HomeMy WebLinkAboutWetland Delineation 801201006
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Prepared for.
Raymond & Patti Snow
PO Box 586
Chimacum, WA 98325
Snow Wetland
Delineation Report
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April 5, 2007
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Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaeIB.Dawson@gmail.com
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Snow Delineation
April 5, 2007
p. 1 of 37
Table. of Contents
Introduction...................,.......................................,................... 3
Background.........,..................................................................... .3
Location.................,.........................................................,..,....................3. ,
Sources.....,.,...,.,...............,.............................,...,....................................3 ..
Mefuodology......,...............,..................................................... ... 5
Findings...............................,..........,....,........,............................ 5
General Wetland Conditions....................................................................,. 5.
Streams and Habitat...........,.,...,....,.,..............,........................................ 6.
Hydrology............,..,.........,....,....,..,..................,.......,.........,., .........,........ .6..
Soils...., .............................................,..............,...................,. ............,.."..6...
Vegetation............ ..... ......'..... ,... ... .... .;.............. .......,......" ,.. ..... .... ..... ........6,.
Ratings...............................................,....,................,.,......,........ 9
Hydrogeomorphic Class..,...,..,..,...........,.,.............,......................,.............9-
Functional Rating. ..,. .......,.. ..,.................,................,.....,.,.. ....,...........,.,...9.
Buffers............... ....... ....... ..... .., ,.........,............ ........... ,.,.,......,... ...,...,.. .,.10
Summary-......,..........................,...................................,........... 10
Figure 1. USGS Topo.................................................... ...... ...... 11
Figure 2. Aerial Photo and Wetland Unit................................... 12
Figure 3, Wetland Boundary- Map............................................., 13
Figure 4. Jefferson County Sensitive Areas Map........................ 13
Figure 5. NRCS Soil Survey Map............................................... 14
Figure 6. National Wetlands Inventory Map............................... 15
Figure 7. DNR Streams Map............................... ...................... 16
Figure 8. DOE Coastal Atlas..................................................... 16
Appendix 1. Photos.......................... .................... ..................... 17
Appendix 2. References......,...................................,................ ..19
Appendix 3. Soils Descriptions...............,....,......... ,................. ..20
Appendix 4. Data Sheets..........,.,.............,......,...................... ...21
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Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation
April 5, 2007
p.3of37
Introduction
Purpose
At the request of Raymond and Patti Snow> a wetland delineation and rating
was performed at their property in Quilcene> Jefferson County, Washington
on March 31> 2007. The Snows are seeking a building permit on the parcel
for the construction of a single-family residence.
Scope
The wetlands in question are extensive and extend off of the property
boundaries. Delineation was limited to the parcel owned by the Snows.
Observation of the remainder of the wetland was done via public road access
and aerial photography.
Site/Project Description
Currently, a mobile home is located on the northwest comer of the property.
The mobile home will be removed when construction is begun, Permit
application and land clearing is anticipated for 2007. The Snows are also
establishing a conservation easement to protect a portion of Tarboo Creek on
their property in conjunction with the Northwest Watershed Institute and the
Jefferson Land Trust.
Background
Location
. 8087 Center Road> Quilcene WA 98376
. Parcel number: 801201006
. Sections 20 & 21 jTownship 28N jRange 1 W
. Parcel Size: 7.35 acres
. Access: shared private drive off of Center Road
Sources
. USGS Center Quad topographical map
http://www.topozone.com
. Aerial photos, Google Earth. jMap> accessed online 2007
. Jefferson County Critical Areas Map, accessed online 2007
http://www.co.jefferson.wa.us/idms/ma.pserver.shtml
. NRCS Web Soil Survey, accessed online 2007
http://websoilsurvey.nrcs.usda.gov
. USFWS National Wetland Inventory (NWI), accessed online 2007
http://wetlandsfws.er. usgs.gov Iwtlnds Ilaunch.html
. WA DNR Forest Resource Map, accessed online 2007
http://www3.wadnr.gov/dnra.pp5/website/{pars/viewer.htm
. WA DOE Coastal Atlas, accessed online 2007
http:// apps.ecy.wa.gov I web site I coastal atlas
. WA NHP TRS List of Sections that Contain Natural Heritage Features
Associa.ted with Wetlands, August 11, 2006
http://www.dnr.wa.gov I nhp I refdesk I datasearch I index.html
Complete references are listed in Appendix 2.
Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation
April 5, 2007
p. 4 of 37
Topography
The subject property is located along Tarboo Creek, approximately 3.3 miles
north of Tarboo Bay. Access is off of Center Road, about 1.2 miles south of
highway 104 and 0.75 miles south of Dabob Road.
The parcel is located on terraces and bottomlands of Tar boo Valley. Elevation
is between 140 and 200 feet above sea level (Figure 1). The topography is flat
to moderately sloped, with slopes between 10 and 20 percent between an
upland terrace at the west end of the property and the valley bottom.
Aerial Photos
Aerial photos reveal a mix of coniferous and decidous forest, pasture and
shrub land (Figures 2 and 3). Vegetation changes at the wetland boundary
are evident. The current residence is visible on 2005 and more recent aerial
photos.
Sensitive Areas Map
The Sensitive Areas Map of Jefferson County shows the eastem two-thirds of
the parcel as wetland. This area roughly corresponds to the mapped hydric
soils (Figure 4),
Jefferson County Soil Survey
The soil survey of Jefferson County indicates the presence of 5 soil types:
1. AmC Alderwood gravelly loam, 0 to 15 percent slopes
2. AmD Alderwood gravelly loam, 15 to 30 percent slopes
3. Sh Semiahmoo muck, moderately shallow variant
4. Sm Semiahmoo muck, shallow variant
5. StB Swantown gravelly sandy loam, 0 to 8 percent slopes
Semiahmoo muck is a listed hydric soil. Swantown gravelly sandy loam is a
somewhat poorly drained soil that may exhibit a seasonally high water table.
Alderwood gravelly loam is an upland soil. The eastem two-thirds of the
property are mapped as hydric (Figure 5). See Appendix 3 for soil
descriptions.
National Wetland Inventory
The National Wetland Inventory map shows the onsite wetland to be a
complex of emergent, shrub/scrub, and forested wetlands and ponds along
Tarboo Creek and on adjacent floodplains (Figure 6). The size of the mapped
wetland complex is approximately 59 acres. In addition, approximately 19.6
acres of emergent, shrub/scrub and forested wetlands are mapped within
one-half mile to the north. Seven small ponds and emergent wetlands are
mapped within one-half mile to the south. Hundreds of acres of wetlands
exist further downstream.
Watershed
The section of Tar boo Creek which passes through the subject property is
mapped as a Type F fish-bearing stream on the DNR Resource map (Figure
7). It is also listed as a Category 5 water on the DOE Coastal Atlas, due to
high temperatures (Figure 8). Offsite to the southwest, a Type N non-fish-
Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation
April 5,2007
p. 50f 37
bearing stream is shown on the DNR map. Other tributaries to Tarboo Creek
are shown nearby but not onsite.
Natural Heritage sites
The Natural Heritage Program list of Sections that Contain Natural Heritage
Features Associated with Wetlands does not list Section 20 or 21 of Township
28 Range 1 W as including natural heritage features.
Methodology
Wetland delineation
This wetland delineation used standard procedures outlined in the
Washington State Wetlands Identification and Delineation Manual and the US
Army Corps of Engineers Wetland Delineation Manual. Data points were
established during fieldwork and marked with flagging, Blue flagging denotes
wetland data points and orange flagging denotes upland data points.
Delineation was established by data taken at data points and additional
observation of vegetation, soils and hydrology throughout the site. Wetland
boundaries were flagged with pink flagging printed "Wetland Boundary" and
numbered and labeled. Ratings were done using the Revised Wetland Rating
Systemfor Western Washington, 2004.
Jurisdiction
Wetlands are subject to regulation through federal, state and local
legislation. The subject property is under Jefferson County jurisdiction and
applicable code includes Title 18 of the Unified Development Code (UDC),
Chapter 18.15 Land Use Districts, Article VI-I Wetlands.
Findings
General Wetland Conditions
The subject wetland is largely composed of old pasture in various stages of
regeneration into forest (Figure 2). The portion of the wetland on the Snow
property is primarily a floodplain wetland with small depressions throughout
an<;l slope wetlands on the western edge. The Snow property has a residence
(mobile home) at the Northwestern comer of the parcel. The rest of the
property is undeveloped and undisturbed. Approximately two-thirds of the
parcel is forest. The remaining third is old pasture which has been replanted
in native trees and shrubs as part of a restoration effort. Areas of shrub
vegetation surround the old pasture.
