Wetland Inventory (2)1
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gyn... ~\.,- ~ v.
THE SOOT ~OMPANy
Wetland and Wildlife Consulting Services
416 Washington Streel SE, Suite 202
Olympia, WA 98501
(360)352-9897
(360) 352-9914 fax
cootco[iilolvwa net
WETLANDS INVENTORY
FOR
THE PURVIS PROPERTY
A portion of S23/24 T17N R1E
Thurston County Tax Parcels #21723130000, #2173140000
Thurston County, City of Yelm
AUGUST 2007
REVISED OCTOBER 2007
prepared for:
Tahoma Terra, LLC
P.O. Box 627
Rainier, WA 98576
prepared by:
Steve Shanewise, PW5
Senior Ecologist
.. _..., s
~:: ~ ,~ .,
000994 _
purvisocTa inv. doc
CONTENTS
Figure l: Vicinity Map
Introduction ........................................................... ................. l
Methods ................................................................. .................2
Results ................................................................... .................3
Table 1. Wetlands/Stream Summary ............... .................4
Discussion ............................................................. .................5
Figure 2: Surveyed Wetlands Map
Figure 3: Soil Survey
Appendix I: Wetland Descriptions
Appendix II: Soil Data Sheets
Appendix III: Category Rating Forms
References
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521I24T77NR7E
-All locations approximate-
PURVIS PROPERTY
VICINITY MAP
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FIGURE 1
INTRODUCTION
' This report documents the wetland and stream conditions on approximately 53 acres of
property within the City of Yelm. The property occurs primarily along the eastern edge
of a plateau above Thompson Creek, but also includes a small extension to [he east that
crosses the creek channel. The property currently has minor livestock grazing within the
portion along Thompson Creek; the rest of the property has several single-family homes
that have no agricultural activities. Seven wetland or stream systems have been identified
' for this property. A single stream, Thompson Creek, occurs within a ditched native
channel crossing the property extension in the northeast comer. Six wetlands occur along
t the western property portion, two of them in a large, connected complex that drains north
[o an eventual off-property connection to Thom
son Creek
Th
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e rema
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aze all small, isolated systems in shallow depressions; three of these wetlands are below
the minimum jurisdictional size for regulation (1000 sq ft). Detailed descriptions of the
wetlands aze provided in an Appendix, and include soil pit and category rating
information.
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PURVIS WETLAND INVENTORY
THE COOT COMPANY -~.
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METHODS
' Field Review
Field review of this property was performed in January and March 2007. All azeas of the
t property were traversed on foot while searching for wetland conditions. In addition,
topographic maps were used to locate depressional areas, and aerial photographs were
used to identify unusual vegetation signatures. Al] such features were specifically
' reviewed on the ground for wetland conditions.
Wetland Classification
Wetland characteristics are described within this report according to the U.S. Fish and
Wildlife Service Cowazdin Classification System (1989).
Wetland Delineation
' Most delineation work was accomplished in the mid-winter/early spring wet season to
afford good interpretation of wetland hydrology. Wetland delineation followed a Routine
Methodology based on the Washington State Wetland Identification and Delineation
' Manual (1997), requiring positive indicators for wetland soil, hydrology, and plants:
' • Wetland hydrology was determined by water conditions in pits.
• Presence of hydric soil was determined by soil conditions in pits dug azound
' suspected wetlands. Soil inspection included comparison with the Munsell Color
Charrs (]992). Genera] soil chazacteristics were derived from information contained
within the Soil Survey ofThurstan County, Washington (1990).
'
• Occurrence of wetland vegetation was determined through species identification,
estimation of dominance, and then assignment of wetland indicator status. Indicator
' status was assigned based upon the National List of Plant Species That Occur In
Wetlands (1988), Supplement (1993).
State Category Rating
The Washington State Wetlands Rating System for Western Washington Revised (2004)
was used to establish Category Ratings for the wetlands (Ecology Publication #04-06-
025).
Wetland Buffers
W
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et
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buffer widths were developed by following the City of Yelm Municipal Code
Chapter 14.08, specifically Ordinance #833.
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PURVIS WETLAND INVENTORY
THE COOT COMPANY - 2 -
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RESULTS
t PROPERTY OVERVIEW
' Variable Landscape Structure
This property contains two primary landscape structures. The main body of the property
to the west is situated at the edge of a headland plateau that rises above the Thompson
t Creek "valley" to the east. All land within the plateau azea is positioned well above any
floodplain or flooding issues associated with Thom
son Creek
p
.
Minimal Agricultural Use
Portions of this property may have been used for livestock grazing in the past. Grazing
of cattle still occurs within the northeastern property portion that extends across
' Thompson Creek. Abandoned farm buildings in the south-central part of the property
may have been used in the past for raising domestic poultry.
' Existing Single Family Homes
The property currently supports a handful of single-family homes situated primarily
along the east rim of the bluff descending to Thompson Creek. These homes are
' accessed by a driveway extending west from the west end of Berry Valley Road.
Excavated Basin
An excavated basin occurs west of the abandoned farm building mentioned above. This
' basin may have been dug to accept runoff From the fazm buildings (piping and concrete
troughs connect the two), and acted as a sort of "sewage pond" for whatever animals
' were housed in the abandoned buildings. Although fairly deep and large, this basin
maintains no wetland characteristics, and is a purely upland feature.
WETLANDS
t Well Drained Soils
Neazly al] of this property contains well-drained, upland soils (Everett, Nisqually,
Spanaway). Only a small portion of hydric soils occurs along the west boundary where it
' is associated with a large wetland complex.
Large Wetland Complex
' The western edge of this property engages a small portion of a large wetland complex
(Wetlands 1 and 2) off-properly to the west. This complex represents the headwater
beginning to a drainage route [hat heads north until it eventually connects to the
' Thompson Creek channel.
Small Isolated Wetlands
' Four, small, isolated wetlands occur in the west-central part of the property that are all
similar in habitat strneture. Only one of these systems (Wetland 3) is large enough to be
regulated with a buffer; the remaining three (Wetlands 4, 5 and 6) are below
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PURVIS WETLAND INVENTORY
' THE COOT COMPANY -3-
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jurisdictional size for buffers. Details for these four wetlands aze provided within a
single description in Appendix I of this report.
Thompson Creek System
The Thompson Creek channel crosses the northeast portion of this property. The native
channel in this location has been partially ditched in the past. The OHWM for [his
system occurs at the top edge of the abrupt channel edge on both sides. Although the
channel is partially vegetated below the OHWM, the system should be considered a
°stream" rather than a "wetland". Surface waters from winter flooding extend east of the
channel into the nearly flat floodplain ground here, but do not extend [o the west more
than a few feet due to the rise in ground elevation on this side of the channel. Thompson
Creek has no potential for anadromous fish use via its connection [o the Nisqually River
due to a massive erosion "blow-out" north of Hwy 510 that has created an impassible
barrier many, many feet high.
Table 1. Wetlands/Stream Summary
Wetland Size Category listing/ Buffer
Habitat pts
1 -8.50 acres III / 23 150'
2 -1.9 acres I / 21 150'
3 7,730 sq fr I[I / 14 80'
(0.18 acres)
4 665 sq fr
III / 14
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(0.02 acres)
5 400 sq fl
III / 14
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(0.01 acres)
6 808 sq fr IIU 14
(0.02 acres)
Thompson
Creek Type 3 150'
PURVIS WETLAND INVENTORY
THE COOT COMPANY -4-
DISCUSSION
1 Buffer Averaging Potential
Wetland buffers extending east from Wetland 1 and 3 have i
l
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B
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rregu
ar e
ges.
ot
systems
have law sensitivity [o disturbance, and performing buffer averaging at both locations
would be appropriate. The buffer on Wetland 1 could be averaged to create a straight
edge that would parallel the edge of development. With Wetland 3, the sharp point of the
buffer could be pulled back, with additional buffer then added where it would provide
some protection for Wetland 4. Both buffer adjustments could easily be made while still
1 maintaining a buffer azea equal to that of the unadjusted buffer.
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' PURVIS WETLAND INVENTORY
THE COOT COMPANY - 5 -
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S23/24T77NR1E
Partial Description:
33 =Everett very gravelly sandy loam
65 =McKenna gravelly sandy loam
74 = Nisqually loamy fine sand
111 = Spanaway gravelly sandy loam
126 = Yelm sandy loam
127 = Yelm sandy loam
-All locations approximate-
PURVIS PROPERTY
SOIL MAP
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TBE ~OOT~~tlY
FIGURE 3
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APPENDIX I: WETLAND DESCRIPTIONS
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WETLANDS INVENTORY
FOR THE
PURVIS PROPERTY
AUGUST 2007
t WETLAND 1
' SIZE: _ 8.5 Aeres
LANDSCAPE POSITION
' Wetland 1 is a Depressional, Outflow system that represents the headwater beginning to a
continuous drainage route eventually connecting to Thompson Creek.
' CLASSIFICATION
Wetland 1 has been drained in [he past with a lazge, deep, centralized ditch that probably
reduced persistent surface water levels by 2 to 3 feet Existing conditions support a range
1 of habitats, with emergent and shmb communities in the "lower" portions of the wetland,
while forested conditions occur in the `-upper' portions. Primary hydrology is saturated
ground, with only temporazy, shallow surface water during major storm events.
'
Cowazdin Dominant Veeetation
PALUSTRINE Popu[us trichocarpa
' Forested, Broad-Leafed Deciduous Thuja plicate
Scrub-Shrub, Broad-Leafed Deciduous Spiraea douglasii
Saturated to Seasonally Flooded, Fresh Rosa pisocarpa
' Mineral Phalaris arundinacea
Ditched Agrastis tennis
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BOUNDARY DELINEATION
Most of the Wetland 1 boundary is moderately distinct, but past drainage activities have
' created a fringe of "effectively drained" Bound azound the entire perimeter. Because of
this condition, delineation was performed in March 2007 and relied heavily on the
t presence or absence of water or saturated soil within test pits. The southern, forested
portion of the wetland contains a hummocky ground topography that translates into a
mosaic condition where low spots aze wetland and high ones aze upland. Wetland 1 is
' primazily associated with a formation of hydric, McKenna soil. The following table
depicts general field indicators used to delineate the Wetland boundary:
WETLAND UPLAND
Carex obnupta Cytisus scaparius
' 2 chroma 3+chroma
water in pit dry it
BOTH
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PURVIS WETLAND DESCRIPTIONS-APPENDIXI
THE COOT COMPANY
FUNCTION ASSESSMENT
' Following is a list of commonly recognized wetland functions, with an estimated relative
value rating for this wetland and a brief conceptual statement regarding the primary
factor affecting this rating. A summazy table is also provided for quick reference.
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H7GH MODERATE LOW NOT
APPLICABLE
2 1 4 1
Plant/Animal Habitat Valoe HIGH Three habitat classes provide high
structural diversity.
Sediment Capture HIGH Dense emergent and shrub growth.
Surface Water Runoff Route MOD Headwater beginning to minor
tributary to Thompson Creek.
