Record the rating on the flrst poge
14
H 2.0. Does the landscape have the potential to support the habitat functlons of the site?
3
H 2.1. Accessible habitat (include only habitat that directly abuts wetlqnd unitl.- -' ;brtr;r; ib % undisturbed habitat:lfu [(l moderate and low intensity land uses)/2] Z5= -ZE:t"
lf total accesslble habitat is:
>'/, (gg,g%l of 1 km Polygon 1. points = 3
20-33% of 1 km Polygon Polnts = 2
L}-13%of 1 km Polygon Polnts = I'
<t0%of tkm nts=0
I
H 2.2. Undlsturbed habltat ln 1 km Polygon aroun{ the wetland.
Calculate: I O %undlsturbed habitat fr + [(% moderate and low lntensity land usesl/ZIQO = fr1 o/o
Undlsturbed habltat > 50% of Polygon points = 3
Undisturbed habitat LO-50% and in 1-3 patches polnts = 2
Undisturbed habitat 10-50% and > 3 patches points = 1
Undisturbed habitat < L0% of tkm =Q
H 2.3. Land use intensity in 1 km Polygon: lf
> 50% of 1 km Polygon is high intensity land use points = (- 2)
Points = 0< 50% of 1 km Polygon is high intensity
ITotal for H 2 Add the in the boxes above
H 3.0. ls the habitat provlded by the site valuable to soclety?
2
H 3.1. Does the site provide habltat for specles valued ln laws, regulations, or policles? Choose only the highest score
that applies to the wetland belng roted,
Site meets ANY of the following criteria: polnts = 2
- lt has 3 or more priority habitats withln 100 m (see next page)
- lt provides habitat for Threatened or Endangered species (any plant or animal on the state or federal lists)
- lt ls mapped as a location for an indlvidual WDFW priority species
- lt is a Wetland of High Conservation Value as determined by the Department of Natural Resources
- lt 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 L00 m points = 1
Site does not meet anv of the criterla above ooints = 0
WETLAND DETERMINATION DATA FORM -Western Mountains, Valleys, and Goast Region
Project/Site:Parc,els 959701401,959701403, 959701501 Clty/County:Port Townsend Sampling a26' 718119
ApplicanUOwner:Evereft Sorensen State; WA Sampling Point:DP #1
lnvestigator(s):D Llewellin, OlympicWetland Resources, LLC Seclion, Township, Range:s4T30R1W
Landform (hillslope, terrace, etc.):depression Local relief (concave, convex, none):none Slope (%): 0 to 8%
Subregion (LRR):Mountain Valley Coast s61. 48.125 Long:-122.80 Datum: _
Soil Map Unit Name:CmC Clallam sandy gravelly loam, TnC Townsend gravelly loam NW classmcation:none
Are cllmatic / hydrologic condilions on lhe site typical for this lime of year? Yes X No
-
(lf no, explain ln Remarks.)
AreVegetation-,Soll
-,orHydrology-signlflcantlydisturbed?
Are"Normal Circumstances"presenl? Yes X No-
Are Vegetation _, Soll _, or Hydrology
-
naturally problemalic? (lf needed, explain any answers in Remarks.)
SUMMARY OF FINDINGS - Attach site map showing sampllng point locations, transects, important features, etc.
Hydrophytic Vegetation Present?
Hydric Soil Present?
Welland Hydrology Present?
Yes
Yes
Yes
No
No
No
X
X
x
ls the Sampled Area
wlthin a Wetland?Yes_ No X
Remarks:
Hydrology is often absent this time of year. Area re to have standing water in winter.
VEGETATION - Use scientific names of plants.
Tree Stratum (Plot size:
Absolule Dominant lndicator
o/o Cover Soecies? Status
10 no FACSalix scouleriana
2,Thuia plicata 4A yes FAC
50 yes FACU
100%
3.Pseudotsuga menziesii
4.
= Total Cover
10 yes FACU
Saolinq/Shrub Stratum (Plot size:)
1.
2.
