HomeMy WebLinkAbout2006.06.00 - Wetland Delineation and Mitigation Plan6tt
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C.L. Flint
Wetland Ilelineation
and
Mitigation PIan
Parcel # 964 20A 701
964 240 702
June 2006
Prepared for:
C.L. Flint
P.O- Box 1428
PortTownsend, WA98368
8s-6432
dine@cablespeed.com
C.L. Flint
Wetland Delineation
And
Mitigation Plan
Parcel # 964 2A0 7A1,964 200 702
June 2006
Contents
Introduction
Description of Site
Methodology
Findings
Soils
Vegetation
Hydrologt
Mitigation Plan
Summary
References
Appendix
Sheet #1 Location Mlp and Soil Survey of Jefferson County, State of Washington
Sheet #2 Findings M"p
Applied Methodology
Wetlands Rating Field Data Form
Data Forms, Routine Determination WA State Wetland Delineation ManualMonitoring Form (Sampte)
C.L. Flint
Wetland Delineation
And
Mitigation Plan
Parcel # 964 2A0 701 (702)
June 2006
Introduction
At the request of C.L.Flint a wetland delineation was 6onducted on June 14, 2006. An
extension of Deering Wetland (WL #9-1) near the northem parcel (964 200 702) was
identified during a Level I Wetland Assessment conducted on January 31,2006.
At the time of the original assessment the majority of understory vegetation had been
cleared on the northern parcel and along Katherine Street to 296 Street. The large trees
were not cut. Due to the identification of the wetland and potential impacts to wetland
buffer it was decided by the City that Katherine Street should not extend to 29th Street as
per building code requirements.
The goal of the wetland delineation is determine the exact edge of the wetland, categorize
the wetland according to the recent Department of Ecology Rating form, and measure and
mark the buffers. This report includes a mitigation plan to address buffer impacts.
Buffer setbacks now impact the designed septic site location on parcel 964200 702. ALI
the buildings are on parcel 964 200 701 and are well outside wetland buffers. Buffer
reductions apply only to the proposed septic system and are therefore within the
jurisdiction of the Environmental Health Specialist of Jefferson County and the City of
Port Townsend.
Description of Site
. Legal Description: Parcel #964 200 701 (702) Section 4 Township 30N Range I W
o Location:2827 Katherine St. (undeveloped) North of Hastings St. and West of Thomas
st.. Soils: TuC Tukey gravelly loam and CmC Clallam gravelly sandy loam
. Slopes: 0 to 15% slopes
A map of the site location and mapped soils is included in the Appendix (Sheet #1).
The subject property consists of two parcels (130' X 198' and 100' X 100'). Three
building; a house, gtr€e, and out building are under construction and nearly completed on
the southern lot (964 2A0 701). These structures are all outside any wetland buffers.
Flint Wetland Delineation and Mitigation Plan
Report File Number 2006061406
I Olympic Wetland Resources, Inc.
Methodology
Wetland analysis was conducted using the methodology outlined in the Washington State
Rating Systems for Western Washington (2004) and City of Port Townsend's Municipal
Code @TMC), Critical Areas Ordinance (NO. 2899, July 2005). All wetlands within the
City of Port Townsend are subject to requirements outlined in the Code. Land use
restrictions will apply to all future developments associated with this parcel.
A comprehensive description of methodology used during this delineation is included in the
Appendix.
The following resources were consulted for this project:o Port Townsend Critical Areas Map Wetlands (1995)o Aerial Photographs (Soil maps pre-1975 and 2000, included in Appendix)o City of Port Townsend's Municipal Code (July 2005)r Soil Survey of Jefferson cowrty (u.S. Soil conservation Service l97s)o Washington State Wetlandldentification and Delineation Manualo National List of Plant Species That Occur in Wetlands: Northwest (Region 9)
Findings
The wetland, east of Katherine Street and within a portion of 29ft Street, has a distinct
wetland/upland edge. The plant communities, soil types, and a slight drop in elevation
define the delineated edge. The north-east corner of lot 964 200 701 is within wetland
buffer.
This large seasonal wetland has been previously identified and categorized as a Category II
wetland (1994Palazzi). The new DOE rating form (DOE 04-06-025) was used to rate this
wetland which also verified the Category II rating. Category II wetlands, with a moderate
habitat value, have an assigned 100' buffer
This extension of the Deering Wetland was flagged with orange plastic ribbon labeled
"Wetland Boundary," at points 15 to 20 feet apart. Flagging is labeled with alphanumeric
codes (A1 through A4). The data point locations, wetland edges, and buffers are indicated
on the Findings Map in the Appendix (Sheet #2).