Biofiltration LOW Minimal persistent surface water due
to ditching.
Groundwater Recharge LOW Underlying poorly drained soil;
Minimal surface water persistence
due to ditchin .
Stormwater De[enfion LOW Ditched outlet with no constriction.
Surface Water Supply LOW Only seasonal surface water
dischazge.
Flood Attenuation NA Not associated u~th a Riverine
system.
CATEGORY RATING: II[ (47 pts)
This wetland qualifies for a Category III rating with a Habitat Function score of 23 pts.,
requiring a 150' buffer pursuant to the Yelm Municipal Code.
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Score for Water Qualit Functions 10
Score for H drologic Functions 14
Score for Habitat Functions 23
TOTAL Score for Functions 47
' PURVIS WETLAND DESCRIPTIONS-APPENDIXI
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fHE COOT COMPANY
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WETLAND 2
SIZE: ~1.9 Acres
LANDSCAPE POSITION:
This wetland is a depressional, Outflow system that represents the outfall route from
Wetland 1.
CLASSIFICATION
This wetland represents the outlet drainage route for Wetland 1. The original, native
outlet route is now an abandoned channel where the upper portion has been altered (filled
in) by past earthwork. An artificial channel was excavated to replace the abandoned
channel, probably in association with the ditching of Wetland 1. Both swales support a
mixture of shrub and emergent communities across their width, with a mazgin of mostly
tall trees that create a closed canopy overhead. The abandoned charnel now supporcs
pockets of shallow surface water while the artificial channel sustains seasonal, shallow
sheet-flow draining from Wetland 1. The small pond is e permanent water feature that
vanes significantly in depth from winter to summer. Where the two Swale portions of
this wetland connect, the system then turns into a Category I Mature Forested condition
that continues to the north property line dominated by large black cottonwood and
Oregon ash trees. North of [he project property, the wetland occurs as an actively
grazed, cleared emergent pasture dominated by a saturated soil hydrology.
Cowardin Dominant Vegetation
PALUSTRINE Fraxinus latijolia
Forested, Broad-Leafed Deciduous Populus trichocarpa
Emergent, Persistent Physocarpus capita[us
Saturated to Seasonally Flooded, Fresh Symphoricarpo.s albu.s
Mineral Ranunculus repens
Oenanthe sarmentasa
Graminoid spp.
PURVIS WETLAND DESCRIPTIONS-APPENDIX I
' THE COOT COMPANY
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BOUNDARY DELINEATION
All wetland edges associated with the Wetland 2 system aze distinct boundazies generally
identified by a brief, abrupt rise Prom the geuerally level Swale bottom into the adjacent
upland landscape. The following table depicts general field indicators used to delineate
this wetland boundary:
WETLAND UPLAND
Oenanthe sarmenmsa Polystrchum munitum
1 chroma 2+ clvoma
saturated to surface drv nit
BOTH
Fraxinus latifolia
Symphoricarpos albus
Physocarpus capitatus
PURVIS WETLAND DESCRIPTIONS-APPENDIX I
THE COOT COMPANY 4
FUNCTION ASSESSMENT
' Following is a list of commonly recognized wetland functions, with an estimated relative
value rating for this wetland and a brief conceptual statement regarding the primary
factor affecting this rating. A summazy table is also provided for quick reference.
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HIGH MODERATE LOW NOT
APPLICABLE '~
2 2 3 1
Plant/Animal Habitat Value HIGH Diverse plant community with
emergent, shrub and forest species.
Surface Water Runoff Route HIGH Outlet for Wetland l; continuous
drainage eventually connecting to
Thom son Creek.
Bio5ltration MOD Shallow, sheet-flowing surface water
through mostly dense emergent
row[h.
Sediment Capture MOD Mostly dense emergent growth with
shallow, sheet-flowing surface
water.
Surface Water Supply LOW Only seasonal surface water outlet.
Groundwater Recharge LOW Minimal, persistent, non-flowing
surface water.
Stormwater Detention LOW Minima] depressional structure.
Flood Attenuation NA Not associated with a Riverine
system.
CATEGORY RATING: I (40 pts)
This wetland qualifies for a Mature Forest Category I rating with a moderate level of
Habitat Function (21 pts), requiring a ] 50' buffer pursuant to the Yelm Municipal Code.
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Score for Water Qualit Functions 9
Score for Hydrolo is Functions 10
Score for Habitat Functions 21
TOTAL Score for Fuuctious 40
PURVIS WETLAND DESCRIPTIONS-APPENDIXI
t THE COOT COMPANY
WETLAND 3, 4, 5, 6
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S[ZE: Wetland 3: 7,730 sgfr (O.18ac)
Wetland 4: 665 sgft (0.02ac)
Wetland 5: 400 sgfr (O.Olac)
Wetland 6: 808 sgft (0.02ac)
LANDSCAPE POSITION
These four wetlands are all Depressional, Closed systems set within shallow basins along
' benches in a gently sloped landscape.
CLASSIFICATION
These small to very small wetlands are mostly shrub dominated, shallow basins with
temporary to seasonal surface water conditions. Under existing conditions, these systems
have no surface water outfall although extreme high water conditions could cause
' temporary overland sheetflow to either Wetland 1 or 2. The wetlands lack snags or
woody debris.
' Cowardin Dominant Vegetation
PALUSTRINE Spiraea douglasii
' Scrub-Shrub, Broad Leaved Deciduous Rosa pisocarpa
Temporary to Seasonal Flooding, Fresh Fraxinus [atifolia
Mineral Phalaris arundinacea
' Drained
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BOUNDARY DELINEATION
Most of the wetland boundazies for these systems were fairly distinct and occurred where
the ground rose abruptly for a few inches from an otherwise flat basin bottom. Soils were
either darker, or heavily mottled within the wetland, and upland vegetation formed a
mostly clear edge a[ the delineated boundary. The following table depicts general field
indicators used to delineate the wetland boundazy:
WETLAND UPLAND
1 chroma
Water in pit
Gau[thena sha[lon
2 chroma
BOTH
Spiraea douglasii
EveretUYelm soils
PURVIS WETLAND DESCRIPTIONS-APPENDIXI
THE COOT COMPANY
FUNCTION ASSESSMENT
' Following is a list of commonly recognized wetland functions, with an estimated relative
value rating for this wetland and a brief conceptual statement regarding the primary
factor affecting this rating. A summary table is also provided for quick reference.
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HIGH MODERATE LOW NOT
APPLICABLE
2 1 4 1
Groundwater Recharge HIGH Depressional basins with no outlets
over porous soils
Sediment Capture HIGH Closed basins with no surface water
outlets.
Stormwater Detention MOD Depressional basins with no outlets,
but small very small watersheds.
Biofiltration LOW Only temporary to seasonal surface
water persistence.
Plant/Animal Habitat Value LOW Small size; low structural diversity,
limited surface water presence
Surface Water Runoff Route LOW Closed basins with no surface water
outlets.
Surface Water Supply LOW Closed basins with no surface water
outlets
Flood Attenuation NA Not associated with a Riverine
system
CATEGORY RATING: III (50 pts)
These wetlands all qualify for a Category III rating with a Habitat Function Score of 14
points. Wetlands 4, 5 and 6 aze below the jurisdictional size limit (1,000 sq fr) far
regulation by the City of Yelm; Wetland 3 requires an 80' buffer.
Score for Water Qualit Functions 12
Score for H drolo is Functions 24
Score for Habitat Functions 14
TOTAL Score for Functions 50
' PURVIS WETLAND DESCRIPTIONS-APPENDIX I
THE COOT COMPANY
APPENDIX II: SOIL DATA SHEETS
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WETLANDS INVENTORY
FOR THE
PURVIS PROPERTY
AUGUST 2007
1 IN-PIT
' DATA FORM
ROUTINE ONSITE DETERMINATION ME'PHOD
!WA State Wefland Delineation nr 19R7 Coros Wetland Delineation Manuall
Projeo[/Site: Purvis Property Dale: March 2007
Applicant/Owner Tahoma Ten'a LhC County 'fhurslon
Slats LVA
Field lnvosti ator (s): S. Shenewise S/T/R: 23,24lTI7/RIE
Do Normal Circumstances exist a[ the sitel Yes Cammm~ity ID: I-IN
Is the site significantly disturbed? No Transect ID:
Is [he area a potential Problem Area? No Plo[ [D:
Explanation ofatypical or problem area:
VEGETATION
Dominant Plm¢Species Indicator Stratum
1. Spiraea dnuglasii FACW S
2. Rosa pisocmprr PAC S
3. Phalaris artrndinacea FACW FI
HYDROPHYTIC VEGETATION INDICATORS:
Percent of dominant species that are OBL, FACW, an d/or FAG: >50
Indicators that aPPIY~
Regional knowledge of plan[ communities: X Wetland plant list X
PhysiologicaVreproduc[ive adapmtions: Morphological adaptations:
Technical hiterature: Wetland plan[ Dala Hase:
Other:
Hydrophy[ic vegetation present? Yes
Rationale/Remarks: Dominant spp. FAC and wetter.
HYDROLOGY - -
Saturated in lJpper 12"
Is it the growing season?: Yes
Haled on: March
Oxidized Roo[ Channels < 12"
Depth [o free wflter in pit:
De th m saturated soil: Q2"
Stream, lake, or gauge data: Other
Aerial photographs:
Wetland hydrology present? Yes
Rationale/Remarks: Approved hydrology indicators p resent _
SOILS
Map Unit Name: McKenna gravelly sill loam Drainage Class: PD
(Series & Phase)
Taxomm~y (subgroup): loamy skeletal, mixed, nonacid, mesic Mollic 1{aplaquepts
Field observations confirm mapped type? Unconfirmed
ProlSle Description
neprh hlorizon Mavixcolor M1follle colors M1(ortleabrmJame Tezrvre/ Drawir,yofsoil
(iocaenl (Mansell) (Muwolll su/oonlnsi eln,GVU, nIC, pmfilc (mnlcl,
dea~npima/
0~ 12 I OYR2/2 many faint IOYRS/8
Hydric Snil Utdicators
Listed on Local Lisl
Reducing Conditions
Listed on National List
Hydric soils present? Yes
Rationale for decision/Remarks: 2 chroma/wmoRles
WETLAND DETERMINATION
Hydrophytic vegetation present? Yes
Hydric Soils presem? Yes
Wetland Hydrology present? Yes Is Sampling Pain[ within a wefland7Yes
Rationale/Remarks: Positive Cor ell 3 parameters
NOTES:
,.