3,
4.
5.
Holodiscus discolor
Galtheria shallon 45 yes FACU
Herb Stratum (Plot size:
55o/o =Total Cover
65 yes FACU
15 no FACU
Pteridium aquilinum't.
2.
3.
4.
5.
6.
7.
8.
9.
Rubus ursinus
10.
11.80% = Total Cover
Woodv Vlne Stratum (Plot size:
1
2
% Bare Ground in Herb Stratum
= Total Cover
Dominance Test workshoot:
Number of Dominant Species
That Are OBL, FACW or FAC:1 (A)
Total Number of Dominant
Species Across All Slrata:2 (B)
Percent of Dominant Species
That Are OBL, FACW or FAC:s0%(//B)
Prevalence lndex worksheet:
Total o/o Cover of:Multinlv bv:
OBL soecies
FACW specles
FAC species 2
FACU species 5
UPL species
x1=-
x2=_
x3= 6
x4=L-
x5=-
Column Tolals: 7 (A)26 (B)
Prevalence lndex = B/A = 3.71
Hydrophytlc Vogetatlon lndicators:
_ 1 - Rapid Test for Hydrophytic Vegetation
_ 2 - Dominance Test is >50%
-
3 - Prevalence lndexis 33.01
-
4 - Morphological Adaptationst (Provide supporting
data ln Remarks or on a separate sheet)
-
5 - Wetland Non-Vascular Plantsr
-
Probtemalic Hydrophylic Vegetalionr (Explaln)
rlndicators of hydric soil and wetland hydrology must
be present, unless disturbed or problematic.
Hydrophytlc
Vegetatlon
NoXPresent?Yes
Remarks:
Wetland vegetation is not dominant.
US Army Corps of Engineers Western Mountains, Valleys, and Coast - Version 2.0
sotL Sampling Point:
to the
Color lmolst\
CS=Covered or
of
7-16" 10YR 5/2 70% 10 YR 4/6
Grains. 2Localion:
Proflle
o/o Tvoet Loct Texture
Matrlx
indlcator or
Depth
finches)
o-7"
Color (molstl lo
1oYR 3/2
SODM
Redox Fealures
Hydrlc Soll lndlcators: (Appllcable to all
* Hislosol (Al)
-
Histic Epipedon (A2)
-
BlackHistic (A3)
_ Hydrogen Sulfide (A4)
X Depleted Below Dark Surface (A1 1)
_ Thick Dark Surface (A12)
__-: Sandy Mucky Mlneral (S1)
_ Sandy Gleyed Mairix (S4)
LRRS, unless othenivlse noted.)
_ SandyRedox (S5)
-
Stripped Maklx (36)
-
Loamy Mucky Mineral (F1) (except MLRA 1)
_ Loamy Gleyed Matrix (F2)
_ Depleled Malrix (F3)
_ Redox Dark Surface (F6)
-
Depleted Dark Surface (F7)
_ 2 cm Muck (A10)
_ Red Parent Material (TF2)
-
Very Shallow Dark Surface (TF12)
_ Other (Explain in Remarks)
lndlcators for Problematlc Hydric Sollss:
_ Redox Depressions
slndlcators of hydroph$ic vegetation and
wetland hydrology must be present,
unless disturbed or Problematic.