The majority.. of the wetland lies on other private property. Approximately
three-quarters of the wetland is forested. Another quarter is pasture, some of
which is grazed or mowed. Shrub dominated areas are scattered along the
edges of the pastures.
Data Point 1 (DP 1) was located on the western edge of the floodplain, Data
Point 2 (DP 2) was situated approximately 30 feet upslope from this
floodplain edge near the only slope seep that was found. Data Point 3(DP 3}
was approximately 10 feet farther upslope (Figure 3 and Appendix 1).
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April 5, 2007
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Streams and Habitat
Tarboo Creek runs north to south through the center of the wetland (Figure
7). Tarboo Creek is a Type F Fish-Bearing stream. At least two Type F
tributaries and one Type N Non-Fish-Bearing stream join Tarboo Creek
within the wetland. Only Tarboo Creek runs through the Snow property,
approximately 150 feet from the eastern property boundmy.
A pileated woodpecker was heard in the area, but no priority species or their
sign were observed onsite.
Hydrology
Surface water was present at a small seep near the base of the slope leading
down to the valley bottom on the Snow property. The floodplain had
numerous small depressions filled with water with depths ranging from 1
inch to 18 inches. Soils in the floodplain was saturated to within a few
inches of the surface. Tarboo Creek is approximately three to five feet wide
and six to twelve inches deep where it crosses the Snow property.
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At DP 1 located in the floodplain (Figure 3), water was present 2 inches below
the surface in the test pit. Wetland hydrology criteria were also met by
observation of drainage pattems, a positive FAC-neutral test of the
vegetation, and the confirmation of the mapped hydric soil Semiahmoo muck
(See Appendix 4 for complete data sheets). DP 2 had a small surface seep 6
feet from the pit, but no water or saturation within the pit. DP 3 had no
indicators of hydrology.
Soils
At DP 1 the soil to 11 inches below surface was a saturated peaty muck, This
organic soil was similar in description to Semiahmoo muck, a listed hydric
soil. From 11 to 16 inches, a mucky clay was found with low chroma (lOYR
2/1 Munsell reading).
At DP2, the upper 8 inches of soil was clay with a MunseUreading of lOYR
3/2. From 8 to 16 inches, a clay loam was present with prominent mottles
(10YR 5/6), indicating seasonally hydric conditions, The soil profile did not
match the description of Alderwood gravelly loam in the Jefferson County
Soil Survey.
Soils at DP 3 were better drained and higher chroma, with a loamy texture in
the first 13 inches. Below 13 inches, a clay loam of lOYR 3/3 with distinct
mottles (10YR 4/3) was present. Since the matrix chroma was greater than 2
this did not meet hydric criteria. However the soil did seem transitional
towards hydric. Quick pits farther upslope did not encounter this mottled
clay layer.
Vegetation
The dominant vegetation at DP 1 was 89% hydrophytic, meeting wetland
criteria. In addition, the vegetation had a FAC-neutral test ratio of 4: 1,
showing that it was strongly hydrophytic.
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Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail.com
Snow Delineation
April 5, 2007
p. 7 of 37
At DP 2, the dominant vegetation was slightly over 50% hydrophytic and
therefore met wetland criteria. This was judged to be the upper limit of
wetland vegetation on the slope, although scattered facultative species such
as alder and salmonberry were present in lesser numbers farther upslope.
DP 3 had less than 50% hydrophytic vegetation, and so did not meet wetland
criteria.
List of Plant Species Identified Onsite
Wetland Plants
~~f~ommo~name~ ,~--____~cator ~~
Alnus ntbra Red alder FAC Tree
Picea sitchensis Sitka spruce FAC Tree
Thuja plica.ta Western red cedar FAC Tree
Lonicera involucrata Twinberry FAC+ Shrub
Rubus spectabilis Salmonberry FAC+ Shrub
Salix lucida lasiandra Pacific willow FACW+ Shrub
Geum macrophyllum Large-leaved avens FACW- Herb
Lysichiton america nus Skunk cabbage OBL Herb
Maianthemum dilatatum False lily-of-the-valley FAC Herb
Rarw.nculus repens Creeping buttercup FACW Herb
Stachys chamissonis cooleyae Cooley's hedgenettle FACW Herb
Urtica dioica. Stinging nettle FAC+ Herb
Veronica americana American brooklime OBL Herb
Agrostis stolonifera Colonial bentgrass FAC Graminid
Carex obrw.pta Slough sedge OBL Graminid
Juncus ef./Usus Soft rush FACW Graminid
Phalaris antndinacea Reed canarygrass FACW Graminid
Scirpus microcarpus Small-fruited bullrush OBL Graminid
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Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation
April 5, 2007
p. 8 of 37
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Athyrium filix-femina Lady fern FAC Fern
Equisetum arvense Common horsetail FAC Horsetail
Equisetum telmateia Giant horsetail FACW Horsetail
Upland Plants
~_'Indicat~r',~
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Abies grandis Grand fir FACU Tree
Acer macrophyllum Big-leaf maple FACU Tree
Prunus emarginata Bitter cherry FACU Tree
Pseudotsuga menziesii Douglas-fir FACU Tree
Acer circinatum Vine maple FAC- Shrub
.
Rex aquifolium Holly NI Shrub
Malwma nervosa Oregon-grape FACU Shrub
Malus sp. Apple NI Shrub
.
Oemleria cerasiformis Osoberry FACU Shrub
Rubus armeniacu.s Himalayan blackberry FACU Shrub
Rubus laciniatus Evergreen blackberry FACU+ Shrub
Rubus ursinus Trailing blackberry FACU Shrub
Sambucus racemosa Red elderberry FACU Shrub
Vaccinium parvifolium Red huckleberry NI Shrub
TriUium ovatum Pacific trillium FACU Herb
Dactylis glomerata Orchardgrass FACU Graminid
Phleum pratense Timothy FAC- Graminid
Polystichum munitum Sword fern FACU Fern
Pteridium aquilinum Bracken FACU Fern
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Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation
April 5, 2007
p. 9 of 37
OBL Obligate Wetland
FACW Facultative Wetland
FAC Facultative
FACU Facultative Upland
UPL Obligate Upland
NI No Indicator
+ or-
Occur almost always in wetlands.
Usually occur in wetlands.
Equally likely to occur in wetlands or non wetlands.
Usually occur in non wetlands.
Occur almost always in non wetlands.
denotes more or less likely to occur in wetlands
Ratings
Hydrogeomorphic Class
Three hydrogeomorphic classes are present in the subject wetland. Slope
wetlands on the valley edges grade into depressional and riverine wetlands
on the valley floor. As per the Revised Rating System guidelines, the wetland
was rated as Depressional since more than two classes are present. The
entire 59 acre wetland was rated as one unit (Figure 2).
Functional Rating
Based on functions provided by the wetland, the subject wetland scored 16
points for Water Quality, 8 points for Hydrological Functions and 23 points
for Habitat Functions for a total of 47 points on the state rating form,
making it a Category III wetland (see Appendix 4 for complete form). All
Category III wetlands 2,500 square feet or larger are regulated in Jefferson
County.
Water quality potential was provided by the presence of organic soil and
greater than 50% persistent, ungrared vegetation. Water quality opportunity
was provided by streams discharging into the wetland that drain farmed
fields, roads and clear-cut logging.
Hydrologic potential was provided by numerous small depressions that trap
water and the ratio of wetland size to watershed size. Hydrologic opportunity
is provided by the fact that the downstream portion of Tarboo Creek has
several road crossings and buildings in the floodplain, The Tarboo Valley has
an associated 100-year floodplain (Figure 8).
Habitat potential was provided by the variety of vegetation classes and
hydroperiods, and rich species diversity. Restoration has added a number of
standing snags and even more species diversity, which was not counted in
the plant list. Somewhat impacted buffers and corridors led to a moderate
score for habitat opportunity.
Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
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April 5, 2007
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Buffers
According to UDC 18,15.340 Protection Standards, Table 3-4, the standard
buffer width for a delineated Category III wetland is 75 feet from the wetland
boundary. The approximate location of the buffer is shown on Figure 3. No
clearing, pruning of native vegetation or grading is allowed in wetland buffers
and they are to remain in a natural state. The buffer was flagged with pink
flagging and labeled Wetland Buffer. Careful land clearing is required in
order to not accidentally impact the buffer, especially since tree fall will likely
occur downslope in that direction when logging.