TAE SOOT ~OMPAIry
w.a..e..e wnnu. er.r.rr
1 OUT-PIT
DATA FORM
ROUTING ONSITE DETERMINATION METHOD
(WA Stnte We[lend Delineation or 1957 Coros Wetland Delineation ManuaD
ProjecUSite: Purvis Property Dale: March 2007
Applicant/Owner 'fahoma Terra LLC County: Thurston
State: WA
Field Investi amt(s): S. Shanewise SIT/R: 23,24/T 17/RIE
Do Normal Circwnstances exist at the site? Yas Community ID: ]-OUT
Is the site significantly disturbed? No "fransect ID:
is the area a potential Problem Areal No Plol ID:
Explanation of atypical or problem area:
VF.G F.TATION
Dominant Plant Speeies Indicator Strntum
1. L}Itisus scoparius UPL S
2. P.reudotsaga menziesii FACU T
3. Rhamnus put'shiana FAC T
4. Pteridium aguilinum FACU H
HYDROPHYTIC VEGETATION INDICATORS:
Percent of dominant species That are OBL, FAC W, and/or FAQ <50
indicators that apply:
Regional knowledge of plan[ communities X Wetland plan[ list X
Physiological/reproductive adaptations: Morphological adaptations:
Technical Literature: Wetland plan[Dala Rase:
Other:
Hydrophy4ic vegotnlion present? No
Rationale/Remarks: Dominant spp. FAC-U
HYDROLOGY
NONE
Depth to free water in pit
De th to saturated soil:>12"
Stream, lake, or gauge data: Olher:
Aerial photographs:
Wetland hydrology present? No
Ra[ionale/Remarks: Na presence or indication of wetl and hydrology.
SOILS
Map Unit Name: Everett very gravelly sandy loam Drainage Class: SED
(Serias& Phase)
Taxonomy (subgroup): sandy skeletal, mixed, mesic Andic Xerochrepts
Field observations confirm mapped type? Unconfirmed
Profile Description
nePlh nonzon Mem wlor Mmik mlorr Monlc e4unJnnoa TmuN
(inoLas) (Munvelp (MnnsellJ size/conlresi simdure,em
0-33 I OYR3/3
312 IOYR3/4 none
Hydric Soil (ndicarolre
NONB
Hydric soils present? No
Rationale Cor decision/Remarks: No indicators
W F.TLAND DETERMINATION
Hydmphytic vegetation present? No
Hydric Soils present? No '
Wetland hydrology presem?No Is Sampling Poinnvitllinawe(land?No
Rationale/Remarks: Negative for all three parameters
NOTES:
THE ~OOT~OMPANy
wm..~e.ve wmun ei.i.e.
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ r e~ ~ ~ ~ ~
2 IN-PIT
DATA FORM
ROUTIRE ONSITE DCTERM[NAT[ON METHOD
tWA State Wetbrnd Delineation or 1987 Coros Wetland Delineation Manual)
Project/Site: Purvis Property Date: Maroh 2007
Applicant/Owner: Tahoma Terra LLC County: Thurstmr
State: WA
Field Invas[i ator (s): S. Shanewise S/T/R: 23,24/T17/RIE
Do Normal Circumstances exist at the site? Yes Community ID: 2-IN
Is the aite significantly disturbed? No Transact ID:
Is the area a potential Problem Areal No Plot ID:
Explanation of atypical or problem area:
VEGETATION
Unminan[ Flant Species Indicator Stratum
1. Frnxinus latifo[ia FACW T
2. Physocmpers cnpitatus FACW- S
3. Oenanthe sarmenmsa OBL E
4. Ranurvculus repens FACW hI
5. Symphw~icarpos albus FACU S
HYDROPHYTJC VEGETATION INDICATORS :
Percent of dominant species that are OBL, FACW, and/or FAC: >50 °/a
Indicators that apply:
Regional knowledge of plan[ conununi[ies: X Wetland plant list X
Physiological/reproductive adaptations: Morphological adaptations'.
Technical Lite~ahve: Wetland plant Date Hasa:
Other:
Hydrophy[ic vegetation present? Yes
Rmionale/Remarks: Dominant spp. FAC and welter.
HYDROLOGY
SaturateA in Upper 12"
Drainage Pa¢ems
Is jt the growing season?: Yes
Based om Memh
Oxidized Rool Channels < 12"
Deptll ro Cree water in pir. b"
De th to saturated soil: 0"
Stream, lake, or gauge data: Other:
Aerial photographs:
Wetland hydrology present? Yes
Rationale/Remarks: Approved hydrology indicators present
SOILS
Map Unil Name: Yelm fine sandy loam Drainage Class: W D
(Series & These)
Taxonomy (subgroup): Medial, mesic Aquic Dyslric Xerochrepts
Field observations confirm mapped rypa7 Unconfirmed
Profile llescription
Darn Hndmn Mena cnNr Monln rnlmd MolaeaD~maenw Tuuud nawiny of roll
(IncLcs) (Munsel9 (Mnmelp siss/conrcuw simceire, ae pmfila (mvicL
d.,nfn~mnl
012 IOYR2/I
Hydric Snil Indiurtors
Reducing Conditions
Gleyed or Low-Chroma
Hydric soils present? Yes
Rationale for decision/Remarks- Ichroma
W CTLAND DETERMINATION
Hydrophy[ic vegetation present? Yas
Hydric Soils present? Yes
Wetland I'lydrology present? Yes Is Sampling Poim within a wetland? Yes
Rationale/Remarks: Positive Fm' all 3 parameters
NOTES:
,.~
TflE SOOT OMPAN~
w.n..e..e wnem. n.i.ar
2 OUT-PIT
DATA FORM
ROUTINE ONSITE DETERMINATION METHOD
(WA State Wetland Delioentinn nr I9fl7 Cnrns Wetland Delinea Finn Manuall
Project/Site: Purvis property Date: March 2007 I
ApplicnnUOwner: Tahoma Terra LLC County: Thurston
State: WA
Field htves[i a[or (s : S. Shenewise S/T/R: 23,24/T'17/RIE
Do Normal Ciroums[ances exist a[ the sire? Yes Community ID; 2-0UT
Is the site significantly dishuhed? No 'Pransect 1D:
[s the area a po[eotiel Problem Area? No PIotID:
Explanation of atypical or p~rohlem area:
VEGETATION
Dominant 1'Inn[ Species Indicator Stratum
I. Psetrdotsugn menaierri FACU T
2. Rubus discolor FACU V
3. dlnus• rethra FAC T
4. Sjmrphoricarpos albus FACU S
5. /'opulus hichocarpa FAC T
HYDROPHYTIC VECF.TATION INDICATORS :
Percent of dominant species that are OBL, PAC W, fin d/or FAC: c $0
Indicamrs that apply:
Regional knowledge of plant communities: X Wetland plant list X
Physiological/reproductive adaptations: Morphological adaptations:
Technical Literature: Wetland plant Data Base:
Other:
Hydrophytic vegetation present? No
Rationale/Remarks: Dominant spp. PAC-U
HYDROLOGY
NONE
Depth m free water in pit
De [h to sanuateJ soil:>I2"
Stream, lake, or gauge data: Other:
Aerial phomgraphs:
Wetland hydrology present? No
Rationale/Remarks: No presence or indication of wetland hydrology.
SOILS
Map Wfit Name: Yelm fine sandy loran Drainage Class: WD
(Series & Phase)
'Taxonomy (subgroup): Medial, mesic Aquic Dysb'ic Xemchrepts
Field observations confirm mapped type? Unconfirmed
Profile Description
ecp0i Honzon Meln'x color Motile colors Motile neonaena Tuinre/
(indiu) IMmm~lp (MnnsalU eiedcanirem smmuve, em.
0~5 I OYR3/3
5~ 12 I OYR2/2
Hydric boil Indicators
NONE
Hydric soils present? No
Rationale far decision/Remarks: No indicmors, 2 chroma, not mottles
W ETLgND DETERMINATION
Hydrophytic vegetation present? No
Hydric Soils present? No
Wetland Hydrology present? No Is Sampling Paint within a wetland? Nn
Rationale/Bemarks: Negative for all three pmameters
NOTES:
TAE SOOT ~OMPANy
w.n.~e.nf canna. e~omu
3,4,5,6 IN-PIT
DATA FORM
ROUTINE ONSITE UETCRMINATION METHOD
(WA State Wetland Delineation or 1987 Corps Wetland Delineation Manual)
Project/Site: Purvis Property Date: January 2007
Applicant/Owner Tahoina Terra LLC County: Thurston
Smote: WA
Eiold Investi a[or (s): S. Shanewise S/T/R: 23,24/TI7/RIE
Do Normal Circumstances exist at [he site? Ves Community IU: 3,4,5,6-IN
Is the site signifcantly disturbed? No Transact ID:
Is the area a potential Problem Area? No Plot IU:
Explanation of atypical or problem area:
VEf,ETA'f10N
dominant Plant Species Indicator Stratum
1. Spiraen douglasii FACW S
2. Rosa pisocarpn FAC S
3. Fraxinvs latijolra FACW T
4. Phalnris nrundinacea FACW H
HYDROPH YTIC VEGCTATION INf11CATORS :
Percent of dominant species that are OBL, FACW, an d/or FAG: >50 95
Indicators that apply:
Regional knowledge of plant communities: X Wetland plant list. X
Physiological/reproductive adaptations: Morphological adaptations:
Technical Literature: Wetland plan[ Data Rasa:
Other:
Hydrophytic vegetation presentl Yes
Rationale/Remarks: Dominant spp. PAC and wetter.
HYUROLOCY
Saturated in Upper 12"
Is it the growing season?: No
Rased on: January
Depth to free water in pit 8"
De th to BaRlreted Soil: 0"
Strewn, lake, or gauge date: Other:
Aerial photographs:
Wetland hydrology present? Yes
Rationale/Remarks: Approved hydrology indicators p resent
SOILS
Map Unit Name: Everett Urainage Class:
(Series & Phase)
'I'axonnnry (subgroup):
Pield observations confnn mapped type? Unconfirmed
Profile Description
naplh 1{ovizan Mnu oalao Molilo molars Molllevbnndonco Tcxpud niewin6 ofsol
(inoliu) (MUVdI) (Munsnlp xizeloommsi ilruowu.ero. Profile (maleb
nuPnPUaa>
0~4 IOYR2/2 none
412 IOYR2/1 none
Hydric Soil Indicators
Gle ed or Low-Chroma
Hydric soils prescnt7 Yes
Rationale for decision/Remarks: I Chroma
WETLAND DETEItM INA'1'ION
Hydrophytic vegetation presen[7 Yes
Hydric Soils present? Yes
Wetland hydrology present? Yes Is Sampling Pain[ within a wetland? Yes
Ralicnale/Remarks: Positive for all 3 parameters
NOTF,S:
TflE SOOT ~OMPANy
wal..e.~e wmur. eiover
~ ~ ~ ~ ~ ~ _ ~ ~ ~ ~ ~ ~ ~ r ~ a ~ ~
3,4,5,6 OUT-PIT
DATA PORM
ROUTINE ONSITE DCTERMINATION METHOD
WA State Wethmd Delineation nr 1987 Cor is We11anU Delineation Manual
Project/Site: Purvis Property Date: January 2007
Applicant/Owner: Tahoma Tcrre LLC County: Thurston
State: WA
Field Inveati etor (s): S. Shanewise S/T/R: 23,24/T 17/RIE
Do Nm'mel Circumstances exls[ aI the site? Yes Community ID: 3,4,5,6-OUT
is the site significantly disturbed? No Transact lD:
Is the area a potential Problem Areal No Plot [D:
Explanation of atypical or problem area:
VEGGTA'CION
Dominant Plant Species Indicator Stratum
1. Polysticham munitmn FACU S
2. Pseudotsnga merrziesii FACU T
7. Gnu[therra sha77an FACU* S
4. Phalaris arundinacea FACW H
HYDROPH YT[C VF,GETATION INDICATORS:
Percent of dominant species [hat are DBL, FACW, an d/or FAQ ~ 50
Indicators that apply:
Regional knowledge of plant communities: X Wetland plan[ list X
Physiological/reproductive adaptations: Morphological adaptations:
Technical Lilemnve: Wetland plant Data Base:
Other.