Hydric Soil Present? Yes X No
Restrlctive Layer (if Present):
Type:
-
Depth (inches):
Hydric soils are present at this site
HYDROLOGY
_ Surface Water (Al)
_ Hlgh Water Table (A2)
_ Saturation (A3)
-
Water Marks (B1)
-
Sediment Deposits (82)
_ Drift Deposits (83)
-
Algal Mat or Crust (84)
_ lron Deposits (85)
* Surface Soil Cracks (86)
-
lnundation Visible on Aerial lmagery (B7)
-
Sparsely Vegetated Concave Surface (88)
_ Water-Stained Leaves (BO) (except
MLRA 1, 2,4A, and 48)
_ Salt crust (811)
_ Aquatic lnvertebrates (813)
_ Hydrogen Sulfide Odor (Cl)
-
Oxidized Rhizospheres along Living Roots (C3)
! Pr"."n." of Reduced lron (C4)
_ Recent lron Reduction in Tllled Solls (C6)
_ Stunted or Stressed Plants (Dl) (LRR A)
_ Other (Explain ln Remarks)
SecondarLlndicators (2 or more reouired)
-
Water-Stained Leaves (BS) (MLRA 1,2,
4A, and 48)
_ Drainage Palterns (810)
_ Dry-Season Water Table (C2)
_ Saturation Visible on Aerial lmagery (Cg)
-
Geomorphic Posltlon (D2)
_ ShallowAquitard (D3)
_ FAO-NeutralTest(D5)
-
Raised Ant Mounds (D6) (LRR A)
_ Frost-Heave Hummocks (D7)
Primen lndiealnrs rm nf nne renr rlred' ehenk all lhat nnnlv\
lndlcators:
Wetland Hydrology Present? Yes ttoX .
Surface Water Present?
Water Table Preserit?
Saluration Present?
Yes- tto X Depth (inches):
Yes- No X Depth (inches):
Yes
-
No X Depth (inches):
ifDescribegauge,
During the dry month of July there is no hydrology present, however hydric soils were observed.
Western Mounlains, Valleys, and Coast - Version 2.0US Army Corps of Engineers
WETLAND DETERMTNATION DATA FORM -Western Mountains, valleys, and Goast Region
project/stte: Parcels959701401, 959701403, 959701501 city/county:Port Townsend Sampling Date:718119
DP#2
ApplicanUOwner:Everett Sorensen
tnvestigator(s): D Llewellin, Olympic Wetland Resources, LLC Section, Township, Range:s4T30R1W
Landform (hlllsloPe, tenace, etc'):depression Local relief (concave, convex, none):none Slope (o/o): 0 to 8%
Subregion (LRR):Mountain ValleY Coast y61' 48.125 Long:-122.80 Datum:
Soil Map Unit Name:CmC Clallam sandy gravelly loam, TnC Townsend gravellY loam NW classificalion:none
Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No
-
(lf no, explain in Remarks.)
Are Vegelation soil
-,
or Hydrology
-
significanily disturbed? Are "Normal Circumstances" present? Yes X No
-Are Vegetation Soil _, or Hydrology _ naturally problemalic? (lf needed, explain any answers in Remarks')
suMMARy OF FINDINGS - Attach site map showang sampling point locations, transects, important features, etc.
VEGETATION - Use scientific names of plants.
State' WA sampling Point:
ls the Sampled Area
wlthln a Wetland?XYes No-
Hydrophytic Vegetation Present?
Hydrlc Soil Presenl?
Wetland HydrologY Present?
Yes X No
Yes X No
Yes
-
No X
water in winter.to have standiis often absent this time of AreaH
Number of Dominant Species
That Are OBL, FACW or FAC:
Percent of Dominant Species
Thal Are OBL, FACW or FAC:
2 (A)
4 (B)
75%(A/B)
Test
Total Number of Dominant
Species Across All Strata:
oBL specles I
FACW species
FAC species 3-
FACU specles
UPL species
Column Totals: 7
Prevalence lndex = B/A
Multlolv bv:
x1= 1
x2=
-
x3= 9
x4= 12
x5=-
(A) 22 F)
= 3.14
nf'
Prevalence
Tolel o/"
-
1 - Rapid Tesl for Hydrophytic Vegetation
.f, 2 - Dominance Test is >50o/o
-[ 3 - Prevalence lndex ls 33.01
-
4 - Morphological Adaptationsr (Provide supporting
data in Remarks or on a separate sheet)
-
5 - Wetland Non-Vascular Plantsr
-
Problematic Hydrophytic Vegetalionr (Explain)
rlndlcators of hydric soil and wetland hydrology must
be presenl, unless dlsturbed or problematic.