Tarboo Cree).{ will have an associated stream buffer of 150 feet, but this is
superseded on the Snow property by the wetland, which provides a wider
buffer.
Summary
A Category III wetland was delineated on the Snow property in Quilcene,
Washington, Wetland boundaries and buffers were marked in the field. The
proposed building site lies outside of the buffer, Land clearing activities
should be planned carefully as to not impact the buffer.
All wetlands are considered potential wetlands until confttmed by the
appropriate regulatory agency. All information in this report should be
reviewed by the appropriate regulatory agencies prior to approval. If there are
further questions or planning requirements for this project please do not
hesitate to contact me.
)4jb~~~
Michael B. Dawson
Wetland Delineator Certification Training, Wetland Training Institute, 2005
Revised Western Washington Rating System Training, DOE, 2006
Michael B. Dawson
1361 51 st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
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Snow Delineation
April 5, 2007
p. 11 of 37
Figure 1. USGS Tapa
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UTM 10 513242E 5305735N (NAD27)
Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaAIB Dawson@gmail com
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April 5. 2007
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Figure 2. Aerial Photo and Wetland Unit
Michael B. Dawson
1361 51 st Street
Port Townsend, WA 98368
360-385-1773
Iv'lichaelB Dawson@gmail com
Snow Delineation
April 5, 2007
p.13of37
Figure 3. Wetland Boundary Map
1"" = 2()O"
Figure 4. Jefferson County Sensitive Areas Map
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Figure 5. NRCS Soil Survey Map
Snow property
Tables · Map Unit Hydric Rating 0
Suinmaiy. bY Map Unit -J.efferson CoUI1ty~,. WashIngton
5011 Survey Area Map Map Unit Name
Unit Symbol
Arne
Alderwood gravelly loam, 0 to 15 percent
slopes
Alderwood gravelly loam, 15 to 30 percent
slopes
Semiahmoo muck, moderately shallow
variant
Semiahmoo muck, shallow variant
Swantown gravelly sandy loam, 0 to 8
percent slopes
@
Rating Total Acres in AOI Percent of AOI
Not Hydric 0.3 3.4
Not HydriC 3.0 39.0
All Hydric 0.8 10,1
All Hydric 3.5 45,4
Not HydriC 0.2 2.2
AmD
Sh
Sm
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Michael B. Dawson
1361 51 st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation
April 5, 2007
Figure 6. National Wetlands Inventory Map
Snow wetlands
122-49-50 W
122-49-40 W
122-49-30 W
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Michael B. Dawson
1361 51 st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Legend
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Major Roads
Other Road
, Interstate
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r . USGS Quad Index 24K
Lower 48 Wetland Polygons
III Estuarine and Marine Deepwater
17'.j Estuarine and Marine Wetland
i~;; Freshwater Emergent Wetland
.. Freshwater Forested/Shrub Wetland
[f] Freshwater Pond
. Lake
Other
. Riverine
Lower 48 Available Wetland Data
Non-Digital
Digital
No Data
Scan
~ NHD Streams
Counties 100K
Urban Areas 300K
a States 100K
o South America
o North America
Scale: 1 :15,840
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April 5, 2007
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Figure 7. DNR Streams Map
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Major Roads
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~ JS '1 g"",,,,,
r/ tT..e'~:.:m
Streets
0 County
Fbod Zone
~ .yy.d....;:r.
~A t03 Ye:.' ~'O'.T.I....."'..I
WaleI' Bodies I.H)OK)
Figure 8. DOE Coastal Atlas
_ Re"A.-."O-,'
o G..o:t;..,(!'
D \f3''l>~1
o ~O;'.
o b.:n:1
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~ Streams
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HiUshade 110m;.
Michael B. Dawson
1361 51 st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation '
April 5, 2007
p. 17 of 37
Appendix 1. Photos
Tarboo Creek on Snow Property
DP1
. ,
Michael B. Dawson
1361 51 st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
~q ~ \\~
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OCT - 1 2007 \ L
.~
..' COUNTY
.:{iTY OEVELOPt..~EN
Snow Delineation
April 5, 2007
p. 18 of 37
DP 2 & 3
Proposed Building Site
Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Snow Delineation
April 5, 2007
p. 19 of 37
Appendix 2. References
Cowardin, L. M., v, Carter, F. C. Golet, E. T. LaRoe. 1979. Classification of Wetlands
and Deepwater Habitats of the United States. US Fish and Wildlife Service
(USFWS), Washington, D.C. Jamestown, ND: Northern Prairie Wildlife Research
Center hUp: Ilwww.npwrc.usgs.gov/resource/1998/c1asswetlc1asswet.htm
Hitchcock, L.C. and A. Cronquist, 1973. Flora of the Pacific Northwest. University of
Washington Press.
Hruby, T. 2004. Washington State Wetlands Rating Systemfor Western Washington-
Revised. Washington State Department of Ecology Publication #04-06-025.
Jefferson County, Unified Development Code. Accessed online 2007.
http://nt5.scbbs.com/c&i-bin/om isa,pLdll?
clientID=336183&infobase=ieffco l.nfo&softpage= PL frame
Jefferson County, Critical Areas Map. Accessed online 2007.
htl;p: Ilwww.coJefferson.wa.us/idms/mapserver.shtml
McMi11a.n., A. 1997. Washington State Wetland Identification and Delineation Manual.
Washington State Department of Ecology Publication #96-94.
Munsell Soil Color Charts, 2000 rev. GretagMacbeth. New Windsor, New York.
Pojar, J. and A. MacKinnon, 1994. Plants of the Pacific Northwest Coast. Lone Pine
Publishing. Vancouver, British Columbia.
Reed, Jr., P. 1988. National List of Plant Species That Occur in Wetlands, USFWS
Biological Report 88 (26.9), http://www.fws,gov/nwi/bha/list88.html
Speare Cooke, S., 1997. A Field Guide to the Common Wetland Plants of Western
Washington and Northwestern Oregon. Seattle Audubon Society. Seattle,
Washington.
USDA Natural Resources Conservation Service (NRCS), Web Soil Survey. Accessed
online 2007. htl;p: Ilwebsoilsurv~y.nrcs. usda.g.ov
USDA Plants Database. Accessed online, 2007. http://plants.usda.gov
USFWS, 1993. 1993 Supplement to List of Plant Species That Occur in Wetlands:
Northwest (Region 9). Supplement to USFWS Biological Report 88 (26.9).
USFWS, National Wetland Inventory. Accessed online 2007.
http://wetlandsfws.er.usgs.gov IwtlndsI launch.html
Washington Department of Ecology, CoastalAtlas. Accessed online 2007
http://apps,ecy.wa.gov/website/coastal atlas
Washington Department of Natural Resources, Forest Resource Map. Accessed online
2007. http://www3.wadnr.gov/dnrapp5/website/fpars/viewer.htm
Washington Natural Heritage Program, List of Sections that Contain Natural Heritage
Features Associated with Wetlands, August 11, 2006. Accessed online 2007.
http://www.dnr.wa.gov InhpIrefdeskI datasearch/index.html
Wetland Training Institute, Inc. 1995. Field Guide for Wetland Delineation; 1987
Corps of Engineers Manual, Glenwood, NM. WTI 02-1
{";-'''- f"":"~-;'-"~":'i,..11
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OCT - 1 2007 II ,.. , I
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Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
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Snow Delineation
April 5, 2007
p. 20 of 37
Appendix 3. Soils Descriptions
Map Unit Description (Brief. Generated)
Jeft'erson County Area, Washington
[Minor map unit components are excluded from this report)
Map unit: ArnC - A1delWOOd gravelly loam, 0 to 15 pen:ent slopes
Component: AIdeIWOOd (100%)
The AIderwcod component makes up 100 percent of the map unit. Slopes are 0 to 15 pen:ent This corirponent is 011 temlces. The
parelIt material consists of basal till with a component of voIc8nic ash in the upper part Depth to a root restrictive Ia)tll; densic material,
is 20 to 40 inches. The nattJraI drainage class is moderately well drained. Water moll8l1l6llt in the most restrictive layer is low. Available
water to a depth of 60 inches Is lie!)' bw. Shtink-swell potential Is loW. 7hJs soil is not flooded. It Is not ponded. A seasonal zone of water
saturation is at 30 Inches during January, February, March. Organic matter content in. the surface. hotlzon Is about 6percent
Nonirrlgated land capability classification is 4s. This soil does not meet hydtic ctitetia.