Hydrophytic vegetatiot present? No
Rationale/12emarks: Dominant app. FA6U
H YDI20LOGY
None
None
De th to saturated soil:>12"
Stream, lake, or gauge data: Other: -
Aerial photographs:
Wetland hydrology present? No
Rationale/Remarks: No presence or indication of wetland hydrology.
SOILS
Map Unit Name: Everett Drainage Class
(Series S+ Phase)
Taxonomy (subgroup):
Field observations confirm mapped type? Unconflnned
Profile Description
OapIL Horieon Mmn'x colo. Mollln mlurs Moyle abundance Taxwid
(ioebeai (Mmiselb (MUmelh size/cnntrnst 9lnimnl9, we.
0~5 10YR3@ none
5.912 JOYR2Y2 none
Ilydric Soil Indicators
None
HyUric soils presentT No
Rationale for decision/Remarks: 2 chroma no mottles
WETLAND DETCRMINATION
Hydrophytic vegetation present? No
Hydric Soils present'? No
Wetland Hydrology present? No Is Sampling Point within a wetland? No
Rationale/Remarks: Negative for all three parameters
NOTES:
TflE~~00T~OMPANy
wwl..a..e wilenr. mmaar
' APPENDIX III: CATEGORY RATING FORMS
1
1
1
1
1
1
1
1
1
1
1
1
WETLANDS INVENTORY
FOR THE
PURVIS PROPERTY
AUGUST 2007
1
1
Wetlmd name or number _I
DRAFT WETLAND RATING FORM -WESTERN WASHINGTON
Name of wetland (if known): Purvis Prooerty
Location: SEC: 23/24 TWNSHP: 17N 12NGE; l8 (Attack map with outline of wetland to rating form)
Person Ra[ing Welland: S Shanewise Affiliation: The Coot Compaq Dale of Site Visit: March 2007
DRAFT SUMMARY OF RATING
Catesory based on FUNCTIONS provided by wetland
I_ II_ ~_/ IV_
' Category I =Score >=70
Category II =Score 51-69
Category IH =Score 30-50
Cate
Or
N =S
< 30
R
v
core
u
1
1
1
Score for Water Quality Functions 10
Score for Hydrologic Functions 14
Score for Habitat Functions 23
TOTAL score for Fuuctions 47
Category based on SPECIAL CIIARACTERISTICS of wetland
I_ II_ Does not Apply_/
Wetland Ra[ing Form-western Washmgtnn
FIDaI CalegOry (choose the "highest" category 4om above)
Check the appropriate type and class of wetland being rated.
CWetTaud''T;}'Pe~`_.F~,-"~~
Estuarine '-"~' ~"='ila~Ade~I3ss'rw
^s~at
Depressional ~$;
r~F
/
Natural Herita a Wetland Riverine
Bow Lake-fringe
Mature Forest Slo e
Old Growth Forest Flats
Coastal La oo^ Freshwater Tidal
Interdunal
None of the above /
t
August 2004
1
1
Wetland name or number _I
=,D '~~epresstonaLand~FlatsWetlands '`.'~~ "` -''-"'"
, ' ~ zz ~.4~~ 'n~~~~~
W
E
I
~~
'
`
~ pp
Y }
.„
AT
RQIIAI;
,TY.y~FgUNC11IONSa
ndicaCOrsthattfie'~
et
]andunctxonstoi
„
.,~. P~3,. fi>.. i&E^,i1~••~" •X""-' ,y9 4-n
'
~
~ y
~ t-z~,~
^.r
~.~ ''
,q,
~.F+I' '"
r'k ^'
+a,
lm POVe3Waterx LLah~'~s'~B~a~~
a
~~^i ~~
„
-
n
er r ~. _.r
~. ".
D D 1. Does the wetland have the potential to improve water quality? (see p.38) x ~~ "•
'
D 1.1 Characteristics of surface water flows out of the wetland: sr tss~
Wetland is a depression with no surface water outlet points = 3
D Wetland has an intermittently flowing, OR highly constricted outlet points = 2 I
Wetland has an unconstricted surface outlet points = I
Wetland is flat and~has no obvious outlet and or outlet is a ditch oints = I
D L2 The soil2 inches below the surface is clay, organiq or smells anoxic
(hydrogen sulfide or rotten eggs) 4
D YES
points = 4
NO
ourts = 0
D 1.3 Characteristics of persistent vegetation (emergent, shrub, and/or forest class)
D Wetland has persistent, ungrazed, vegetation> = 95% of area points = 5
Wetland has persistent, ungrazed, vegetation> = I/2 of azea points = 3 5
Wetland has persistent, ungrazed vegetation > = 1/10 of area points = 1
Wetland has persistent, ungrazed vegetation <1/l0 of azea points = 0
D 1.4 Characteristics of seasonal ponding or inundation.
This is the area of the wetland that is ponded for at least 2 months
but dries out
D ,
sometime during the year. Do not count the area that is permanently ponded. 0
Estimate area w the average condition ~ out of (0 yrs.
Area seasonally ponded is > % total azea of wetland points = 4
Area seasonally ponded is>'/< total area of wetland paints = 2
Area seasonally ponded is < y total area of wetland points = 0
NOTE: See text or indicators o seasonal and ermanent inundation.
D Total for D 1 Add the points in the boxes above 10
D D 2. Does [he wetland have the opDOrtunity [o improve water quafity? (see p. 44)
Answer YES if you know or believe there are pollutants in groundwater or surface
water coming into dte wetland that would otherwise reduce water quality in
streams, lakes or groundwater downgradient from the wetland
Nate which of thefollowi
.
n
conditions provide the sources of pollutants.
- Grazing in the wetland or within I50 ft
- Untreated stormwa[er discharges to wetland
- Tilled fields or orchards within 150 8 of wetland
- A stream or culvert discharges into wetland that drains developed areas,
residential azeas, farmed fields, roads, or clear-cut logging
- Residential, urban azeas, golf courses are within 150 ft of wetland multiplier
- Wetland is fed by groundwater high in phosphorus or nitrogen
- Other I
YES multi tier is 2 multiplier is 1 _
~ D TOTAL -Water Quality Functions Multiply the score from Dl by D2 ]0
Add score !o table on . 1
W.ah..d Pa,ien c
' .. _.._.._.._ y ~~n-..wiuu rr av u,gw~ J Aaglls[2004
1
1
t
Wetland name or number 1
D Depi'esstonal and Fl
t
tl
`
a
s We
ands ,
~ ~ + r'Pmnts
yHYf?ROLOGIC FUNCTIONS .Indreato'rstthat thew land functions to iednce 'b
-'~~ s' ` ' °~
~
t .floodin an'd;sheam;d'e`gr`adatton
~~~ i
~~` ~~ P~it
LL
,`.
~w``` * :r ::,
_
_
;,
~
._
D 3. Does the wetland have the otential to redu
fl
di
ce
oo
ng and erosion?
see .4~
D D 3.1 Characteristics of surface water flows out of the wetland
Wetland has no surface water outlet
points = 3
Wetland has au intermittently flowing, or highly constricted outlet
oi
t
=2 1
p
n
s
Wetland is flat and has no obvious outlet and/or outlet is a small ditch points =1
Wetland has an unconstricted surface outlet
D oints = 0
D 3.2 Depth of storage during we[ periods
Estimate the height of ponding above the bottom of [he outlet.
Marks of ponding are 3 fr or more above the surface
points = 7
The wet9and is a "headwatef' wetland"
3
points = 5
Marks of ponding between 2 ft to < 3 h from surface
points = 5
Marks are at least 0.5 ft to < 2 ft from surface
points = 3
Wetland is flat but has small depressions on the surface that trap water points = 1
Marks of ondin less than OS ft oints = 0
D D 3.3 Contribution of wetland to storage in the watershed
Estimate the ratio of the area of upstream basin contributing surface water to the
wetland to the area of the wetland itse J
The area of the basin is less than 10 times the area of wetland
i
po
nts = 5
The area of [he basin is 10 to 100 times [he area of the wetland
3
points = 3
The area of the basin is more than 100 times [he area of the wetland
oi
t
= 0
p
n
s
Wetland is in the FLATS class (basin~(te wetland, b deFmition) oints = 5
D Total for D 3 Add the points in the boxes above 7
D D 4. Does the wetland have the opportunity to reduce flooding and erosion?
(see p. 49
Answer YLS if the wetland 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 comhtg 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 Welland is from groundwater.
Note which of the, following indicators of opportunity apply.
/Wetland is ht a headwate
f
i
r o
a r
ver or stream [hat has flooding problems
- Wetland drains to a river or stream [hat has flooding problems multiplier
- Wetland has no outlet and impounds surface runoff water that might otherwise
flow into a river or stream that has flooding problems
- Other
YES multiplier is 2 NO multi tier is 1
j~ TOTAL -Hydrologic Functions Multiply the score from D 3 by D 4 14
Add score to table on p. 1
Wetland Rating Form -wes[em Washington
August 2004
1
1
i
1
1
Wetland Warne or Dumber I_
iThese questtons apply to weitartds of a1Z,'HCrM et sa ses ~~~t; ° ~ ~ `~*.
t' ~ ~, ~ ~Polnts
,
"i c ~= ~ v ><~r ~' * ,.a s'r"v*' t -~ ` v' ` .S~x
EfASITAT'-~'IINCTIONS indtcatorstha~wetlan-dfimcttottsio.provide_unportant~habtta{ ~ ~. r
H 1. Does the wetland have the otenfial to provide habitat for many species? a ~`
H 1.1 Vegetation strueture (see p. 72)
Check the types of vegetation classes present (as defined by Cawardin)- if the class covers mare
than 10% of the area of the wetland or'/. acre.