Sails
Jefferson County Soil Survey (page 40) lists soils within the valley as: TuC Tukey gravelly
loam and CmC Clallam gravelly sandy loam; neither soil is listed as a hydric soil on the
Jefferson County Area Hydric Soil list (January l99l). A series of unmapped wetlands
(City of Port Townsend Critical Areas Maps) are located at the top of Basins 5 and 9.
These seasonal wetlands are common and form within the compacted glacial layers of
Clallam soil series whenever there are minor drops in elevation.
Data Point #1 is outside the wetland; the soil did qualifu as hydric (lOYR 3l2withmotrles
10YR 5/4 and IOYR 512). DataPoint #2, within the wetland, has hydric soils, (10YR 2/1
Flint Wetland Delineation and Mitigation Plan
Report File Number 2006061406
2 Olympic Wetland Resourceq Inc-
and 10YR 4l2wirhmottlesl0YR 3i4). The wetland soil is nearly black and was moist,
indicating high water tables and frequent saturation.
Vegetation
Both the wetland and the upland areas consist of a diversity of native plant species. The
wetland has amosaic of plant communities, structural layers, and habitat features. Wetland
vegetation consists of spirea, rose, willow, with an understory of sedges. The upland
vegetation, within the buffer that has not been cleared, is dominated by Douglas's fir, salal,
oceanspray, and elderberry.
Below is the list of vegetation identified on site and the assigued indicator status of each
specles.
Scientific Name
Wetland
Common name Status Layer
Athyrum filix-femina Lady fem FAC Herb
Carex dewevana Dewey sedge FAC Sedse
Carex obnupta Sloueh sedee OBL Sedee
Festuca arundinaceq Tall fescue FAC-Grass
Ranuncalus repens Creeping buttercup FACW Herb
Rosa nutkana Nootka rose FAC Shrub
Salix lucida var. lasiqndrs Pacific willow FACW+Shrub
Salix scouleriana Scouler willsw FAC Shrub
Spiraea doug,lasii Hardhack FACW Shrub
Thuia plicata Western red cedar FAC Tree
Upland
Amelanchier alnifolia Service-berry FACU Shrub
Anthoxanthum odoratum Sweet vernal gass NA Grass
Dactvlis glomerata Orchard-sass FACU Grass
Gaultheria shallon Salal FACU Shrub
Holodiscas discolor Ocean-sDray NI Shrub
Juncus effusus Soft rush FACW Rush
Lolium perenne Perennial ryeFtrass FACU Grass
P seudotsug.a menzies ii Douelas- fir FACU Tree
Pteridium aqulinum Bracken fern FACU Fern
Rubus discolor Himalayan blackberry FACU Shrub
Rubus ursinus Trailine blackberry FACU Shrub
Sambucas r*cemosa Elderberry FACU Shrub
UPL Upland Species, FACU Facultative Upland SpeciesNon Wetland, FAC Facultative Species,
FACW Facultative Wetland Species, OBL Obligate Wetland Species, NI No Indicator Assigned
The qualifier of + or - further defines the status of the species.
Plants classified according to the Fish and Wildlife Service; 1988,1993 Update
Flint Wetland Delineation and Mitigation Plan
Report File Number 2006061406
3 Olympic Wetland Resources, Inc.
Hydrologt
Water only needs to be present 20 days ofthe growing season (begins early March) for an
area to qualiff as a wetland. Since this delineation was conducted in mid June, well into
the growing season, hydrolory can be assumed when there is the presence of wetland
vegetation that requires frequent saturation (OBL obligate vegetation).
Mitigation PIan
The understory along Katherine Sheet including the wetland buffer was cleared before the
wetland was identified. Between the time of the Level I and the wetland delineation,
restoration planting was installed within the buffer. The following plants were planted
within the impacted buffer; l0 mock orange, 11 Indian plum, 3 oregon grape, 3 twinberry,
5 vine maple, I cherry, I snowberry. Native understory, including salal, oceanspray, and
rose are quickly returning to the impacted areas as well. Invasive weeds were minimal.
It is recommended that 30 or more trees and shrub be planted along the impacted areas of
Katherine Street and that all invasive species be weeded when identified. Weedy species
include Himalayan blackberry, Scot's broom and thistle. Additional maintenance wilt
include watering planted trees and shrubs through the dry summers. The mitigation area is
indicated on the Findings Map in the Appendix (Sheet #2).
Performance Standards
The proposed length of time for mitigation compliance is five years- This time period witl
allow for the planted and volunteer species to become established. Survivorship of tree
and shrub species is expected to be 80% or greater and will be determined during the
monitoring process. The wetland buffer mitigation will be considered successful if 80% or
greater of desirable cover (both planted and volunteers) is achieved and the plants are
healthy and vigorous.