Map unit: ArnD - A1derwood gravelly loam, 15 to 30 percent slopes
Component: A1delWOOd (100%)
The AIderwood component makes lip 100 percent of the.map unit. Slopes are 15 to SO percent. This component is 011 terraces. The
parent material consists of basal tiH with a component of lIOicanic ash in the upper part Depth to a root restrictive Ia)tll; densic materia/,
is 20 to 40 inches. The natural drainage c/a$$ /s moderately well drained Water movement in the most restrictive layer is loW. Available
water to a depth of 60 Inches Is 1I\!IIY low. Shtink-swel1 potBntIaJ is low. This soil is not flooded. It Is not ponded. A seasonal zone of water
saturation is at 30 inches durIng.lanuaty. Febtuaty. Match. Organic matter content in the surface horizon is about 6 percent
Nonirrigated land capability cIassificatioiI is 4e. 7hJs soil does not meet hydt/c ctitetia.
Map unit: 8h - Semiahmoo muck, moderately shaIow variant
Component: Semlahmoo (100%)
The Semiahmoo component makes up 100 percent of the map unit. Slopes are 0 to 1 percent This component is 011 depressions. The
parelIt material consists of heIbaceous otg8IIic materfaI. Depth to a root restrictive.layer is gTeater than 60 inches. The natural drainage
c/a$$1s WI)' pootIy drained. Water mowment iJ the most restrictive layer Is moderately high. Available water to a depth of 60 inches /s
1IeIY high. Shrin/(-sweH potential is low. 7hJs soil Is not fIoodBd. It Is 1r8quentty ponded. A seasonal zone of water saturation is at 0
inches during January, February, March, April, May. November. December. Organic matter conterIt in the surface horizon Is about 45
percent NOIIirrigated land capability classification is 5w. This soil meets hydric ctitetia.
Map unit: 8m - Semiahmoo muck, shaDow variant
Component: Semiahmoo (100%)
The Semiahmoo oomponent maIces up 100 percent of the map unit. Slopes am 0 to 1 petCeIIt. This component is 011 depIessions. The
parent materialconsists of hetbacsous organic materfaI. Depth to a root restrictive layer /s gTeater than 60 inches. The nattJraI r/raInage
c/a$$ is 1IeIY pootIy drained. Water movement In the most restrictive layer is mOderately high. Available water to a depth of 60 Inches /s
1IeIY high. Shrink-sweH potential Is low. 7hJs soil is not fIoodBd.lt is frequently ponded. A seasonal zone of water saturation Is at 0
inches during January, Februaty, March, April, May. November, DeCember. Organic matter content in the surface horizon is about 45
percent NOIIInigated land capabifity classification is 5w. This soil meets hydric ctitetia.
Map unit: 8tB - Swantown gravelly sandy loam, 0 to 8 pen:ent slopes
Component: Swantown (100%)
The Swantown component makes up 100 percent of the map unit. Slopes are 0 to 8 petCeIIt. This component is on uplands. The parent
material consists of tiH. Depth to a root restrictive Ia)tll; densic material, is 20 to 30 Inches. The natural drainage class is somewhat
poorly drained. Water movemet1t in the most restrictive layer Is bw. Available water to a depth of 60 inches is 1I\!IIY loW. Shtink-sweH
potential is low. This soil is not fIoodBd. It Is not ponded. A seasonal zone of water saturation is at 9 Inches during January, February,
March, November, Dacamber. OrganIc matter content in the surface horizon is about 2 percent. Nonirrigated land capability
cIassificatioiIls 6w. 7hJs soil does not meet hyrlric criteria.
USDA Natural Resources
~ Conservation Service
Tabular Data Version: 3
Tabular Data Version Date: 11/2112006
Michael B. Dawson
1361 51st Street
Port Townsend, WA 98368
360-385-1773
MichaelS Dawson@gmail com
Page 1 ot 1
Routine Wetland Determination
DATA FORM 1 (Revised)
WA State Wetland Delineation Manual or 1987 Corps Wetland Delineation Manual)
Project/Site: Snow property Date: 2007/03/31
Applicant/owner: Raymond & Patti Snow County: Jefferson
Investigator(s): Michael Dawson State: WA
., Srr/R: 20128N/1 W
Do normal circumstances exist on the site? I8IVes DNo Community ID:Wetland A
Is the site significantly disturbed (atypical situation)? DVes 181 No Transect ID:
Is the area a potential problem area? DVes 181 No PlotlD: DP 1
Explanation of atypical or problem area: Near flag A3.
VEGETATION (For *strata, indicate T = tree; S = shrub; H = herb; V = vine)
Dominant Plant Species *Stratum % cover Indicator Dominant Plant Species *Stratum % cover Indicator
Alnus rubra T 10 FAC Equisetum arvense H 5 FAC
Oemleria cerasiformis S 2 FACU Equisetum telmateia H 5 FACW
Scirpus microcarpus H 35 OBL Agrostis sto/onifera H 5 FAC
Juncus effusus H 30 FACW
Ranunculus repens H 25 FACW
Athyrium filix-femina H 10 FAC
HYDROPHYTIC VEGETATION INDICATORS:
% of dominants OBL, FACW, & FAC: 8/9 89%
Check all indicators that apply and explain below:
o Visual observation of plant species growing in o Physiological/reproductive adaptations
areas of prolonged inundation/saturation 181 Wetland plant database
o Morphological adaptations 181 Personal knowledge of regional plant communities
o Technical Literature o Other (explain)
Hydrophytic vegetation present? 181 Ves ONo
Rationale for decisionlRemarks: Greater than 50% of dominants hydrophytic.
HYDROLOGY
Is it the growing season? 181 Ves ONo Water Marks: DVes 181 No Sediment Deposits: 0 Ves 181 No
on
Based on: 0 Soil temp (record temp) Drift Lines: Dves 181 No Drainage Patterns: 181 Ves ONo
(air temp 460) Flat slope with small depressions
181 Other (explain) dormancy ended and clay layer in soil.
Depth of inundation: 0 inches Oxidized Root (live roots) Local Soil Survey: 181 Ves ONo
Channels <12 it: o Ves 181 No
Depth to free water in pit: 2 inches FAC Neutral: 181 Ves DNo Water-stained Leaves:
Dves 181 No
Depth to saturated soil: to surface 4:1
Check all that apply & explain below: Other (explain):
o Stream, lake or gage data --~ "-;:.--;;-._~_.._--:~~:~,'
181 Aerial photographs rr--- rc; (t' '; i \
j F\' Ie \\::7 lJ \ "
o Other \ \ \ ,f I r ~_~~~-,:-.___~"~;.___n_-\ \ i
" ~.,. , : j \ .
:: r<"\ . : !
181 0 \ :'" OCT - 1 2001 ."~
Wetland hydrology present? Yes No i \ \ \ : \l-
Rationale for decision/remarks: !.;J ~~ i
High water table, drainage patterns, positive FAC-neutral rnd sbil survey. ,_ -----1
\"VUri I -
I
: dl'r
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SOILS
Map Unit Name (Series and Phase): Sm Semiahmoo Drainage Class: Very poorly drained
muck, shallow variant
Field observations confirm mapped type? ~Ves ONo
Taxonomy (subgroup): Typic Medisaprists
Profile Description
Depth _ Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile
(inches) Horizon (Munsell moist) (Munsellrnoist) size and contrast structure, etc. (match descriotion)
0-11" 10YR 2/1 None Peaty muck
11-16" 10YR 2/1 None Mucky clay
Hydric Soil Indicators: (check all that apply)
~ Histosol o Matrix chroma 0 2 with mottles
o Histic Epipedon o Mg or Fe Concretions
o Sulfidic Odor o High Organic Content in Surface Layer of Sandy Soils
~ Aquic Moisture Regime o Organic Streaking in Sandy Soils
o Reducing Conditions ~ Listed on National/Local Hydric Soils List
~ Gleyed or Low-Chroma (=1) matrix o Other (explain in remarks)
Hydric soils present? ~Yes ONo
Rationale for decision/Remarks: Organic texture, listed hydric soil, low chroma, complete saturation.