-Aquatic bed
/Emergent plants
_/Scrub/shrub (areas where shrubs have >30% cover) 7
_/Forested (areas where trees have>30% cover)
_Forested areas have 3 out of 5 svata (canopy, sub-canopy, shrubs, herbaceous;
moss/ground-cover)
Add the number of vegetation structures that qualify. lfyou have:
4 structures or more points = 4
3 structures points=2
2 structures points= I
1 structure Dints = 0
H 1.2. Hvdrooericds (see p. 73)
Check the types of water regimes (hydraperiods) present within the wetland. The water
regime has to cover more than 10% of [he wetland or % acre to corm[ (see text jor
descriptions of hydroperiods)
-Permanently flooded or inundated 4 or more types present points = 3 I
/Seasonally flooded or inundated
_
3 types present points = 2
-Occasionally t7ooded or inuudated 2 types present poinC=1
_/Sa[urated only
_ Permanently Mowing stream or river in, or edjacent to, [he wetland
_ Seasonally [lowing stream in, or adjacent [q the wetland
_ Lake fringe wet[¢nd = 2 points
Freshwater fida! wetland = 2 points
H 1.3. richness of Plant Soec'es (see p. 75)
Count the number of plant species in the wetland [hat cover at least 10 ft~. (different patches
of the same epecies can be comhined !o meet the size threshold)
Yau do not have to name [be species.
'~ Do not include Eurasian I~Ifoil, reed canarygrass, purple loasesirife, Canadian Thistle
If you counted: > 19 species points =2
List epecies below if you want to: 5 - 19 species points = 1
<Sspecies points=0
I
w>aA„n a,e.,,, n,.~
..... .. ......... ~.....e..,.. .., August GUU4
1
1
1
1
1
1
1
Wetland name or number I
H 1.4. In[ersnersion of habitats (see p. 76)
Decide tinm The diagrams below whether interspersion between Cowardin vegetation
classes (described in H 1.1 ), or the classes and unvege[ated areas (can include open water or
mudflats) is high, medium, low, or none.
DOO O
None = 0 points Low = 1 point Moderate = 2 points
mss, s ~~'~'"
~.~ ~ ~ i T x ~ us'a~"
t r., ~ ~ ~ '
R\\
~x6
\
\~ .4
~- [riparian braided channels]
High = 3 points
NOTE: Ifyw have four or more classes or three vegetation classes and open water
Che rating is always high".
H 1.5. Special Habitat Features (see p. 77)
Check the habitat features that are present in [he wetland. The number ajchecks is [he
number of points you put into the next column.
_/Large, doomed, woody debris within the wetland (>4in. diameter and 6 ft long).
_/Standing snags (diameter at the bottom> 4 inches) in the wetland 2
Undercut banks are present for at least 6.6 ft (2m) and/or overhanging vegetation extends at
least 3.3 ft (Ltn) over a stream (or ditch) in, or contiguous with the wetland, for at least 33 ft
(1 Om)
-Stable steep banks offine materiel that might be used by beaver or musAra[ for derming
(>30degree slope) OR signs of recent beaver ac[iviTy are present (cur shrubs or n•ees [hat
have not yet turned grey brown)
A[ lent ``/<acre of thin-stemmed persistent vegetation or woody branches are present in areas
[ha[ are permanently or seasonally inundated. (structures for ege laying by amphibians)
Invasive plants cover less than 25 % of the wetland area m each stratum of plants
H 1. TOTAL Score - potential for providing habitat 8
Add the scores from codatmtt above
Comments
' Wetland Rafing Form ~ western Washington I4 August 2004
1
1
1
1
i
1
1
1
Wetland nama or number 1
H 2. Does the wetland have the opportunity Co provide habitat for many species'! ~~~~~,
H 2.1 Buffers (see p. 80)
Choose the description that best represents condition ojbuffer of wetland. The highest
scaring criterion that applies to the wetland is to be used in the rating. See text for
definition of "undisturhed."
/ l00 m (330ft) of relatively undisturbed vegetated areas, rocky areas, or open water >9~%
of circumference. No structures are within the undisturbed part of buffer. (relatively
undisturbed also means no-gazing) 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. Paints = 4
l00 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>
50% circumference. Points=3
If buffer does not meet xoy of the criteria above
- No paved azeas (except paved trails) or buildings within 25 m (80ft) of wetland> 95
circumference. Light to moderate gazing, or lawns are OK. Points = 2
No paved areas or buildings within SOm of wetland for>50% circumference.
Light to moderate gazing, or lawns are OK Points=2
Heavy gazing in buffer. Points = 1
Vegetated buffers are Qm wide (6.6ft) Eor more than 95% of the circumference
(e.g. tilled Eelds, paving, basalt bedrock extend to edge of wetland Points = 0.
- Buffer does not meet any of the criteria above. Points = 1
H 2.2 Corridors and Connections (seep. 81J
H 21.1 !s the wetland part of a relatively undisturbed and unbroken vegetated corridor
(either riparian or upland) [hat is at least I50 fr wide, has at least 36% cover of shrubs, forest
or native undisturbed prairie, [hat connects [o estuaries, other wetlands or undisturbed
uplands tlaat are at least 250 acres in size? (dams in riparian corridors, heavily used gravel
roads, paved roads, are considered breaks in the corridor). q
0=4 points (go to H2.3) NO=go to H2.2.2
H 2.2.2 Is [he wetland part of a relatively undisturbed and unbrokeu vegetated corridor
(either riparian or upland) that is at least SOfr wide, has at least 30% cover of
shrubs or forest, and connects to estuaries, other wetlands or undisturbed uplands
that are at least 25 acres m size? OR aLake-fringe wetland, if it does not have an
undisturbed corridor as in the question above?
YES=2 points (go to H2.3) N0=H2.2.3
H 2.23 [s the wetland:
within 5 mi (8km) of a brackish or salt water estuary OR
within 3 mi of a large field or pasture (>40 acres) OR
within l mi of a lake Beater than 20 acres?
YES = 1 oint NO = 0 oints
W I d
e[ an Ratmg Form-western Washmg[on
August 2004
1
1
1
1
1
1
1
1
1
1
Wetland uame or number _I
H 23 Near or adjacent [o other~rioriTy h b~tats list d by WDFW (see p. 32)
Which of the following priority habimts are within 330ft (100m) of the wetland?
(see text for a mare detailed description of these prtoriry habitats)
-/ Riparian: The area adjacent [o 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 Ip'eater than 0.8 ha (2 acres).
-Cliffs: Greater than 7.6 m (25 fr) high and occurring below 5000 ft.
Old-growth forests: (Old-growth west of Cascade crest) Stands of at least 2 tree species,
farming amulti-layered canopy with occasional small openings; with at least 20 trees/ha (8
trees/acre)> 81 em (32 in) dbh or> 200 years of age.
_Ma[nre 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-
erowth; 80 - 200 years old west of the Cascade crest.
-Prairies: Relatively undisturbed areas (as indicated by dominance of native plants)
where amasses aud/or fortis form the natucal climax plan[ community.
-Talus: Homogenous areas of rock rubble ranging in average size O.15 - 2.0 m (QS - 6.5 ft), I
composed of basalt, andesite, and/or 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 oaWconifer 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 [he
open space and uses it for breeding andlor regular feeding; and/or the open space
functions as' a comdor connecting other priority habitats, especially those that
would otherwise be isolated; and/or the open space is an isolated retnnant of natural
habitat larger than 4 ha (10 acres) and is surrounded by urban development.
_Estuary/Esmary-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 evaporndon. Along some low-energy coastlines [here is appreciable
diW[ion of sea water. Estuarine habitat extends upstream and landward [o where
ocean-derived salts measure less than O.Sppt. during the period of average annual low
flow. Includes both estuaries and lagoons.
Marine/Esmarine 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 [hat contribute to shoreline
fimction (e.g., sand/rock/log recrui[menY, nutrient contribution, erosion control).
If wetland has 3 or more priority habitats = 4 points
If wetland has 2 priority habitats = 3 points
If wetland has 1 prioriTy habitat = 1 point No habitats = 0 points
Wedand Rating Porm-western Washington 16 Auaus[2004
1
1
1
1
1
1
1
Wetland name or number 1
H 2.4 Wetland Landscan (choose the one description of the landscape around the wetland that
best fits) (see p. 84)
There are at least 3 other wetlands within'/, mile, and [he 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 5
lake-fringe wetlands within '/smile points = 5
There are at least 3 other wetlands within''/x mile, BUT the connections between
[hem are disturbed points = }
The wetland is Lake-fringe on a lake with disturbance and there are 3 other
lake-fringe wetland within % mile paints=3
There is a[ leas[ 1 wetland within % mile. points =2
There aze no wetlands within % mile. points=0
H 2. T01'AL Score - opportunity for providing habitat
Add the scores in the column above 15
Total Score for Habitat Fuuctlons -add the points for H 1, H 2 and record the result on 23
1
' Wetland Raiing Form -wesfem Washing on 17 August 2004
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Wetland name or number _2_
DRAFT WETLAND RATING FORM -WESTERN WASHINGTON
Name of wetland (if lmown): Purvis Property
Location: SEC: 23/24 TWNSIIP: 17N RNGE: lE (Attach map with outline of wetland to rating form)
Person Rating Wetland: S. Shanewise Affiliation: The Coot Comoanv Date of Site Visit:_March 2007
DRAFT SUMMARY OF RATING
Category based on FUNCTIONS provided by wetland
I II III / FV
Category I =Score >=70 Score for Water Quality Functions 9
Category II =Score 51-69 Score for Hydrologic Functions 10
Category HI =Score 30-50 Score for Habitat Functions 21
Category IV =Score < 30
TOTAL
f
F
i
40
score
or
unet
ons
Category based on SPECIAL CHARACTERISTICS of wetland
I_/_ II_ Does not Apply_
1 F1naI Calt'gOry (choose the "highest" category from above) ^
' Check the appropriate type and class of wetland being rated.
1
W t a1 ad~`L e~„:~'~y
Estuarine ~."'~g,.WettanilrC7a§"'s'`~.
Depressronal
/
Natural Herita a Wetland Riverine
Bo Lake-Erin re
Mature Forest / Slope
Old Growth Forest Flats
Coastal La oon Freshwater Tidal
Interdunal
None of the above
Wetland Rating Form-western Washington I
August 2004
1
1
1
1
t
t
1
t
W eland name ornumber -2
j~* ~~D~epr~esstonaLand Flat's Wetlands ~,•- ~ >~- ~ ~
e {+. ~~ t~fis'
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,
,
WAT~'iR
QUAL"I'I~~UNC$', ONS 'Indicators that thawetland4 tncnons to,v,; .
tm rove;.water, uahty ~• ~"~~~~.~~ .:.-_.`u ~ x p "'
r~ x ...
D D 1. Does the wetland have the potential to improve water quality? (see p.38)
.'..
~`'~-'
s
D L I Characteristics of surface water Flows out of [he wetland:
Wetland is a depression with no surface water outlet points = 3
D Wetland has an intermittently flowing, OR highly constricted outlet points = 2 7
Wetland has an uneonstric[ed surface outlet points = t
Wetland is flat and has no obvious outlet and or outlet is a ditch oints = I
D 1.2 The soil 2 inches below the surface is clay, organic, or smells anoxic
(hydrogen sulfide or rotten eggs)
~ YES points=4 0
NO oints = 0
D 7 S Characteristics of persistent vegetatio¢ (emergent, shrub, and/or forest class)
Wetland has persistent, ungrazed, vegetation > = 95 % of area points = 5
D Wetland has persistent, ungrazed, vegetation > = 112 of area Pointe = 3 ~
Wetland has persistent, ungrazed vegetation > = 1/10 of area points = 1
Wetland has persistent, u¢grazed vegetation 4/10 of area points = 0
D1.4 Characteristics of seasonal ponding or inundation.