Monitoring
Monitoring should be conducted for 5 years to ensure the success of the planted species
and that performance standards are met. A monitoring form included with this mitigation
plan will be used to determine plant survivorship, species density, and general condition of
planted species. This information will determine whether plant survivorship and percent
cover provided are sufftcient to meet the performance standards to mitigate buffer impacts.
A sample monitoring form for this project is included in the Appendix. This form should
be included with the annual report submitted to the City of Port Townsend Development
Services Department, Public Works.
Flint Wetland Delineation and Mitigation Plan
Report File Number 2006061406
4 Olympic Wetland Resources, Inc.
Summa
A II was delineated on June 14,2006 for C.L. Flint. This wetland, with
moderate functions, has associated 100-foot buffers. The majority of the wetland
buffer was cleared of all understory vegetation prior to the identification of the wetland.' To compensate for this buffer violation a mitigation plan and monitoring schedule are
included with this report.
Revegetation has begun to compensate for the buffer impacts. Over 30 trees and shrubs
have already been plarited within the buffer with an additional 30 trees and shrubs will be
added after the final construction is complete. Due to the presence of an undisturbed tree
layer, both planted and native vegetation retuming to the site should have high survival
rates. Newly planted native species over time will increase the diversity as well as address
buffer impacts. Performance standards for the mitigation plan require an 80% cover of
desirable species (planted and returning natives) after 5 years. This will be monitored
yearly by a professional biologist and a monitoring report will be submitted to the City of
Port Townsend Development Services Department annually.
The final authority over this wetland determination and mitigation plan rests with the
govemmental agencies. If there are further questions or planning requirements for this
project please do not hesitate to call.
Dixie Llewellin
Principal Biologist, Olympic Wetland Resources, Inc.
Certified for Wetland Delineation, 1987 Manual
Wetland Training Institute, June 1995
&
)
Flint Wetland Delineation and Mitigation Plan
Report File Number 2006061406
5 Olympic Wetland Resources, Inc.
References
Buckingham' et al., lggs.X'lora of the Olympic Peninsula. Northwest Interpretive Association
and the Washington Native plant Society, Seattte Wash.
Cooke, Sarah Spear, lgg7.A Field Guide to the Common Wetland Plants of Western
Washington and Northwest Oregon. Seaffle Audubon Society, Seattle, Wash.
Cowardiru L.M.V. Carter, F.C;Gobtet, and E.T. [..aRoe, 1979. Classilication of Wefland and
Deep Water Habitats of the U.S. U. S. Fish and Wildlife Sewice, Washingtoq D.C.
Hitchcock and cronquist, 1923. Flora of the pacific Northwest
Federal Interagency Committee for Wetland Delineation, 1987. Federal Manual for fdentif'ing
and Delineating Jurisdictional Wetlands. July 1994 update. U:S. Army Corps ofEngineers, U.S. Environmental ProtectionAgencn U.S. Fish and Wildliie Service, andU.S.D.A. Soil Qenssrvation Service.
Leonar4 William P., 1993. Amphibians of \ilashington and Oregon. Seattle Audubon Series.
MacBettr, Div. of Kollmorgen Instruments Corp., 1992. Munsell Soil Color Charts.
Mitsch and Gosselink, 1993. Wetlands.
Pojar, Mackinnon,1994. Plants of the pacific Northwest coast.
Port Townsend" City of July,2005. Critical Area Ordinance N0. Ztgg.City of port
Townsend-
Ree4 Porter, 1988. National List of plant Species That Occur in Wetlands, Region 9. 1993
update.
Washington State Wetland Deparftnent of Ecology, March 1p97. Washington State WetlandIdentification and Delineation Manual, #96_94.
Washington State Wettand Departmentof Ecology, April 2004. Guidance on WetlandMitigation in Washington State
U.S- Department of Agriculture,lgg4. Keys to Soil Taxonomy. Pocahontas press.
U.S. Department of Agriculture, Soil Conservation Service, 1975. Soil Survey of JeffersonCounty.
Ia
I C.L. Flint
Wetland Delineation
And
Mitigation Plan
,!