Wetland Determination
Hydrophytic vegetation present? ~Yes ONo
Hydric soils present? I8IVes ONo
Wetland hydrology present? 181 Yes ONo
Is the samDlina Doint within a wetland? 181 Ves ONo
Rationale/Remarks:
~~
NOTES:
Revised 4/97
WA State Wetland Delineation Manual or 1987 Corps Wetland Delineation Manual)
Snow property Date: 2007/03/31
Raymond & Patti Snow County: Jefferson
Michael Dawson State: WA
Srr/R: 20128N/1W
Community ID:Wetland A
Transect 10:
PlotlD:
Near flag A2.
Routine Wetland Determination
DATA FORM 1 (Revised)
Project/Site:
Applicant/owner:
Investigator( s):
.. !
~Yes
DYes
DYes
ONo
~No
~No
Do normal circumstances exist on the site?
Is the site significantly disturbed (atypical situation)?
Is the area a potential problem area?
Exolanation of atypical or problem area:
VEGETATION (For *strata, indicate T = tree; S = shrub; H = herb; V = vine)
Dominant Plant Soecies *Stratum % cover Indicator Dominant Plant Soecies
Alnus robra T 10 FAC Maianthemum dilatatum
Rubus spectabilis S 50 FAC+
Oem/eria cerasiformis S 40 FACU
Rubus armeniacus S 10 FACU
Lonicera invo/ucrata S 2 FAC+
Po/ystichum munitum H 10 FACU
HYDROPHYTIC VEGETATION INDICATORS:
% of dominants OSL, FACW, & FAC: 4rl 57%
Check all indicators that apply and explain below:
o Visual observation of plant species growing in
areas of prolonged inundation/saturation
o Morphological adaptations
o Technical Literature
DP2
*Stratum
H
% cover
10
Indicator
FAC
o Physiological/reproductive adaptations
~ Wetland plant database
~ Personal knowledge of regional plant communities
o Other (explain)
Hydrophytic vegetation present? ~ Yes 0 No
Rationale for decision/Remarks: Greater than 50% of dominants hydrophytic.
HYDROLOGY
Is it the growing season? ~ Yes 0 No
Water Marks: 0 Yes ~ No
on
Based on: 0 Soil temp (record temp)
(air temp 460)
~ Other (explain) dormancy ended
Depth of inundation: 0 inches
Drift Lines:
DYes ~ No
Oxidized Root (live roots)
Channels <12i1.: 0 Yes ~ No
FAC Neutral: 0 Yes ~ No
Depth to free water in pit: none
Depth to saturated soil: none
Sediment Deposits: 0 Yes ~ No
Drainage Patterns: 0 Yes ~ No
Local Soil Survey: 0 Yes ~ No
Water-stained Leaves:
DYes ~ No
Check all that apply & explain below: Other (explain): A seep with surface water is 6' to the East. A clay
o Stream, lake or gage data layer i.n the soil is ~ikely forcing slope flow to surface here as well ~he". __
~ Aerial photographs there IS ample mOisture. ff-;....-:\ l~; C W;;: II 'w tE ~\
II, \, u::> """.. _ I
o Other , : L))r : ;
Wetland hydrology present? ~ Yes 0 No ; \ \ \ \ \ OCT - 1 2001 \ d
Rationale for decision/remarks: Transitional to upland. Upslope from here no indicators of hy~rol~y were found.
t l',rf,
COUNTY
"rv DfVELOPMEN1
SOILS
Map Unit Name (Series and Phase): AmD Alderwood Drainage Class: Moderately well drained
gravelly loam, 15 to 30 percent slopes
Field observations confirm mapped type? DYes 181 No
Taxonomy (subgroup): Vitrandic Durochrepts
Profile DescriDtion
Depth Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile
(inches) Horizon (Munsell moist) (Munsell moist) size and contrast structure, etc. (match descriDtion)
0-8" 10YR 3/2 None clay
8 _16" 10YR 5/2 10YR 5/6 Common, medium, Clay loam w/charcoal
prominent bits
Hydric Soil Indicators: (check all that apply)
o Histosol 181 Matrix chroma 0 2 with mottles
o Histic Epipedon o Mg or Fe Concretions
o Sulfidic Odor o High Organic Content in Surface Layer of Sandy Soils
o Aquic Moisture Regime o Organic Streaking in Sandy Soils
o Reducing Conditions o Listed on National/Local Hydric Soils List
o Gleyed or Low-Chroma (=1) matrix o Other (explain in remarks)
Hydric soils present? 181 Yes ONo
Rationale for decision/Remarks: Low chroma with mottles.
Wetland Determination
Hydrophytic vegetation present? 181 Yes ONo
Hydric soils present? 181 Yes ONo
Wetland hydrology present? 181 Yes ONo
Is the samplinQ point within a wetland? 181 Yes ONo .
RationalelRemarks: Transitional to uoland.
NOTES:
Revised 4/97
I
I
I
I
.1
Routine Wetland Determination
DATA FORM 1 (Revised)
WA State Wetland Delineation Manual or 1987 COrDS Wetland Delineation Manual)
Project/Site: Snow property Date: 2007/03/31
Applicant/owner: Raymond & Patti Snow County: Jefferson
Investigator(s): Michael Dawson State: WA
srr/R: 20128N/1 W
Do normal circumstances exist on the site? 181 Ves DNo Community ID:Wetland A
Is the site significantly disturbed (atypical situation)? DVes 181 No Transect ID:
Is the area a potential problem area? DVes 181 No PlotlD: DP3
Explanation of atypical or problem area: Near flag A 1.
VEGETATION (For *strata, indicate T = tree; S = shrub; H = herb; V = vine)
Dominant Plant Species *Stratum % cover Indicator Dominant Plant Species *Stratum % cover Indicator
Alnus rubra T 70 FAC Po/ystichum munitum H 10 FACU
Abies grandis T 25 FACU-
Oem/eria cerasiformis S 75 FACU
Rubus spectabilis S 10 FAC+
/lex aquifolium S 5 NI
Rubus armeniacus S 5 FACU
HYDROPHYTIC VEGETATION INDICATORS:
% of dominants OBl, FACW, & FAC: 2f7 29%
Check all indicators that apply and explain below:
o Visual observation of plant species growing in o Physiological/reproductive adaptations
areas of prolonged inundation/saturation 181 Wetland plant database
o Morphological adaptations 181 Personal knowledge of regional plant communities
o Technical Literature D Other (explain)
Hydrophytic vegetation present? DVes 181 No
Rationale for decisionlRemarks: less than 50% of dominants hydrophytic.
HVDROLOGV
Is it the growing season? 181 Ves DNo Water Marks: DVes 181 No Sediment Deposits: 0 Ves 181 No
on
Based on: 0 Soil temp (record temp) Drift Lines: DVes 181 No Drainage Patterns: DVes 181 No
(air temp 460)
181 Other (explain) dormancy ended
Depth of inundation: 0 inches Oxidized Root (live roots) local Soil Survey: Dves 181 No
Channels <12i1.: 0 Ves 181 No
Depth to free water in pit: none FAC Neutral: DVes 181 No Water-stained leaves:
DVes 181 No
Depth to saturated soil: none
'.:'
Check all that apply & explain below: Other (explain): Close in elevation to DP 2, but the soil texture and
o Stream, lake or gage data drainage much different. E) re fF:l if~ n \YJ r;::> [
,In !""!~ U" ~
181 Aerial photographs ~il ~ .'..,
'iur--
II .,
o Other \: r~"\ 1_
:; ~ ll" ^J'\'T 1 Mn"1
Wetland hydrology present? o Ves 181 No ,"',; Vvl I U;lVI .....
Rationale for decision/remarks: No indicators present. , j
i
"t.> i1~TY
.; -''>i ;"1C ;Cl f~11Ei
d~'
l_._ u".'
.,{ .._C.\LLO..:..-
--".~-_..,--
SOILS
Map Unit Name (Series and Phase): AmD Alderwood Drainage Class: Moderately well drained
gravelly loam, 15 to 30 percent slopes
Field observations confirm mapped type? DYes 181 No
Taxonomy (subgroup): Vitrandic Durochrepts
Profile Description
Depth Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil profile
(inches) Horizon (Munsell moist) (Munsell moist) size and contrast structure, etc. (match descriDtion)
0-1" 10YR 3/2 None Loam w/duff
1 - 13" 10YR 3/3 none Loam
13-16" 10YR 4/3 10YR 4/6 Common, medium, Clay loam
distinct
Hydric Soil Indicators: (check all that apply)
D Histosol D Matrix chroma 0 2 with mottles
D Histic Epipedon D Mg or Fe Concretions
D Sulfidic Odor D High Organic Content in Surface Layer of Sandy Soils
D Aquic Moisture Regime D Organic Streaking in Sandy Soils
D Reducing Conditions D Listed on National/Local Hydric Soils List
D Gleyed or Low-Chroma (=1) matrix D Other (explain in remarks)
Hydric soils present? DYes 181 No
Rationale for decisionlRemarks: Even though mottles are present, chroma is higher.