Yes X
Hydrophytlc
Vegotatlon
NoPresent?
Saolino/Shrub Stratum (Plot size:
WoodvVine Stratum (Plot size:
ZO yes FAC
1.
2.
3.
4.
5.
Galtheria shallon
Rosa nukana
Rubus ursinus
= Total Cover
-=
Tolal Cover
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
Salix scouleriana
2.Alnus rubra
3.
4.
Carex obn
o/o Bare Ground in Herb Stratum
Holodiscus discolor
Herb Stratum (Plot size:
Tree Slratum (Plot size
Dominanl
-
= Total cover
35 yes FACU
45 yes FACU
20 no FAC
-
= Total Cover
95 yes OBL
5 no fnCU-
1.
2.
o/o Cover SDecies? Status
15 no FAC
Usino the dominance test and the hydrophytic vegetation indicators the area qu
as hiving hydrophytic vegetataion.
alifies
US Army Corps of Engineers Western Mountains, Valleys, and Coast - Version 2.0
Sampling Point:
--
SOIL
10 YR 4/6
Hard cement laYer below
PL=PoreCoated Sand
OI
1
Color
80% D M RockY gravelY loam
sandy loam
Texture
depth needed to
Depth
(inches)
o-2"
2-11" 10YR 6/2
Matrix
Color (molst) %
rcYn:4lz
-
Sandy Redox (S5)
-
Stripped Makix (56)
-
Loamy Mucky Mineral (Fl) (except MLRA 1)
-
Loamy GleYed Matrix (F2)
-
2cm Muck (A10)
-
Red Parent Material (TF2)
-
Very Shallow Dark Surface (TF12)
-
Other (Explain in Remarks)
Hydrlc Soll lndlcators: (Appllcable to all LRRs, unless otherwlse notod.)lndlcators for Problematlc Hydrlc
-
Redox DepressionsMatrix (S4)
3lndicators of hydrophytic vegetation and
welland hydrology must be present,
unless disturbed or Problematic.
_ Histosol (A1)
_ Hlstic Epipedon (A2)
_ Black"Hislic (A3)
_ Hydrogen Sullide (A4)
ll Depleted Below Dark Surface (A11)
-
Depleted Matrix (F3)
-
Redox Dark Surface (F6)
-
Depleted Dark Surface (F7)-
Thick Dark Surface (A12)
' Sandy Mucky Mineral (Sl)
Hydrlc Soll Pressnt? Ves!No
Layer
Type:Glacial compacted soil
11'Depth (inches):
laver below depteted matrix, redox features very abundant. Water travels laterally in this
soils type and will pond in disturbes or ditched areas'
Cement
Clallam
HYDROLOGY
-
Surface Water (Al)
-
High Water Table (A2)
_ Saturatlon (A3)
-
Water Marks (Bl)
-
Sediment Deposlts (82)
-
Driff Deposits (83)
-
Algal Mat or Crust (B4)
-
lron Deposits (B5)
-
Surface Soll Cracks (86)
-
lnundation Visible on Aerial lmagery (B7)
-
SparselyVegetated Concave Surface (B8)
-
Water-Stalned Leaves (Bg) (except
MLRA 1, 2,4A, and 48)
_ Salt Crust (811)
_ Aquatic lnvertebrates (813)
_ Hydrogen Sulflde odor (C1)
-
Oxidlzed Rhizospheres along Llving Roots (C3)
X Pr"."n." ofReduced lron (G4)
-
Recent lron Reduction ln Tilled Soils (c6)
-
Stunted or Slressed Plants (D1) (LRR A)
_ Other (Explain in Remarks)
Secondarv lndicators (2 or more reouired)
-
Water-Stained Leaves (89) (MLRA 1, 2,
4A, and 48)
_ Drainage Pafterns (810)
_ Dry-Season Water Table (C2)
-
Saturation Visible on Aerial lmagery (C9)
-
Geomorphic Position (D2)
_ ShallowAquitard (D3)
_ FAC-Neutral Test (D5)
-
Raised Ant Mounds (DO) (LRR A)
FrosbHeave Hummocks (D7)
Primarv rlrnd' nlreck all lhal/minlmilm rrf one
lndlcators:
Wetland HydrologY Prosent? Yes XNo
Surface Water Present?