This is [he area of the wetland that is ponded jar at least 2 months, but dries out
D sometime during the year. Do no! count the area [hat is permanently ponded.
Estimate area as the average condition 5 out of !0 yrs. ~
Area seasonally ponded is> % total area of wetland points = 4
Area seasonally ponded is > Y total area of wetland points= 2
Area seasonally ponded is <'/, total area of wetland points = 0
NOTE: See text or indicators o seasonal and ermanent inundation.
D Total for D 1 Add the points in the boxes above 9
D D 2. Does the wetland have the opportunih [o improve water quality? (see p. 44)
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 [he wetland- Nate which of the fo[lowin
conditions provide the sources of pollutants.
- Grazing in the wetland or within 150 h
Untreated stormwater discharges to wetland
- Tilled fields or orchazds within 150 ft of wetland
- A stream or culvert discharges imo wetland [ha[ drains developed areas,
reside¢tial areas, farmed fields, roads, or clear-cut logging
Residential, urban areas, golf courses are within 1 i0 ft of wetland multiplier
Wetland is fed by groundwater high in phosphorus or nitrogen
- Other -I
YES multiplier is 2 O multiplier is 1
D TOTAL -Water Quality Funcfions Multiply the score from Dl by D2 9
Add score to table on
Wetland Rating Form-western Washington 5 August 2004
1
1
t
r
Wetland name or number _2_
Depresstonal and Flats Wetlands ~ ~ ~ ~ `
-- Pmnts ~~
~
HYDROLOGIC~JNCi`IOLVS Indtcators,that the wetland functions to reduce
~ ~ ~~
,
- ,';flooding andsiream 8e adahon 2 _
h
~ -° ~l`¢` 's~'L`:
- s °`
~
_
_ _ _
a ~~- - - ~ ,.~'..,
:
D 3. Does the wetland have the potential to reduce floodtng and eroston~ -
(see .46 _ - _ -
_
D D 3.1 Characteristics of surt$ce water flows out of the wetland
Wetland has no surface water outlet points = 3
Wetland has an intermittently flowing, or highly consnicted outlet points = 2 ~
Wetland is flat and has no obvious outlet and/or outlet is a small ditch points = l
Wetland has an unconstricted surface outlet Dints = 0
D D 3.? Depth of storage during wet periods
Estimate the height of ponding above the bottom of the outlet.
Marks of ponding are 3 ft or more above the surface points = 7
The wetland is a "headwatel' wetland" points = 5 0
Marks of ponding between 2 ft to <, ft from surface points = 5
Marks are a[ least 0.5 ft [o < 2 ft from surface points = 3
Wetland is flat but has small depressions on the surface that nap water points = ]
Marks of ondin less than 0.5 fr Dints = 0
D D 3.3 Contribution of wetland to storage in the watershed
Estimate the ratio of the area of upstream basin contributing surface water to the
wetland to the area of the wetland idselJ:
The area of the basin is less than 10 times the area of wetland points = 5
The area of [he basin is 10 to 100 times the area of the wetland points = 3 3
The area of the basin is more than I00 times [he azea of the wetland points = 0
Wetland is in the FLATS class (basin=the wetland, b definition) Dints = 5
D Total for D 3 Add the points in the boxes above 5
D D 4. Does the wetland have the opportunity to reduce flooding and erosiop?
(see p. 49
Answer YES if the wetland is in a location in [he 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 chap 90% of
[he water in [he wetland is Crom groundwater.
Nofe which of the following indicators of opportunity apply
/Wetland is in a headwater of a river or stream that has flooding problems
- Wetland drains to a mer or stream that has flooding problems multiplier
- Wetland has no outlet and impounds surface mnofF water that might otherwise
flow into a river or stream [ha[ has flooding problems 2
Other
YES multiplier is 2 NO multiplier is 1
[~ TOTAL -Hydrologic Functions Multiply the score from D 3 by D A 10
Add score to table on p. I
w enanc rcamrg r orm - western Washington
August 2004
1
1
1
1
1
1
1
1
1
1
1
1
W etland name or number ~
These questtons apply to wet[ands~oal Gila`ss
` ~ : %~~Pomts
es r ~`4 s~~
~
~
~
'HABITATi FLiNGTIONS„ Indtcators"that wetland fu
tr
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d
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an
a
a
~
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ons
o
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?=
H 1. Does the wetland have the potepfial to provide habitat for many species?
_
.
H Ll Vegetation structure (seep. 72f _
'
Check the types of vegetation classes present (as defined by Cowardin)- if the class covers more
than 10% of the area of the wetland or % acre
.
-Aquatic bed I
_/_Etnergent plants
-Scrub/shrub (areas where shrubs have>30% cover)
_/ Forested (areas where trees have>30% cover)
-Forested areas have 3 out of 5 strata (canopy, sub-canopy, shmbs, herhaceous,
moss/mound-cover)
Add the number of vegetatiott structures that qualify. If you have:
4 structures or more points=4
3 structures points=2
2 structures points=l
1 structure oints=0
H I.2. Hvdrooeriods (see p. 73)
Check the types of water regimes (hydraperiods) present within the wetland. The water
regime has to cover more than ! 0% of the wetland or ~/ acre to count. (see text for
descriptions ofhydroperiodsJ l
_Permane¢tly flooded or inundated 4 or more types present points = 3
/Seasonally flooded or inmdated
_
3 Types present points = 2
-Occasionally flooded or inundated 2 types present point = 1
/Saturated onl
_
y 1 type present points = 0
_ Permanently flowing stream or river in, or adjacwtt To, Che wetland
_ Seasonally flowing stream in, or adjacent tq the wetla¢d
_ Lnke fringe wetland = 2 points
Freshwater Tidal wetland=2 points
H 1.3. Richness of Plant S e i s (see p. 75)
Count the number of plan[ species u[ the wetland that cover a[ least l0 ftr. (d~erent patches
of the same species can be combined to meet the size threshold)
You do not hove to name the species.
Do not include Eurasian dtilforl, reed canarygrass', purple lrnosestrife, Canadian Thistle
If you counted: > l9 species points = 2 I
List species below if you want [a: ~ - 19 species points = 1
~ 5 species points = 0
WaH~od Ra9.... c,....,
-o ~~ auY~LLSi LUU4
1
1
1
1
1
1
Weiland name or number _2_
H 1.4. [ntersoersion of habitats (see p. 76)
Decide from the diagrams below whether interspersion between Cowardin vegetation
classes (described in H 1. I ), or the classes and unvege[ated areas (can include open water or
mudflats) is high, medium, tow, or none.
o
None = 0 p
o
ints Low = 1 point Moderate = 2 points
~
£
z ~ a
+x-acv "~ IIff.~'~ R 'a~ ~ Ers-w. "`a°sr'.s'~
s<, x
~~
[ripanan braided channels]
High =3 points
NOTE: If you have four or more classes or three vegetation classes and open water
the rating is always "high"
H 1.5. Special Habitat Features' (see p. 7~
Checkthe habitat features that are present in the wetand The number of checks is the
nwnber of paints you put into the nest column.
_/Large, downed, woody debris within [he wetland (>4in. diameter and 6 ft long).
_/_Stariding snags (diameter at the bonom > 4 inches) in the wetland
-Undercut banks are present for at (east 6.6 ft (2m) and/or overhand ng vegetation extends at
least 33 ft (1 m) over a stream (or ditch) in, or contiguous with the wetland, for at least 33 ft
(1 Om)
Stable sleep 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 nat yet (vrned grey brown)
3
At least'/. acre of thin-stemmed persistent vegetation or woody branches are present in areas
[hat are permanently or seasonally inundated /structures for egg-laying by amphibians)
_/_ [evasive plants cover less than 25°/o of the we8nnd area in each stratum of plants
H 1. TOTAL Score - potential for providing habitat 6
Add the scores rpm column above
Comments
' Wetland Rating Form-western Washington 14 August 2004
1
1
1
1
1
Wetland name or number _2_
H 2. Does the wetland have the opportunity to provide habitat for many species? ~: m ~ ~
H 2. L Buffers (see p. 80)
Choose the description rhat best represends condition of buffer of wetland. The highest
scoring criterion that applies to the wetland is to be used in the rating. See text for
definition of "undisturbed. "
/100 m (3308) of relatively undisturbed vegetated areas, rocky areas, or open water >95 % g
of circumference. No structures are within the undisturbed part of buffer (relatively
undisturbed also means no-grazing) Points = 5
- 100 m (330 h) of relatively undisturbed vegetated areas, rocky areas, or open water
50% circumference. ,. Points=4
- 50 m (170fr) of relatively uudisturbed vegetated areas, rocky areas, or open water>9~
circumference. Points = 4
- 100 m (3308) of relatively undisturbed vegetated areas, rocky areas, or open water> 25
circumference. - Points=3
- 50 m (1708) of relatively undisturbed vegetated areas, rocky areas, or open water for>
50% evcumference. Points = 3
If buffer does not meet any of [he criteria above
No paved areas (except paved trails) or buildings within 25 m (808) of wetland> 95
circumference. Light to moderate grazing, or lawns are OK Paints = 2
- No paved areas or buildings within SOm of wetland for>50% circumference.
Light to moderate grazing or lawns aze OK. Points = 2
Heavy grazing in buffer. Points = 1
Vegetated buffers are Qm wide (6.6ft) for more than 95% of the circumference
(e.g. tilled fields, paving, basalt bedrock extend to edge of wetland Points = 0.
- Buffer does not meet any of the criteria above. Points = 1
H 2.2 Corridors and Connections (see p. 87)
H 2.2.1 [s the wetland part of a relatively uudisturbed and unbroken vegetated corridor
(either riparian or upland) that is at least l50 fr wide, has at least 30% cover of shrubs, forest
or native undisturbed prairie, that connects to esmaries, other wetlands or undisturbed
uplands that are at least 250 acres ¢t size? (dams in riparian corridors, heavily used gravel 4
roads, paved
road
s, are considered breaks in (he corridor).
~
L
p .,~ r 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 SOh wide, has at least 30% wver of
shrubs or forest, and connects to estuaries, other wetlands or undisturbed uplands
that are at Icast 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 (ga to H~.3) N0=H2.2.3
H 2.23 Is the wetland:
within 5 mi (8km) of a brackish or salt water estuary OR
within 3 mi of a large field or pasture (>40 acres) OR
within I mi of a lake greater than 20 acres?
YES=1 oin[ N0=0 oints
Wedand Rating Form-western Washington 15 Augus[2004
1
1
1
1
1
t
Wetland name or number _>
H 2S Near or adjacent to other prioriro habitats I'sted by WDFW (see p. 82)
Which ofthe following priority habitats aze within 330ft (100m) of the wetland?