Parcel # 9& 200 701,9& 20O 702
June 2A06
Appendix
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Sheet #1 Location Map and soil suryey of Jefferson county, state of washifrgton
Sheet #2 Findings MaP
Apptied Methodolbgy
Wetlands Rating Field Data Form
Data {'ogms, Routine Determination WA $tate Wetland befineation Manual
Monitoring,f'orm (SamPle)
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Iille,Location and Soil Map
2827 Katherine
Port Townsenq WA 98368
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P.O. Box 1428
Port Townsend, WA 98368
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Port Townsend, WA 98368
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100' Buffer From Wetland Edge
@ ftagged delineation markers
I Data Points
AII wetlandlocations
and sizes are approximate;
to establish exact points
aformal survey is required
Applied Methodology
City of Port Townsend
Washington State Wetland Identification and Delineation Manual
Fieldworkto determine the actual wetlandboundaries was conducted according to the
methodology outlined in the Washington State Wetland Identification and Delineation
Manual, March 1997 (Departmentof Ecology #96-94). Chapter 173-22ofthe Washington
Adminisrative Code requires that all wetlands within the State of Washington be definlated
using this manual. AII critical areas wittrinthe City of Port Townsend areiegulated
according to the Port Townsend Municipal Code Critical Codes Ordinance 6NO. Z*ll, Lrty
2005 PTMC).
The methodology outlined inthe Washington State Wetland Identification and Delineation
Manual requires examination of the three parameters for a positive wetland determination:
hydric soils, hydrophytic vegetation, and hydrology. For an area to qualify as ajurisdictional wetland it must have a positive indicator from all three parameters. All
wetlands identified using this methodology may be federally regulatd regardless of size.
Soils
A hydric soil is a soil that forrns under conditions of saturation, flooding, or ponding
lasting long enough during the growing season to result in an anaerobic upper layer.
Hydric soils favor the growth and regerreration of hydrophytic vegetation. The indicators
for this type of soil include low chrom4 mottles, gleying, and high organic content within
the upper 32 inches of the soil profile. Holes were dug on the site and soil colors (including
value and chroma) were recorded in the top 16 inches. Soil colors were analyzed'using GMunsell Color Charts (1992).
Vegetation
Wetland plant species must constihrte greater thanSlo/oof the total vegetation present to
meet the qualification as a site dominated by hydrophytic vegetation. Dominance of plant
species is determined by calculating actual aerial cover within a 3O-foot radius for hees, a
1O-foot radius for shrubs, and a 6-foot radius for the herbaceous layer at each data point.
Commonly occurring plant species have been rated by the United States Fish and Mldlife
Service (USFVD National List of Plant Species That Occur in Wetlands: Northwest
(Regron 9) as to their frequency of occurrence in wetlands and non-wetlands. During thefieldworh each species was recorded and given a rating based on indicator stafus and
percent cover.
Hydrologt
Wetland hydrology is defined in the Washington State Wetland Identification and
Delineation Manual as "areas that are periodically inundated or have soils sahrated to the
surface at some time during the growing season." Areas musthave seasonally inundated oranfrrmfcr{ cni! af !+ari 11 <ol- ^-C+L-- -^,,,:-- rn'r\ t---- ---. - c^ro r \ dr@lqcrvu r\Ir crl twbt r/-.J ,/o ul Llltt tsruwufts SCiiSOll (ZU CayS OUI Oi ZJd daysi. i he gfowmg
season is described in Jefferson County by the Jefferson County soil survey as March 12
to November25. The growing season can also be defined by soil temperature at19.7
inches below the soil surface being higher than biological 0 (5"C or 40"F).
lndicators of hydrology include visual observation of inundation or soil saftration, water-
stained leaves, cracking of the soil surface, and/or sediment deposits. Positive signs of
hydmlogy are often absent during the summer and fall months but can be infened if there
are positive indicators of hydric soil and hydrophytic vegetation.
Classification
Wetland categorization was determined using the Washington State Department of
Ecolory @OE) Wetland Rating System Revised (Ecology Publication #04-06-025,
eugusiZOO4), according to type and class ofwetland. The wetland is assigned a numerical
value for water quality function, hydrologic function, and habitat frrnction. The total score
determines the category of wetland Wetlands are rated as entire systems and quite often
exceed project boundaries. Ratings ftmge from Category I to Category [V; Category I is the
highest qualrty wetland. Buffers are assigned according to land use and numeric scores.
Category I wetlands are not replaceable and therefore receives the largest buffers and
highest protection.
I)etermining Wetland Edges
Wetland edges were determined by establishing pairs of data points: one within the wetland
which contains positive indicators of all three of the wetland requirements: soils, hydrology,
and vegetation, and another data point outside the wetland, where one or all of the
requirements were not present. The wetland edge is flagged between the pairs of points at
intervals of 20 to 40 feet.