Water Table Preserit?
Saturation Present?
Yes- No X Depth(inches):
Yes
-
No X Depth (inches):
Yes
-
No X DePth (inches):
Data (stream gauge,inspections),
was observed anywhere on site during the month of July. The main indicator of
wetland was OBL and FAC plants and hydric soils.
No surface water
the presence of a
US Army Corps of Englneers Western Mountalns, Valleys, and Coast - Version 2'0
.) /-)
WETLAND DETERMINATION DATA FORM -Western Mountalns, Valleys, and Coast Region
ProJect/Site:Parcels 959701401 959701403, 959701 501 City/County;Port Townsend Sampling Date:8nh9
Applicant/Owner:Everett Sorensen State: 14- Sampling p661. DP #3
lnvesligator(s):D Llewellin, OlympicWetland Resources, LLC Section, Township, Range:S4T3OR1W
Landform (hillslope, tenace, etc'):depression Local relief (concave, convex, none):none SloPe (o/o): 0 to 8%
Subregion (LRR)Mountain Valley Goast Lalr 48.125 Long:-122.80 Datum: _
Soll Map Unit Name:CmC Clallam sandY gravellY loam, TnC Townsend gravellY loam NW classificatlon:none
Are cllmatic / hydrologic conditions on the site typical for lhis time of year? Yes X No
-
(lf no, explain in Remarks.)
AreVegetation Soll
-,orHydrology-slgnificanllydisturbed?
Are"Normal Circumstances"present? Yes X No-
Are Vegeiation Soil _, or Hydrology
-
nalurally problematic? (lf needed, explain any answers in Remarks')
suMMARy OF FINDINGS - Attach site map showing sampling point locations, transects, important features, etc.
Hydrophytlc Vegetation Present?
Hydric Soil Present?
Wetland HydrologY Present?
Yes
Yes
Yes
No
No
No
X
X
X
ls the Samplod Area
wlthln a Wetland?Yes NoX
Remarks:
Hvdrologv is often absent this time of vear. Soiltest Pit dry at 16", soils rock hard'
VEGETATION - Use scientific names of plants.
Number of Dominant Species
That Are OBL, FACW or FAC:
Percent of Dominant Species
That Are OBL, FACW, or FAC:
(A)
2 (B)
0%(A/B)
Total Number of Dominant
Species Across All Strata:
Total o/o Cover of;
OBL species
FACWspecies
FAC species 2
FACU species
UPL species
Multiolv by:
x1=-
x2=
-
xg= l-x4=L
x5=-
(A) 26 (B)
Prevalence lndex = g/A = 3'71
Column Totals: 7
_ 1 - Rapld Test for Hydrophytic Vegetalion
_ 2 - Dominance Test is >50%
-
3 - Prevalence lndex is <3,01
-
4 - Morphological Adaptationsr (Provide supporting
data in Remarks or on a separate sheet)
-
5 - Wetland Non-Vascular Plantsl
-
Problematic Hydrophytic Vegetationr (Explain)
rlndicalors of hydric soil and welland hydrology must
be present, unless disturbed or problematic.
Hydrophytlc
Vegetatlon
YesProssnt?NoX
Salix scouleriana
Arbrt," m"nti"tii FACU
10
Galtheria shallon
Rhododendron macrophyllum
= Total Cover
3.Pseudotsuga menziesii
2.
4.
20 no
1.
2.
3.
4.
5.
100o/o = Total Cover
Total Cover
o/o Bare Ground in Herb Stratum
Holodiscus discolor
Herb Slratum (Plot size:
Woodv Vine Stratum (Plot size
% Cover Soecles? Slatus
10 no FAC
80 yes FACU
100o/o
= Tolal Cover
no FACU
85 . yes FACU
5 no FACU
Saplino/Shrub Stratum (Plol size:
Tree Slralum (Plot size: )
1.