(see textfnr a more detailed description ojthese priority habitats)
_/Riparian: The azea adjacent to aquatic systems with flowing water [hat contains
elements of bath 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 occurting below 5000 ft.
Old-growth forests: (Old-growth west of Cascade crest) Stands of at (east 2 tree species,
forming amulti-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 Cores[s: Stands with average diameters exceeding 53 cm (2] in) dbh; crown cover
may be less that l00%; crown cover may be less that 100%; decay, decadence, numbers of
snags, and quantity of large downed material is generally less than [hat found in old-
growth; 80 - 200 years old west of the Cascade crest. 1
_Prairies: Relatively undisturbed areas (as indicated by dominance of native plants)
where grasses and/or fortis form the natural climax plant community.
Talus: Homogenous areas of rock rubble ranging th average size 0.15 - 2.0 m (OS - 65 ft),
composed of basalt, andesite, and/or sedimentary rock, including riprnp
slides and mine tailings. May be associated with cliffs.
Caves: A naturally occurting cavity, recess, void, or system of in[ercormected
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 and/or regular feeding; and/or the open space
functions as a cortidor 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/Es[aary-like: Deepwater tidal habitats and adjacent tidal wetlands, usually
semicnelosed by land but with open, partly obstructed or sporadic awess 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 [o where
ocean-derived salts measure less than O.Sppt. during [he period of average annual tow
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., sand/rock/log recruitment, nutrient contribution, erosion control).
If wetland has 3 or more priority habitats= 4 points
If wetland has 2 priority habitats = 3 points
If wetland has 1 priority habitat = 1 point No habitats = 0 points
Wetland Rating Conn-western Washington I6 August 2004
1
1
Wetland name or number _2_
H 2.4 Wetland Landscape (choose the one description of the landscape arozmd the wetland that
best fits) (see p. 84)
There are at least i other wetlands within'/ 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 5
The wetland is Lake-fringe on a lake with little disturbanw and there are 3 other
lake-fringe wetlands within % mile points = 5
There are at least 3 other wetlands within `h mile, BUT the connections between
them are disturbed points=3
The wetland is Lake-binge on a lake with disturbance and there are 3 other
lake-fringe wetland within `F: mile points=3
There is at least I wetland within %x mile. points = 2
There are no wetlands within % mile. points = 0
H 2. TOTAL Score - opportunity for providing habitat 15
Add the scores in the column above
Total Score for Habitat Functions -add the points for H 1, H 2 and record the result on
1 21
' Wetland Rating Form-western Washin~on 17 August 2004
1
WETLAND 2
1 CATEGORIZATION BASED ON SPECIAL CHARACTERISTICS
' Please determine if the wetland meets the attributes described below and circle the
appropriate answers and Category.
1
1
Wetland+Type
:Check off any criteria that apply fo the wetland Circle the Category whenzhe
~-
approPri4tecriteria are met - - :Category -'
1 -
SC A.0 Forested Wetlands (see p. 90)
Does the wetland have at lease 1 acre of forest that meet one of these criteria for the
Department of Pish and Wildlife's forests as priority habitats'? Ifyau answer yes you
will still need to rate the wetland based on its junctions.
Old-growth forests: (west of Cascade crest) Stands of at least two tree species,
forming amulti-layered canopy with occasional small openings; with at leas[ 8
trees/acre (20 trees/hectaze) that are at least 200 years of age OR have a
diameter at breast height (dbh) of 32 inches (81 cm) or more.
NOTE: The criterion for dbh is based on measurements for upland forests.
Two-hundred yeaz old trees in wetlands will ofen have a smaller dbh
because their ~'owth rates are often slower. The DP W criterion is and 'OR"
so old-growth forests do not necessarily have to have trees of this diameter.
X Ma[ure forests: (west of the Cascade Crest) Stands where the largest trees aze
80 -200 years old OR have avernge diameters (dbh) exceeding 21 inches (53cm);
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.
YES = CateROrv I NO Cat. I
~ Ca'~tego~ry~ofetland based~ony,Specral Chaxactenshcs ~,~'~~-r 3~~~~ a.--
~
~
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e ,~ zghest rahngt wetlandfall tnta; ser eral+cat
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1
1
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Wetland name or number _3,4,5,6_
DRAFT WETLAND RATING FORM-WESTERN WASHINGTON
Name of wetland (if known): Purvis Proner[v
Location: SEC: 23/24 TWNSHP: 17N RuGE: lE (Attach map with outline of wetland to rafing form)
Person Rating Wetland: S Shxnewise Affiliation: The Coot Comnanv Date of Site Visit: March 2007
DRAFT SUMMARY OF RATING
Category based on FUNCTIONS provided by wetland
I II III / IV
Category I = Score >=70 Score for Water Quality Functions 12
Category II =Score 51-69 Score for ({ydrologic Functions 24
Category III =Score 30-50 Score for Habitat Functions 14
Category IV =Score < 30
TOTAL
f
F
ti
50
score
or
unc
ons
Category based on SPECLAL CITARACTERISTICS of wetland
I_ II_ Does not Apply_/_
Final CalegOty (choose the "highest" category from above)
Check the appropriate type and class of wetland being rated.
Wetland'," e ~`~?~"",,''.~,~"" s ~~'~#..~Weitand~Class,.
Estuarine De ressioual s
Natural Herita eWetland Riverine
Bo Lake-frin e
Mature Forest Slo e
Old Growth Forest Flats
Coastal La ooh Freshwater Tidal
Interdunal
None of the above x
1
1
1
1
1
1
1
1
1
1
1
1
Wefland 7,d,i,6
jjj Depres~stonatan~l~FlaYs~Wet1 ~~s~~~,~~~~ ~;~'~
~ *pomts
A ~ 4WATER QUALTTX~Fi)NCT
IONS,.`"~Indteators that the~wetlmmdfimchonsto~ a
~
r ~ ~-"~
F~~~ Watex
»'tm ove
~
~italrTy~~;.'~s~~~~
~ra~~"-~~''*~
~c~
-
.
.
. ,....~. .
D D 1. Does the wetland have the potential to improve water quality? (see p.3S) -~~~
e n
D L 1 Characteristics of surface water flows out of the wetland:
Wetland is a depression with no surface water outlet points=3 3
D Wetland has an intermittently flowing, OR highly constricted outlet points = 2
Wetland has an unconstric[ed surface outlet points = 1
Wetland is flat and has uo obvious outlet and or outlet is a ditch pints = 1
D 1.2 The soil 2 inches below the surface is clay, organic, or smells anoxic
(hydrogen suede or rotten eggs)
D YES points = 4 0
NO pints = 0
D 1.3 Characteristics of persistent vegetation (emergent, shrub, and/or forest class)
Wetland has persistent, ungrazed, vegetation > = 9S % of azea points = 5
D Wetland has persistent, ungrazed, vege[tion> = IYL of area points = 3 g
Wetland has persistent, ungrazed vegetation> = l/10 of area points = 1
Wetland has persistent, ungrazed-vegetation<l/10 of area points=0
D1.4 Characteristics of seasonal ponding or inundation.
This is the area of the wetland that is ponded for at least ?months, bud dries out
D sometime during the year. Do not count the area that is permanently ponded.
Estimate area as the average condition 5 out of 10 yrs. 4
Area seasonally ponded is>'/_ total area of wetland points = 4
Area seasonally ponded is> `/. total area of wetland points = 2
Area seasonally ponded is <'/ total area of wetland points = 0
NOTE: See text jot indicators o seasonal and ermanent inundation.
D Total for D 1 Add the points in the boxes above 12
D D 2. Does the wedaud have the ouoortuni[v to improve water qualiTy? (see p. 44)
Answer YES if you know or believe there are pollutants in groundwater or surface
water coming into the wetland [hat would otherwise reduce water qualiTy in
streams, lakes or groundwater downgradient from the wetland. ;Dote which of the jollowin
conditions provide the sources afpollutants.
Grazing in the wetland or within 150 ti
- Untreated stormwater discharges to wetland
- Tilled fields or orchards within ISO fr of wetland
A stream or culvert discharges into wetland that drains developed areas,
residential area, farmed fields, roads, or clear-cut logging
- Residential, urban areas, golf courses are within I SO ft of wetland multiplier,
- Wetland is ted by groundwater high in phosphorus or nitrogen
- Other I_
YES multiplier is 2 NO multiplier is 1
D TOTAL -Water Quality Functions Multiply the score from D I by DZ 12
Add score to table an . 1
1
1
1
1
1
1
1
1
1
Wetland 3,4,5,6
D Depi•,essronal'andFlats Wetlands '; _
-~ Eomts~
-
~
.
;~
FIYDROLOGIC FUJVCTIONS Indreators that the wetland functions to ieducz r `'
~
~ t fi ~= ~
Tloodm and sheani degradation
~ ~
~
_
_
a
D 3. Does the wetland have the potential to reduce floodtnd and crosron?
(see .46)
D D 3.1 Characteristics of surface water flows out of [he wetland
Wetland has no surface water outlet points = 4
Wetland has an intermittently flowing or highly constricted outlet points = 2 q
Wetland is flat and has no obvious outlet and/or outlet is a sma1L ditch points = 1
Wetland has an unconsMeted surface outlet oints=0
D D 3 ~ Depth of storage during we[ periods
Estimate the height ofpond5ag above the bottom ojthe outlet
Marks of pondine are 3 ft or more above the surface points = 7
The wetland is a `headwater' wetland" points = 5
Marks of ponding between 2 ft m <3 ft from surface points = 5 3
Marks are at least OS ft to < 2 ft from surface points = 3
Wetland is flat but has small depressions on the surface [hat trap water points= 1
Marks of ondin less tltan OS ft oints = 0
D D 3.3 Contribution of wetland to storage in the watershed
Estimate the ratio of the area of upstream basin contribzaing surface water [o the
wetdand [n the area of the wetland itself
The area of the basin is less than 10 times the area of wetland points = 5
The area of the basin is 10 to 100 times Che area of the wetland point = 3 ~
The area of the basin is more than 100 times [he area oP Che wetland points = 0
Wetland is in the FLATS class (basin=the wetland, by definition) oints=5
D
Total For D 3 Add the points in the boxes above I ____
12 j
D
D 4. Does the wetland have the opportunity to reduce floodipg and erosion? ___~:
)
(see p. 49
Answer YES ifthe wetland 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 6y a structure such as
flood gate, tide gate, flap valve, reservoir etc. OR you estimate that more than 90% of
the water in [he wetland is from groundwater.
Note which of the following n:dlcators of oppwTUnity apply.
- Wetland is in a headwater of a river or stream that has flooding problems
- Wetland drnins to a river or stream that has flooding probtents
X Wetland has no outlet and impounds surface runoff water [hat might otherwise multiplier
flow into a river or stream that has flooding problems
- Other Q_
YE3 multiplier is 2 NO multiplier is Y
]~ TOTAL -Hydrologic Functions Multiply the score from D 3 by D 4 24
Add score to table on p. 1
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1
euana ~ 4 ~ n
These questzous apply tozwetlands oj'a[[ FZGM classes: ~~ ~~Potnts
.~ ,i ,~ k d ~, ~ -~x~' tt~` ~T,,~ Six ~„
~?-PABITAT FL7NCTIONS'.- Indicators that wetland=imtotions to,pxovtdo unport_ant habttat~'s~ ~~*=?