Wetland Rating Form-Western Washington
20
16
16
ll=Score 51€9
lll=Score3GSO
lV=Score <30
l=Score >
52
category based'on sPEclAL cHARAcrERrsrcs of wefland
Final choose the "h from above
of
notapply X
-
based on Functions provided by wetland
of Rater: Dixie Lletr/ellin
Total Score For
Range:1W
Affiliation: Olvmoic Wetland Resources. lnc.
Date of Site Msi[ January 31, 2006
Section:4 ,Township:30N
Score forWater Quality
Score for Water Hydrologic
Score for Habitat
I
Natural Heritage WeUand
Bog
X Depressional
Riverine
Lake-Fringe
Slope
Flats
Freshwater Tidal
Forest
Growth Forest
Lagoon
lnterdunal
None ofthe Above
D ional and Flats Wetlands
@s-lndicators thatwefendEndona b improve water qualig
Dl. Does the wetland have the potentiaf to improve water qualiU?
POINTS
3
D1.1 Characteriitics of surface water ffows out of the wetland:
Wetland is a depression with no surface water ou$et
Wetland has an intermittently flowing, or height constricted, ouflet
Wetland has an unconstricted surface outlet
Wetland is flat and has no obvious ouUet and/or outlet is a ditch
3
2
1
1
4
D1.2 The Soil 2' below the surface is clay, organic, or smells anoxic.
YES
NO
4
0
3
D1.3 Characteristics of persistent vegetation (emergent, shrub, and /or forest class):
Wefrand has persistent, ungrazed, vegetation>=954/o d'area
We0and has persistent, ungrazed, vegetation>=1|2 of area
Wetland has persistent, ungrazed, vegetation>=l/l0 of area
Wedand has oersistenL unqrazed. veqetation< 1/10 of area
5
3
1
0
0
D1.4 Characferistics of seasonal ponding or inundation.
This is the area of the wetland 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 ftve out of ten years.
Area seasonally ponded is >1/2 totalarea of wetland
Area seasonally ponded is >1/4 total area of wetand
Area seasonally ponded is <1/4 totalarea of wetland
4
2
0
{0Total for D1 Add the points in the boxes above
2
YES ff you know to believe there are pollutants in groundwater of surface water coming
the wetland that would othenrise reduce water quality in streams, lakes, or groundwater
from the wetland. Note which of the following conditions provide the sources,
thewetlandwithin 150'
stream or culvert discharges into wetland that drains developed areas, residential areas,
farmed fields, roads, or clear cuts
rn
stormwaterUntreated to wetlanddischarges
Tilled fields or orchards within 150' of wetland
areas, golf courses are within 150' of wetlandrbanu
Wetland is fed by groundwater high in phosphorus or nitrogen
Other
islis2NO
20Total -Water Quality Function Multiply and score from Di by D2
Add score to table on 1
D ional and Flats Weflands
D3- Does the wetland have the
lndicators that
to tuduce
to reduce
and erosion?
WeUand has no surface water ou$et
wetland has an intermittenfly flowing, or highly constricted, ouflet
wetland is flat and has no obvious ou0et and/or is a small ditch
4
1
water out the
Wetland has an unconstricted surface outlet
D3.1 of
Marks of ponding are 3 ft or more above ihe surface
The wetland is a headwater wefland
Marks of ponding between 2 ft to < 3ft ftom the surf;ace
Marks are at least0.S to < 2 ft ftom surface
Wetland is flat but has smalldepressions on the surfiace
outlet
1thatwatertrap
ofMarks thanless 0.5 ft
D3.2 Depth during wet ponding above the bottom
The area of the basin is less than 10 times the area of the wettand
The area of the basin is 10 to 100 times the area of the wetand
The area of the basin is more than 100 times the area of the wefland
to storage the water
theEstimate otration areathe of basinupstream watersurface theto wetlandcontributing
areathe theof itself.wetland
D3.3 of
Wetland in the FLATS class
1
3
T for in the x
velocity,
afYes wetlandthe ints a location thetn wherewatershed flood reductionor tnstorage,water it provides helps downstreamprotect and frompropertyresourQesaquaticorexcessiveand/or erosive flows-
ifNO the water into thecoming wetland is controlled a suchstructure as a floodby gate,gate,reservoir ORetc.flap valve,estimate morethatyou 90o/o theof tnwaterthan thefromtsgroundwater.
ofwhich the ofindicatorsfollowing applyopportunity
isWetland m a headwater of rivera or stream that has flooding problems
Wetland drains ato orriver stream that has flooding problems
hasWedand no outlet and ndsrmpou surface water that othenrisemight
flow into nvera or stream hasthat problemsflooding
TOPOther OF BASINS
is2 NO is1
Total -Hydrologic F and score from D3 by D4
Add score to table on 1
unction Multiply
16
Habitat FunctiO0S-lndicators that the wetland tunctions to provide important habitat
H1.1 Does the wetland have the potential to provlde habitat for many epecies?