2.
3.
4.
5.
6.
7.
8.
L
10.
11.
1
2
Wetland vegetation is not dominant.
US Army Corps of Engineers Western Mountains, Valleys, and Coast-Version 2'0
Sampllng Point:
--
solL
6-11 rcYR4l2 50% 10 YR 4/4 50 D M gravelly loam
Redox Fealures
Color /molsl\
or
Remarks
Gralns. 2location: PL=Pore
Profile Descrlptlon:
sandy loam
o/o Tvoet Loc' Texture
MatrixDepth
(lnches)
0-6"
Color (moist) Yo
10YR v2 1oO%
Hydric Soll lndlcators: (ApFllcable to all LRRs, unless otherwlse noted.)
* Histosol (A1) _ Sandy Redox (S5)
-
Histic Eplpedon (A2)
-
Stripped Matrlx (56)
-
Black Histic (A3)
-
Loamy Mucky Mineral (F1) (except MLRA l)
-
Hydrogen Sulfide (A4)
-
Loamy Gleyed Malrix (F2)
X Depleted Bdow Dark Surface (A1 1)
-
Depleled Matrix (F3)
-
Thick Dark Surface (A12)
-
Redox Dark Surface (F6)
- . Sandy Mucky Mlneral (S'l)
-
Depleted Dark Surface (F7)
_ Sandy Gleyed Matrix (S4)
-
Redox Depressions (F8)
lndlcators for Problematlc Hydric Solls3:
_ 2 cm Muck (A10)
-
Red Parent Material ClF2)
_ Very Shallow Dark Surface (TF12)
_ Other (Explain ln Remarks)
3lndicators of hydrophylic vegetation and
wetland hydrology must be present,
unless disturbed or problematic,
Hydrlc Soll Present? Yes X No
Type
Restrictlve Layer (lf present)
Depth (inches):
Hydric soils are present at this site above the cement hardpan layer.
Remarks
HYDROLOGY
_ Surface Water (Al)
_ Hlgh Water Table (A2)
_ Saturation (A3)
_ Water Marks (Bl)
_ Sediment Deposits (B2)
_ Ddfr Deposlts (83)
_ Algal Mat or Crust (84)
_ lron Deposits (85)
_ Surface Soil Cracks (86)
_ lnundailon Vislble on Aerial lmagery (87)
.- Sparsely Vegetated Concave Surface (88)
_ Water-Stalned Leaves (89) (except
MLRA 1, 2,44, and 4Bl
_ Salt Crust (811)
_ Aquatlc lnvertebrates (813)
-
Hydrogen Sulfide Odor (Cl)
_ Oxidlzed Rhizospheres along Living Roots (C3)
L Pr"."n."ofRoducedlron(C4)
_ Recent lron Reduction ln Tilled Solls (C6)
_ Slunted or Stressed Plants (D'l) (LRR A)
_ Olher (Explain in Remarks)
Secondarv lndicators {2 or more requiredl
_ Water-Stained Leaves (Bg) (MLRA 1, 2,
4A, and 4B)
_ Drainage Pattems (810)
_ Dry-Season Water Table (C2)
_ Saturation Msible on Aerial lmagery (C9)
_ Geomorphic Positlon (D2)
_ ShallowAquitard (D3)
_ FAC-Neutral Test (D5)
_ Raised Ant Mounds (D6) (LRR A)
_ Frost-Heave Hummocks (D7)
Primaru lndicators lminimum of one reouired: check all that aoDlv)
Surface Water Present?
WaterTable Present?
Saturalion Present?
Yes
-
fto X Depth (inches):
Yes
-
No X Depth (inches):
Yes- No X Depth(inches):
Fleld
Wetland Hydrology Present? Yes XNo
gauge, monitoring
During the dry month of July there is no hydrology present.
Western Mountains, Valleys, and Coast - Version 2.0US Army Corps of Engineers