H 1. Does the wetland have the potential to provide habitat for many species? '
~ ..
!
H l .1 V e~etation structure (see p. 72) . , _.a
..
Check the types of vegetation classes present (as defined by Cowardfn)- if the class covers mare
than 10% of the area of the wetland or % acre.
-Aquatic bed
-Emergent plants
x_Semb/shrub (areas where shrubs have>30% cover)
-Forested (areas where trees have >30% cover)
-Forested areas have 3 out of 5 strata (canopy, suh-canopy, shrubs, herbaceous, 0
moss/ground-cover)
Add the number ojvegettdion structures' that quay. fyou have:
4 strucrures or more points = 4
3 stmctures points = 2
2 structures points=l
1 structure oints = 0
H 1.2. Hvdro eriods (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 far
descriptions of hydroperiods)
-Permanently flooded or inundated 4 or more types present points = 3 0
_x_Seasonally flooded or inundated 3 Types present points = 2
-Occasionally flooded or inundated 2 types present point = 1
-Saturated only l type present points = 0
_ Permanently flowing stream or river in, or adjacent to, [he wetland
_ Seasonally tlowing stream in, or adjacent to, the wetland
Lade-fiirrge weltaad =2 points
Freshwater tidal wetland = 2 points
H 13. Richness of Plant Sce ~es (see p. 75)
Count the number of plant species in the wetland that cover a[ least 10 ft'. (d~erettt patches
ojthe sarne species can be combined to meet the size threshold)
You do no[ have to name the species.
Do not include Eurasian rLl(foil, reed canaryo ass, purple laosestrije, Canadian Thistle
If you counted: > 19 species points = 2 0
List species below fyou want to: 5 - 19 species points = 1
<Sspecies points=0
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Wetland 3,4,5,6
H 1.4. Interspersion of habitats (see p. 76)
Decide from Ute diagrams below whether interspersion between Cowardin vegetation
classes (described m H L I), or the classes and unvegetated areas (can include open water or
madflats) is high, medium, low- or none.
OQ
None = 0 points Low = ~ t Moderate = 2 points
~~
m
5 b ` ~~L` ~ ~ '
Y L ~ +~. -....
~
,,vuE~,3
~. F d ~, Yy, ;y ~`
~ 4.
'~n,..s%
'w.y,. a
4
~
~
s~ sv
~..
[riparian braided channels]
High =3 points
NOTE: If you have four or more classes or three vegetation classes and open water
[he ratino is always "hi
H 1.5. Soecial Hab~ta[ Feamres~ (see p. 7n
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 a[ the bottom > 4 inches) in [he wetland
-Undercut banks are present for at least 6.6 h (2m) and/or overhanging vegetation extends at
least 33 ft Qm) over a stream (or ditch) iq or contiguous with the wetland, for at least 33 ft I
(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 (cu7 shrubs or trees that
have not yet turned grey brown)
_At least''/a acre of Utin-stemmed persistent vegetation or woody branches are present in areas
that are permanently or seasonally inundated. (structures far eggluying by amphihians)
_x_ Invasive plants cover less than 25 % of the wetland area in each stratum of plants
H 1. TOTAL Score- potential for providing habitat
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~
Add the scores from codump above ~
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1
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1
Wetland 3 4 5 6
H 2. Does the wetland have the opportunity to provide habitat for many species? `~~~„
H 2.1 Buffers (see p. 80)
Choose the description that best represents condition of buffer of wetland. 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 buffet (relatively
undisturbed also means no-grazing) Points = 5
X 100 m (330 fr) of relatively undisturbed vegetated areas, rocky areas, or open water > 4
50% circumference. points=q
50 m (170ft) of relatively undisturbed vegetated areas, rocky areas, or opcn water>95
circumference. Points = 4
- 100 m (330fr) of relatively undisturbed vegetated areas, rocky areas, or open water> 25%
circumference. Paints = 3
- 50 m (170ft) of relatively wrdisturbed vegetated areas, rocky areas, or open water for>
50% circumference. Points=3
TT buffer does tut meet any of the criteria above
- No paved areas (except paved trails) or buildings within 25 m (80ft) of wetland > 95%
cireumference. Light to moderate grazing, or lawns aze OK. Points= 2
- No paved areas or buildings within SOm of wetland for>50% circumference.
Light to moderate grazing, or lawns are OK Points = 2
- Heavy grazing in buffer. Pnints = I
- Vegetated buffers are a2m wide (6.6fr) for more than 95 % of the circumference
(e.g. tilled fields, paving basal[ bedrock extend to edge of wetland Points = 0.
- Buffer does not meet any of the criteria above. Points = 1
H 21 Condors and Connectio s (seep. 81)
H 2.2.1 Is [he wetland part of a relatively undisturbed and unbroken vegetated corridor
(either riparian or upland) that is at least l50 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, hean'7}+usedgrave!
roads, paved rogds, are considered breaks in the corridor). 4
fE5=4 points (go to H2.3) NO=go eo H2.2.2
H 2.22 Is the wetland part of a relatively undisNrbed and unbroken vegetated wrridor
(either riparian or upland) that is at least SOft wide, has at least 30% cover of
shrubs or forest, and connects to estuaries, other wetlands or undisturbed uplands
that are at least 25 acres in size? OR aLake-fringe wetland, if it does not have an
undistmbed corridor as in the question above?
YES=2 points (go to H23) N0=H2.23
H 22.3 Is the wetland:
within 5 mi (8km) 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 = I int NO = U ointss
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Wetland 3,4,5,6
H 2.3 Near or adiacent ro other o 'rv I bit Lz I' t d b WOF W (see p. R2)
Which of the following priority habitats are within 330ft (100m) of the wetland?
(see text far a more detailed description of these priority habitats)
-Riparian: The area adjacent to aquatic systems with flowing water that contains
elements of both aquatic and [ertestrial 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 occurzing below 5000 h.
_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 a[ 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-
g~owth; 80 - 200 years old west of the Cascade crest.
-Prairies: Relatively undisturbed areas (as indicated by dominance of native plants)
where gasses and/or fortis form the natural climax plant communiTy. Fl
-Talus: Homogenous areas of rock rubble ranging in average size 0.15 - 2.0 m (0.5 - 65 fr),
wmposed of basalt, andesite, and/or sedimentary rock, including riprap
slides and mine tailings. May be associated with cliffs.
-Caves: A naturally occurting 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 and/or regulaz feeding; and/or the open space
functions as a corridor connecting other priority habi[nts, especially Chose [hat
would otherwise be isolated; and/or the open space is an isolated remnant of natural
habitat larger than 4 ha (l0 acres) and is surrounded by urban development.
-Estuary/Estuary-like: Deepwa[er 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 tow-energy coastlines there is appreciable
dilution of sea water. Estuarine habitat extends upstream and landward to where
ocean-derived salts measure less than QSppt. during the period of average annual low
Flow. Includes both estuaries and lagoons.
-Marine/Estnarine Shorelines: Shorelines include the intertidal and sub[idal zones
of beaches, and may also include [he 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 CQ shoreline
[unction (e.g., sand/rock/log recruitment, nutrient wntribution, erosion wntrol).
If wetland has 3 or more prioriTy habitats = 4 points
If wetland has 2 priority habifats=3 points
If wetland has 1 priority habitat =1 point No habitats = 0 points
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H 2.4 Wetland Landscape (choose the one descripfion of the landscape around the wetland that
best fits) (see p. 84)
There are a[ least 3 other wetlands within %z mile, and the connections between them
are relatively undisturbed Qigh[ grazing between wetlands OK, as is lake shore with
some boating, but comnections should NOT be bisected by paved roads, fill, fields, 5
or other development. points = 5
The wetland is Lake-fringe on a take with little disturbance and there are 3 other
lake-fringe wetlands within % mile points = 5
There aze a[ least 3 other wetlands within''/z mite, 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 % mile points =3
There is aT least 1 wetland within % mile. points =2
There are no wetlands within % mile. points = 0
H 2. TOTAL Score - oppomurity for providing habitat 13
Add the scores in the column above
Total Score for Habitat Functions -add the points for H 1, H 2 and record the result on
l l4
' REFERENCES
Cooke, Sarah Spear. Editor. 1997. A Field Guide to the Common Wetland Plants of
Western Washington & Northwestern Oregon. Seattle Audubon Society, Seattle, WA.
' Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979, Reprinted 1992.
Classification of Wetlands and Deepwater Habitats of [he United States. U.S. Fish and
' Wildlife Service, FWS/OBS-79/31, 103 pp.
Environmental Laboratory. 1982 Corps of Engineers Wetland Delineation Manua[,
Technical Report Y-87-1, U.S. Army Engineer Waterways Experiment Station,
Vicksburg, MS.
Federal Interagency Committee for Wetland Delineation. 1989. Federal Manual for
Identifying and Dehneating.lurisdictianal Wetlands. U.S. Army Corps of Engineers,
U.S. Environmental Protection Agency, U.S. Fish and Wildlife Service, and U.S.D.A.
Soil Conservation Service, Washington, D.C. Cooperative technical publication. 76 pp.
' plus appendices.
Hitchcock, C.L, and A. Cronquist. 1976. Flora afthe Pacifrc Northwest. University of
Washington Press, Seattle, WA.
' Kollmorgen Corporation . 1992. Munsell Soil Color Charts. Baltimore, MD.
Reed, P.B. 7r. 1988. National List of Plam Species that Occur in Wetlands: National
' Summary. USFWS Biological report 88(24). 244 pp.
Reed, P.B. Jr. 1993. Northwest Region 9, Supplement to Nafianal List ojPdant Species
' that Occur in Wedandr: USFWS.
U.S. Army Corps of Engineers. 1982 Corps of Engineers Wetland Delineation Manual.
' Technical Report Y-87-1, together with clarification and interpretation guidelines as
published by the USACOE, 1992.
U.S. Department of Agriculture, Soil Conservation Service. 1990. Soil Survey of
Thurston County, Washington. USDA Soil Conservation Service. 283 pp.
' U.S. Department of Agriculture. 1991. Hydric Sails of the United States.
Washington Department of F,cology. 1997. Washington State Wetland Identification and
' Delineation Manual, Publication #96-94.
Washington Department of Ecology. 2004. Washington State Wetlands Rating System
,for Western Washington Revised. Publication #04-06-025.
' U.S. Department of the Interior. Circa 1987 - 1989. National Wetlands Inventory Maps.
' Washington Department of Fisheries. 7975. A Ca[alog oJWashingmn Streams and
Salmon Utilization, Volume I and Volwne 2.
Yelm, City of. 2006. Yelm Municipal Code. Chapter 14.08 Critical Areas and Resource
Lands.
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