Types 4
2
1
0
3 Types
1
2
H1.2 Hydrooeriods
Check he $pes of water regimes (hydroperiods) within the
cover more than 10% of the wetland or 1/4 acres to counl
wetland. Thewater has to
_Permanently flooded or inundated
_Seasonally flooded or inundatedX Occasionally flooded or inundatedX Saturated only
Permanentlv flowinq stream or river in. or adiacent to. the
1
H1.3 Ricfiness of Plant Species
Count the # of plant species in the weUand that cover at least 10 @
Do not include reed canarygrass, purple loosestrife, Canadian thistle
POINTS
>19
5to19
<5
2
1
0
1
H1.4 lnterspersion of habitats
lnterspersion of habitats between vegetation, unvegetated areas is high medium or low
High= 3 points Moderate=2 points Low=1 point None=0 points
2
H1.5 Special Habitat Features
Check the habitat features that are present in the wetland, the # of checks is the # of points
-Large,
downed weedy debris within the wetland (.4" diameter and 6' long)
_Standing snags (diameter at the bottom >4') in the wetland
Under cut banks are present for at least 6.6 ft and/or overhanging vegetation extends 3.3 ft for 33 ft
-stable
steep banks of fine material that might be used by beaver or muskratX At least 114 acre of thin-stemmed persistent vegetation or woody branches in areas that are
seasonally or permanently inundated (struciure for egg-laying amphibians).X lnvasive plants cover less lhan2io/o of the wetland area in each stratum of plants
2
Total for Hl. Potential for providing Habitat Add the points in the boxes above 8
H2. Does the wetland have the provide habitat for species?
1
the description that best represents condition of buffer of wefland.The highest scoring
that applies to the wetland ts to be used m the rating-POINTS
100m (330) of relative undisturbed vegetated areas, rocky areas, or open water >g5o/o of circumference.
100m (330') of relaiive undisturbed vegetated areas, rocky areas, or open water >S0% of circgmference.
5
4
4
3
3
2
2
'l
0
1
(170',)of relative undisturbed vegetated areas,rocky areas,or open water >95Vo of circumference-,|fi)m (330)of relative undisturbed vegetated areas,rocky areas,or open water >25Yo of circtrmference.
(1 70")of relative undisturbed vegetated greas, rocky areas, or open waler
lf buffer does not meet any of the criteria above
>Wo of cinrrmference.
paved areas (except trails) or buildings within 25 m (S0) of weiland >95% ciranmfercnce.
paved areas or buildings within 50 m (s0) of weiland >sOo/o circumference.
grazing in buffer
buffers are < 2M wide (6.6 fl) for more than 9s% of the circumference
does not meet of the above crtteria
H2.2
H2.2.1 ts the wefland part of a relatively undisturbed and unbroken vegetated conidor (riparian or upland)that tsleast150ftwide,has at least 30olo @ver of shrubs,forest of native undisturbed prairie,that @nnects tooroherwetlandsorundisturbeduplandsthatareatleast250acresinsize?YES 4 points (go to H2.3)NO go to H2.2.2
H2.2.2 is the wetland part of a relatively undisturbed and unbroken vegetated coridor (riparian or upland)that tsleast50ftwide,has at least 30o/o @ver of shrubs,forest of native undisturbed prarne,that connects toorotherwetlandsorundisturbeduplandsthatareatleast25acresinslze?OR a Lake-fringeifitdoesnothaveanundisturbedconidorastnthequestionabove?
YES 2 points (go to H2 .3)NO go to H2.2.3
2.3 ls the wetland
5 mil (8km)of a brackish or salt water estuary OR within 3 mt of a large field or pasture
wiftin 1 mile of a lake that 20 acres?YES 1
of fte follouring habitats are within 330 ft (100m) of the wefland POINTSRipadan
Stands or more habitats
priority habitats
4
3
1
Cliffs
Oldgrowth forests
Mature forests
Prairies
white oak
Urban natural open space
Estuary/Estuary-like
Marine Estuarine shorelines
1 habitat
4
choose the one description of the landscape around the weiland that best fits
mile, and the connections between then are relatively undisturbed
little disturbance and there are 3 other lake-fringeweflands
There are at least 3 wetland within 1/2 mile, BUTthe connections between then are disturbedThe wetland is Lake-fringe on a lake with disturbance and there are 3 other
POINTS
5
5
3
3
2
0
There are at least 3 other wefland within 1/2
( light grazing OK, but shoutd NOT be bisected by paved roads or development
The wetland is Lake-fringe on a lake with
within 1/2 mile
lake-ftinge wetlandswithin 112 mile
There is at least 1 wetland within 1t2 mile
there are no wetland within 1/2 mile
H2.4 Wetland Landscaoe
3
8
Total Score for Habitat Functions- Add nts for Hi and H2 and record on
above
1
Total for H2.Habitat in thethe
16
Data Form 1
Routine Wetland Determination
(WA State Delineation Manual or 1987 Corps Wetland Delineation Manual)
Project/Site:Z8?7 Katherine Street Date: June 14, 2006
Applicant/owner: C.L, Flint County: leffersonState: WA
lnvestigator: Dixie Llewellin. Olympic Wetland Resources. lnc. S/T/R: 54, T30N, R lW
community lD:Do normal circumstances exist on the site
ls the site significantly disturbed (atypical situation)
ls the area a Problem Area?