Wetland Determination
Hydrophytic vegetation present? Dyes 181 No
Hydric soils present? Dyes 181 No
Wetland hydrology present? DYes 181 No
Is the samolina Doint within a wetland? Dyes 181 No
RationalelRemarks: Near wetland boundary and somewhat transitional but positive wetland indicators are lackina.
NOTES:
Revised 4/97
Wetland name or number A
WETLAND RATING FORM - WESTERN W ASIDNGTON
Version 2 - Updated July 2006 to increase accuracy and reproducibility among users
Name of wetland (if known): 1"Altf,OO VM-L.r;y / 5 r-JOW Date of site visit: 2.007 /D 3/~ I
Rated by tJ\ \c...~AtL- 'D Aw ~O t-J Trained by Ecology? Yes ~No _ Date of training 2-DO'/o 2-
~~ /
SEC: 2-( TWNSHP:z..gtJ RNGE:I W Is Srr/R in Appendix D? Yes_ No-Y-
Map of wetland unit: Figure ~ Estimated size 5" Gf a...c.-r-e ~
SUMMARY OF RATING
Category based on FUNCTIONS provided by wetland
I n m/ IV
Category I = Score >=70
Category II = Score 51-69
Category III = Score 30-50
CategOry IV = Score < 30
Score for Water Quality Functions
Score for Hydrologic Functions
Score for Habitat Functions
TOTAL score for Functions
(~
~
'2-3
4-7
Category based on SPECIAL CHARACTERISTICS of wetland
1_ n_ Does not Apply V
Final Category (choose the "highest" category from above) I ill I
Summary of basic information about the wetland unit
Wetland Rating Form - western Washington
version 2
Estuarine
Natural Herita e Wetland
Bo
Mature Forest
Old Growth Forest
Coastal La oon
Interdunal
None of the above
I
NT
Wetland name or number .A
Does the wetland unit being rated meet any of the criteria below?
If you answer YES to any of the questions below you will need to protect the wetland
according to the regulations regarding the special characteristics found in the wetland.
. ; .....iJi3t'lclitlQlJ.f(JJbe ....(Jt~~ii~.~..~cgmlQe...t'letJ...ro...if~c3le. ~i :'i<~ ;'
SPl. Has the wetland unit been documented as a habitat for any Federally listed
Threatened or Endangered animal or plant species (I'/E species)?
For the purposes of this rating system, "documented" means the wetland is on the
a ro riate state or federal database.
SP2. Has the wetland unit been documented as habitat for any State listed
Threatened or Endangered animal species?
For the purposes of this rating system, "documented" means the wetland is on the
appropriate state database. Note: Wetlands with State listed plant species are
cate orized as Cate 0 I Natural Herita e Wetlands see . 19 of data form .
SP3. Does the wetland unit contain individuals of Priority species listed by the
WDFW for the state?
v
J
v
SP4. Does the wetland unit have a local significance in addition to its functions?
For example, the wetland has been identified in the Shoreline Master
Program, the Critical Areas Ordinance, or in a local management plan as
having special significance.
v
To complete the next part of the data sheet you will need to determine the
Hvdrogeomorphic Class of the wetland being rated.
The hydrogeomorphic classification groups wetlands into those that function in similar ways. This
simplifies the questions needed to answer how well the wetland functions. The Hydrogeomorphic
Class of a wetland can be determined using the key below. See p. 24 for more detailed instructions
on classifying wetlands.
Wetland Rating Form - western Washington
version 2
2
August 2004
Wetland name or number A
Classification of Wetland Units in Western Washington
1. Are the water levels in the entire unit usually controlled by tides (Le. except during floods)?
@ go to 2 YES - the wetland class is Tidal Fringe
If yes, is the salinity of the water during periods of annual low flow below 0.5 ppt (parts per
thousand)? YES - Freshwater Tidal Fringe NO - Saltwater Tidal Fringe (Estuarine)
If your wetland can be classified as a Freshwater Tidal Fringe use the formsfor Riverine
wetlands. Ifit is Saltwater Tidal Fringe it is rated as an Estuarine wetland. Wetlands that
were called estuarine in the first and second editions of the rating system are called Salt
Water Tidal Fringe in the Hydrogeomorphic Classification. Estuarine wetlands were
categorized separately in the earlier editions, and this separation is being kept in this
revision. To maintain consistency between editions, the term "Estuarine" wetland is kept.
Please note, however, that the characteristics that define Category I and II estuarine
wetlands have changed (see p. ).
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
~ 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 both of the following criteria?
_The vegetated part of the wetland is on the shores of a body of permanent open water
(without any vegetation on the surface) at least 20 acres (8 ha) in size;
At least 30% of the open water area is deeper than 6.6 ft (2 m)?
~ go to 4 YES - The wetland class is Lake-fringe (Lacustrine Fringe)
4. Does the entire wetland unit meet all of the following criteria?
V The wetland is on a slope (slope can be very gradual),
V 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?
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
<3ft diameter and less than 1 foot deep).
NO - go to 5 YES - The wetland class is Slope
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Wetland Rating Form - western Washington
version 2
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OCT - 1 2007 110
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Wetland name or number ~
5. Does the entire wetland unit meet all of the following criteria?
V 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 two years.
NOTE: The riverine unit can contain depressions that are filled with water when the river is
notjlooding. PA-It\ of 'Wb" Wf:n'"LA-NO tS RtveYl.l lJt
NO - go to 6 YES - The wetland class is Riverine
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. FA-r<-T" 0 F ThE' WlS'TlAND I S ~61'RB$lO~~
NO - go to 7 ~The wetland class is Depressional
7. Is the entire wetland unit located in a very flat area with no obvious depression and no overbank
flooding. The unit does not pond surface water more than a few inches. The unit seems to be
maintained by high groundwater in the area. The wetland may be ditched, but has no obvious
natural outlet.
~g, go to 8 YES - The wetland class is Depressional
8, Your wetland unit seems to be difficult to classify and probably contains several different HGM
clases. For example, seeps at the base of a slope may grade into a riverine floodplain, or a small
stream within a depressional wetland has a zone of flooding along its sides. GO BACK AND
IDENTIFY WIllCH OF THE HYDROLOGIC REGIMES DESCRIBED IN QUESTIONS 1-7
APPL Y TO DIFFERENT AREAS IN THE UNIT (make a rough sketch to help you decide). Use
the following table to identify the appropriate class to use for the rating system if you have several
HGM classes present within your wetland. NOTE: Use this table only if the class that is
recommended in the second column represents 10% or more of the total area of the wetland unit
being rated, If the area of the class listed in column 2 is less than 10% of the unit; classify the
wetland using the class that represents more than 90% of the total area.
gW1jJfjfJtlii$'~i&iWirlilif.l1jtw~tt(lililtifJit'/j~lrl <'ra~~f1i;{i .., .
Slo e + Riverine
Slo + De ressional
Slo + Lake- . e
Depressional + Riverine along stream within boundary
D ressional + Lake-frin e
Salt Water Tidal Fringe and any other class of freshwater
wetland
:"i':'Wt{ifJ!lIXf!tll~::flf:!rttl:lif~':!jrilltj""<i;
Riverine
De ressional
Lake-frin e
Depressional
De ssional
Treat as ESTUARINE under
wetlands with special
characteristics
I
If you are unable still 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. ~
':;t...oP6 + R\ \I~UJ~ + J:>tPV?.65S\otJ Al..-
Wetland Rating Form - western Washington
version 2
4
August 2004
11 . ::g~pt~s~jonal~AdFlatsW~tl~nlls
. ..;?;~;~~~~i~lJ.A.J:.rl'r:f?Jffl'~I,QN'&:..." ....mAicaf<jrstl:uJ.tth~.wetla1ld~l~Qii()il$'@.>.....;
hn . ovewater: . uali
D D 1. Does the wetland unit have the Dotential to improve water quality?