Wetland Determination
Hydrophytic vegetation present?
Hydric soils present? YES
Wetland hydrology present? YES
Rationale/Remarks? Slilghtly upslope from wetland
no
sect lD:
Plot lD: Data Point # I
ls the sampling point within a wetland?
YES
yes
NO
no
no
Shrub FACShrub IFACUAmelanchier alnifolia
Herb OBLshrub lPecSalix scouleriana
Shrub lFncuGaultheria shallon
Check all indicators that apply and explain below:
Regional knowledge of plant communities X
Physiological or reproductive adaptations X
Technical literature X
Hydrophytic vegetation present?
Wetland plant list (Nat'l or regional) X
Morphological adaptations
Wetland plant data base XFEs-l No
Vegetation
Dominant Plant es Stratum lndicatorDominant Plant S es Stratum lndicator
Rational for decision Remarks
Hydrophytic Vegetation
of dominants oBL, FACW, and FAC: 60%
Hydrology
ls it the growing season?YES NO r Marks Sediment Deposits
Drainage patternsBased on :Air Tempeture and Date
Depth of inundation: None inches
Depth to free water in pit: inches
Depth to saturated soil: None inches
Check all that apply and explain:
Wetland hydrology present?
Drift Lines
Oxidized Root (live roots)
Channels<12 in
FAC Neutral:
Local Soil Survey
Stream,or gauge raphs:
YES NO
Rational for decisions Remarks
SOIIS Drainage Class:lve-l
Map Unit Name: CmC Clallam gravelly sandy loam, TUC Tukey gravelly loam
ries & Phase): Clallam and Tukey Field observation confirm Yes No
axonomy (subgroup): Entic Durochrepts mapped type?
Profile Descri n
Depth Horizon Matrax color Mottle ors undance Texture Drawing of soil
(inches)unsell moi nsell moist)
to4 IOYR3 2 IOYR 5 4 San loam
7 to 16"IOYR 5 2
ric Soil lndictors AllThat Apply)
istosol----Histic Epipedon----Sulfidic Odor----Aquic Moisture Regime---Reducing Conditions----
Cleyed or Low-Chroma Colors---Concretions----High Organic Streaking in Sandy Soils
----Listed on Local Hydric Soils List---Listed on National Hyd
Hydric soils present? YES
ric Soils List---Other
NO
onalfor decisions/Remarks: Soils all fill
Mil
NO
NO
Notes:
(WA State Delineatio
ProjectiSite: 2827 Katherine Street
Applicant/owner: C.L Flint
lnvestigator: Dixie Llewellin. Olympic Wetland Resources. lnc.
Do normal circumstances exist on the site
ls the site significantly disturbed (atypical situation) yes
ls the area a Problem Area?
Wetland Determination
Hydrophytic vegetation present?
Hydric soils present?
Wetland hydrology present?
Rationale/Remirks?
Data Form 1
Routine Wetland Determination
n Manual or 1987 Corps Wetland Delineation Manuat)
Date:June 14,2006
County: leffersonState: WA
S/T/R: 54, T30N, R tW
community lD:
ransect lD:
Plot lD: Data Point # 2
NO
NO
ls the sampling point within a wetland?
no
:s
YES
Dominant Plant
NO
ical literaturen
Stratum
Shrub
lndicator
ACWSalix scouleriana Tree FAC
a Tree
Rosa Shrub FAC
Hydrophytic Vegetation lndicators:
of dominants OBL, FACW, and FAC: 100%
all indicators that apply and explain below:
X
Wetland plant list (Nat'l or regional) X
Morphological adaptations
Wetland plant data base X
Hydrophytic vegetation present?