D 1.1 Characteristics of surface water flows out of the wetland:
Unit is a depression with no surface water leaving it (no outlet) points = 3
Unit has an intermittently flowing, OR highly constricted permanently flowing outlet points = 2
../Unit has an unconstricted, or slightly constricted, surface outlet (permanently flowing) points = 1
Unit is a "flaf' depression (Q. 7 on key), or in the Flats class, with permanent surface outflow and
no obvious natural outlet and/or outlet is a man-made ditch points = I
(If ditch is not permanently flowing treat unit as "intermittently flowing")
Provide hoto or drawin
S 1.2 The soH 2 inches below the surface (or duff layer) is clay or organic (use NRCS
deC{tio?j
YES points = 4
NO oints = 0
D 1.3 Characteristics of persistent vegetation (emergent, shrub, and/or forest Cowardin class) Figure ~
Wetland has persistent, ungrazed, vegetation> = 95% of area points = 5
" Wetland has persistent, ungrazed, vegetation> = 1/2 of area points = 3
Wetland has persistent, ungrazed vegetation> = 1/10 of area points = 1
Wetland has persistent, ungrazed vegetation <1/10 of area points = 0
Ma of Coward in v etation classes
D1.4 Characteristics of seasonal ponding or inundation.
This is the area of the wetland unit that is ponded for at least 2 months, but dries out
sometime during the year. Do not count the area that is permanently ponded. Estimate
area as the average condition 5 out of 1 0 yrs.
Area seasonally ponded is > Y2 total area of wetland
Area seasonally ponded is > ~ total area of wetland
vi Area seasonally ponded is < ~ total area of wetland
Wetland name or number --A-
D
D
D
D
D
D
Total for D 1
points = 4
points = 2
points = 0
Ma of H dro eriods
Add the points in the boxes above
D
D 2. Does the wetland unit have the opportunity to improve water quality?
Answer YES if you know or believe there are pollutants in groundwater or surface water
coming into the wetland that would otherwise reduce water quality in streams, lakes or
groundwater downgradient from the wetland. Note which of the following conditions
provide the sources of pollutants. A unit may have pollutants comingfrom several
sources, but any single source would qualify as opportunity.
Grazing in the wetland or within 150 ft
Untreated stormwater discharges to wetland
Tilled fields or orchards within 150 ft of wetland
~ A stream or culvert discharges into wetland that drains developed areas, residential areas,
farmed fields, roads, or clear-cut logging
Residential, urban areas, golf coUrses are within 150 ft ofwet1and
Wetland is fed by groundwater high in phosphorus or nitrogen
Other
YES multi lier is 2 NO multi lier is 1
TOTAL - Water Quality Functions
(see p.3B)
Figure '2-
,
4-
3
Figure _
o
.._~---
..-----
(see p. 44)
multiplier
Wetland Rating Form - western Washington
version 2
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I
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August2004 :"~-' '''TY
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dry DEVELOPMENT J
Wetland name or number A
D.
. .])epressional and Flats Wetlands
HYDROLOGIC FUNCTIONS - Indicators that the wetland u:nit{unctions t()
reduce floodin and stl'eamqe dation
D 3. Does the wetland unit have the Dotential to reduce flooding and erosion?
D 3.1 Characteristics of surface water flows out of the wetland unit
Unit is a depression with no surface water leaving it (no outlet) points = 4
Unit has an intermittently flowing, OR highly constricted permanently flowing outlet points = 2
Unit is a "flat" depression (Q. 7 on key), or in the Flats class, with permanent surface outflow and
no obvious natural outlet and/or outlet is a man-made ditch points = 1
(If ditch is not permanently flowing treat unit as "intermittently flowing")
./ Unit has an unconstricted, or sli tl constricted, surface outlet ermanentl owin
D 3.2 Depth of storage during wet periods
Estimate the height of ponding above the bottom of the outlet. For units with no outlet
measure from the surface of permanent water or deepest part (if dry).
Marks of ponding are 3 ft or more above the surface or bottom of outlet points = 7
The wetland is a "headwater" wetland" points = 5
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
Unit is flat (yes to Q. 2 or Q. 7 on key) but has small depressions on the surface that trap
water points = 1
Marks of ondin less than 0.5 ft oints = 0
D 3.3 Contribution of wetland unit 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 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 area of the unit
Entire unit is in the FLATS class
Total for D 3
D
ints = 0
D
D
D
D
points = 5
points = 3
points = 0
oints = 5
Add the points in the boxes above
D
D 4. Does the wetland unit have the oDDortunitv to reduce flooding and erosion?
Answer YES if the unit is in a location in the watershed where the flood storage, or
reduction in water velocity, it provides helps protect downstream property and aquatic
resources from flooding or excessive and/or erosive flows. Answer NO if the water
coming into the wetland is controlled by a structure such as flood gate, tide gate, flap
valve, reservoir etc. OR you estimate that more than 90% of the water in the wetland is
from groundwater in areas where damaging groundwater flooding does not occur.
Note which of the following indicators of opportunity apply.
/ Wetland is in a headwater ora river or stream that has flooding problems
JL Wetland drains to a river or stream that has flooding problems
- Wetland has no outlet and impounds surface runoff water that might otherwise
flow into a river or stream that has flooding problems
- Other
YES multi lier is 2 NO multi lier is 1
TOTAL - Hydrologic Functions Multiply the score from D 3 by D 4
Add score to table on p. 1
Wetland Rating Form - western Washington
version 2
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August 2004
(seep.46)
o
t
3
\"-4=---1
..-----
(see p. 49)
, I
multiplier
2..
<6
Wetland name or number A
H 1. Does the wetland unit have the potential to provide habitat for many species?
H 1.1 Vel!etation structure (see p. 72)
Check the types of vegetation classes present (as defined by Cowardin)- Size threshold for each
class is ~ acre or more than 10% of the area ifunit is smaller than 2.5 acres.
_Aquatic bed
-L Emergent plants
if Scrub/shrub (areas where shrubs have >30% cover)
../ Forested (areas where trees have >30% cover)
If the unit has a forested class check if:
~The forested class has 3 out of 5 strata (canopy, sub-canopy, shrubs, herbaceous,
moss/ground-cover) that each cover 20% within the forested polygon
Add the number of vegetation structures that qualify. If you have:
4 structures or more
3 structures
2 structures
1 structure
Map of Cowardin vegetation classes
points = 4
points = 2
points = 1
ints = 0
H 1.2. Hydroperiods (see p. 73)
Check the types of water regimes (hydroperiods) present within the wetland, The water
regime has to cover more than 10% of the wetland or ~ acre to count. (see text for
descriptions of hydro periods)
_Permanently flooded or inundated 4 or more types present
Seasonally flooded or inundated 3 types present
..; Occasionally flooded or inundated 2 types present
1- Saturated only 1 type present
~ Permanently flowing stream or river in, or adjacent to, the wetland
_ Seasonally flowing stream in, or adjacent to, the wetland
_ Lake-fringe wet1flnd = 2 points
~reshwater tidal wetland = 2 points Map of hydroperiods
H 1.3. Richness of Plant SlJecies (see p. 75)
Coirnt the number of plant species in the wetland that cover at least 10 :If. (different patches
of the same species can be combined to meet the size threshold)
You do not have to name the species.
Do not include Eurasian Milfoil, reed canary grass, purple loosestrife,
If you counted: > 19 species
List species below if you want to: 5 - 19 species
< 5 species
Wetland Rating Form - western Washington
version 2
13
points = 3
points = 2
point = 1
points = 0
Canadian Thistle
points = 2
points = 1
points = 0
Figure .s:..
4-
Figure _
2-
2-
r'-: r i"'0
:. \
.!ffotalforp~~ Il\ \
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Wetland name or number
A
H 1.4. Interspersion of habitats (see p. 76) igure_
Decide from the diagrams below whether interspersion between Cowardin vegetation
classes (described in H 1.1), or the classes and unvegetated areas (can include open water or
mudflats) is high, medium, low, or none.
o
None = 0 points
Low = 1 point
Moderate = 2 points
[riparian braided channels]
~
High = 3 points
NOTE: If you have four or more classes or three vegetation classes and open water
the ratin is alwa s "hi ". Use ma of Coward in ve etation classes
H 1.5. Special Habitat Features: (seep. 77)
Check the habitat features that are present in the wetland. The number of checks is the
number of points you put into the next column.
'" Large, downed, woody debris within the wetland (>4in. diameter and 6 ft long).
../ Standing snags (diameter at the bottom> 4 inches) in the wetland
V Undercut banks are present for at least 6.6 ft (2m) and/or overhanging vegetation extends at
least 3.3 ft (1m) over a stream (or ditch) in, or contiguous with the unit, for at least 33ft
(lOm)
_Stable steep banks of fine material that might be used by beaver or muskrat for denning
(>30degree slope) OR signs of recent beaver activity are present (cut shrubs or trees that
have not yet turned grey/brown)
~ At least V<I acre of thin-stemmed persistent vegetation or woody branches are present in areas
that are permanently or seasonally inundated (structures for egg-laying by amphibians)
_ Invasive plants cover less than 25% of the wetland area in each stratum of plants
NOTE: The 20% stated in early printings of the manual on page 78 is an error.
H 1. TOTAL Score - potential for providing habitat
Add the scores om Hl.I, H1.2, HI.3, HI.4, H1.5
/
Comments
Wetland Rating Form - western Washington
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August 2004
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Wetland name or number ~
H 2. Does the wetland unit have the opportunity to provide habitat for many species?
H 2.1 Buffers (see p. 80) Figure ~
Choose the description that best represents condition of buffer of wetland unit. The highest scoring
criterion that applies to the wetland is to be used in the rating. See text for definition of
"undisturbed. "
- 100 m (330ft) of relatively undisturbed vegetated areas, rocky areas, or open water >95%
of circumference. No structures are within the undisturbed part of buffer. (relatively
undisturbed also means no-grazing, no landscaping, no daily human use) Points = 5
- 100 m (330 ft) of relatively undisturbed vegetated areas, rocky areas, or open water >
50% circumference. Points = 4
- 50 m (170ft) of relatively undisturbed vegetated areas, rocky areas, or open water >95%
circumference. Points = 4
- 100 m (330ft) of relatively undisturbed vegetated areas, rocky areas, or open water> 25%
circumference, . Points = 3
- 50 m (170ft) of relatively undisturbed vegetated areas, rocky areas, or open water for> "2-
50% circumference. Points = 3
../ If buffer does not meet any of the criteria above
- No paved areas (except paved trails) or buildings within 25 m(80ft) of wetland > 95%
circumference. Light to moderate grazing, or lawns are OK. Points = 2
- No paved areas or buildings within 50m of wetland for >50% circumference.
Light to moderate grazing, or lawns are OK. Points = 2
- Heavy grazing in buffer. Points = 1
- Vegetated buffers are <2m wide (6.6ft) for more than 95% of the circumference (e.g. tilled
fields, paving, basalt bedrock extend to edge of wetland Points = O.
- Buffer does not meet any of the criteria above. Points = 1
Aerial photo showino buffers
H 2.2 Corridors and Connections (see p. 81)
H 2.2.1 Is the wetland part of a relatively undisturbed and unbroken vegetated corridor
(either riparian or upland)'that is at least 150 ft wide, has at least 30% cover of shrubs, forest
or native undisturbed prairie, that connects to estuaries, other wetlands or undisturbed
uplands that are at least 250 acres in size? (dams in riparian corridors, heavily used gravel
roads, paved roads, are considered breaks in the corridor).
YES = 4 points (go to H 2.3) NO = go to H 2.2.2
H 2,2.2 Is the wetland part of a relatively undisturbed and unbroken vegetated corridor
(either riparian or upland) that is at least 50ft wide, has at least 30% cover of shrubs or 1-
forest, and connects to estuaries, other wetlands or undisturbed uplands that are at least 25
acres in size? OR a Lake-fringe wetland, if it does not have an undisturbed corridor as in
the question above?
YES = 2 points (go to H 2.3) NO == H 2.2.3
H 2.2.3 Is the wetland:
within 5 mi (8kIn) of a brackish or salt water estuary OR
within 3 mi of a large field or pasture (>40 acres) OR
within 1 mi of a lake greater than 20 acres?
YES = 1 point NO = 0 ooints
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Wetland Rating Form - western Washington
version 2
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Wetland name or number A
H 2.3 Near or adiacent to other Drioritv habitats listed bv WDFW (see p. 82)
Which of the following priority habitats are within 330ft (100m) of the wetland unit? NOTE: the
connections do not have to be relatively undisturbed.
These are DF.W definitions. Check with your local DFW biologist if there are any questions.
V Riparian: The area adjacent to aquatic systems with flowing water that contains elements of
both aquatic and terrestrial ecosystems which mutually influence each other.
_Aspen Stands: Pure or mixed stands of aspen greater than 0.8 ha (2 acres).
_Cliffs: Greater than 7.6 m (25 ft) high and occurring below 5000 ft.
_Old-growth forests: (Old-growth west of Cascade crest) Stands of at least 2 tree species,
forming a multi-layered canopy with occasional small openings; with at least 20 trees/ha (8
trees/acre) > 81 cm (32 in) dbh or > 200 years of age.
_Mature forests: Stands with average diameters exceeding 53 cm (21 in) dbh; crown cover
may be less that 100%; crown cover may be less that 100%; decay, decadence, numbers of
snags, and quantity of large downed material is generally less than that found in old-
growth; 80 - 200 years old west of the Cascade crest.
_Prairies: Relatively undisturbed areas (as indicated by dominance of native plants) where
grasses and/or forbs form the natural climax plant community.
_Talus: Homogenous areas ofrock rubble ranging in average size 0.15 - 2.0 m (0.5 - 6.5 ft),
composed of basalt, andesite, andlor sedimentary rock, including riprap slides and mine
tailings. May be associated with cliffs.
_Caves: A naturally occurring cavity, recess, void, or system of interconnected passages
_Oregon white Oak: Woodlands Stands of pure oak or oak/conifer associations where
canopy coverage of the oak component of the stand is 25%.
_Urban Natural Open Space: A priority species resides within or is adjacent to the open
space and uses it for breeding andlor regular feeding; andlor the open space functions as a
corridor connecting other priority habitats, especially those that would otherwise be
isolated; and/or the open space is an isolated remnant of natural habitat larger than 4 ha (10
acres) and is surrounded by urban development.
_ Estuary/Estuary-like: Deepwater tidal habitats and adjacent tidal wetlands, usually semi-
enclosed by land but with open, partly obstructed or sporadic access to the open ocean, and
in which ocean water is at least occasionally diluted by freshwater runoff from the land.
The salinity may be periodically increased above that of the open ocean by evaporation.
Along some low-energy coastlines there is appreciable dilution of sea water. Estuarine
habitat extends upstream and landward to where ocean-derived salts measure less than
0.5ppt. during the period of average annual low flow. Includes both estuaries and lagoons.
_ Marine/Estuarine Shorelines: Shorelines include the intertidal and subtidal zones of
beaches, and may also include the backshore and adjacent components of the terrestrial
landscape (e.g., cliffs, snags, mature trees, dunes, meadows) that are important to shoreline
associated fish and wildlife and that contribute to shoreline function (e.g., sandlrock/log
recruitment, nutrient contribution, erosion control).
If wetland has 3 or more priority habitats = 4 points
If wetland has 2 priority habitats = 3 points
Ifwetland has 1 priority habitat = 1 point No habitats = 0 points
Note: All vegetated wetlands are by definition a priority habitat but are not included in this
list. Nearby wetlands are addressed in question H 2.4)
Wetland Rating Form - western Washington
version 2
August 2004
16
Wetland name or number ~
H 2.4 Wetland Landscape (choose the one description of the landscape around the wetland that
bestfits) (see p. 84)
There are at least 3 other wetlands within Y2 mile, and the connections between them are
relatively. undisturbed (light grazing between wetlands OK, as is lake shore with some
boating, but connections should NOT be bisected by paved roads, fill, fields, or other
development. points = 5
The wetland is Lake-fringe on a lake with little disturbance and there are 3 other lake-fringe
wetlands within Y2 mile points = 5 3
..( There are at least 3 other wetlands within Y2 mile, BUT the connections between them are
disturbed points = 3
The wetland is Lake-fringe on a lake with disturbance and there are 3 other lake-fringe
wetland within Y2 mile points = 3
There is at least 1 wetland within Y2 mile. points = 2
There are no wetlands within Y2 mile. points = 0
------
H 2. TOTAL Score - opportunity for providing habitat I ~ I
Add the scores from H2.1,H2.2, H2.3, H2.4
------
TOTAL for H 1 from page 14 15
-----
Total Score for Habitat Functions - add the points for H 1, H 2 and record the result on 2-3
p. 1
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Wetland Rating Form - western Washington
version 2
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