Rational for decision/Remarks:
Regional knowledge of plant communities X
Physiological or reproductive adaptations X
Vegetation
Dominant Plant Species Stratum lndicator
Drift Lines
Oxidized Root (live roots)
Channels< I 2 in
Neutral:
Local Soil Survey
Marks Sediment Deposits
Drainage patterns
YES
Stream, Lake or gaugetrl
NO
ata:Ae
NO
and Date
eck all that apply and explain
Hydrology
ls it the growing season?
Based on :Air Tempeture
Wetland hydrology present?
Rational for decisions/ Remarks
Depth of inundation:
Depth to free water in pit:
Depth to saturated soil:Surface
inches
inches
inches
Mottle colors
(Munsell moist)
Mottle abundance Texture(inches) (Munsell moist)
Matrix colorDepth Horizon
0to4"r oYR 2/r Fine sand loam
4 to 16"r oYR 4/2 r oYR 3/4 Sandy loam
Soils
Map Unit Name: CmC Clallam gravelly sandy loam, TuC Tukey gravelly loam
Yes No
axonomy (subgroup): Entic Durochrepts
ric ln
r----AqstiHicistosol____ulfidicEpin----S Odo Moiutc sturepedo me---_Red nucrReg Conditions----g
G or Low-Ch maroleyed nColors----Concretio hs----Hi anrc nII SoilsorgStreakingSandy
National Hydri
Fts-I
on Local Soilsc onHydriList____Listed Socils List___Other
soilsHydric NOpresent?
nRatio foral sdecision Remarks allSoils fi
Drainage Class:lve-l
& Phase): Clallam and Tukey
Profile Descri
le
ng of soil
AllThat Apply)
Field observation confirm
mapped type?
Mil
il
Notes
NO
Monitoring FormC.L. Flint 2827 Katherine Street(Sample)Observer:NameCommon NameTotalsVolunteer native species and percent coverage:NOn-natiVe SpecieS (Himalayan blackberry, reed canarygrass, Canadian thistle' Scots' broom):Percent coverage of non-natives:List species to be replaced:rc6)Ic{)&!)€oFc)Gg'qlLrt|!otq)0€c)clnr6!ie)d)oa€c)9tclACommentsAcer circinatumSwphoricarpos albusRtbeslewisiiOlenleria cerasiftrmisLonicera involucrataBerberis nernosaVine mapleSnowberryRed-flowering currantMock orangeIndian plumTwinberryOregon GrapeTSSSSSTOlympic Wetland Resources, Inc.
Tille,
0lympklfttlod hourcs,
Findings IUap
Level I
Gibbs Sfreet Wetland856fllthSrea
Port hwrsnd, lTA98368
3ff385#fl
frie@roblespdrom
rtod' C.L. Flint
P.O. Box 1428
Port Townsend, WA 98368
Sole'
As hdicoted Sled \
#rth:
June 2006
!fi#'2006461,m6
turcel #9642ffi7OU7V21
lo0'
v
vv
v
t
29ttr Street (undeveloped) i
HastingsAve.
VV \r Deering Wetlan,
\rV
Delineated Wetland Edge
v,.Vv
ro
c)c.o
o)
(I)Ed
(l,ol{u)
w).op
t5
Wetlond ldentified
IIIIIIII
964200702
ttaa
Subject Forcel
9642W70t
o
DP#1
{t(l)k€a
q)g
t<(D
tttM
Gibbs Street Wetlond
hos NOT been delineoted,
locotions of wellond shown
on lhis mop is opproximote.
parly wetland delineatio+' "eview
-.rne wassmer
Page I of I
From: Judy Surber
Sent: Wednesday, September 13,2006 4:42PM
To: 'Mraz, Richard (ECY)A.'
Gc: Suzanne Wassmer; Lund, Perry
Subject: RE: Third party wetland delineation review
Many thanks Rick - lt was great to see you and Perry
-----Original Message-----
From : M raz, Richard (ECY) A. [mailto : rmra46 1 @ ECY.WA.GOV]
Senk Wednesday, September 13, 2006 4:08 PM
To: Judy Surber
Cc: Suzanne Wassmer; Lund, Perry
Subject: Third party wetland delineation review
Hello Judy:
Thanks for the opportunity to provide assistance regarding the delineation for the wetland just north
of Hastings Avenue in Port Townsend. Based upon the site visit, Ecology staff determined that
certain Hydrologic Functions of the wetland were not present, thereby yielding a score that resulted
in a Category lll ranking. Specifically, the wetland is topographically isolated from other down
gradient systems and does not have the opportunity to reduce flooding and erosion. This aspect
eliminates the use of a multiplier in the ratings system that would have resulted in a Category ll
ranking. Thus, in conclusion, the system is accurately rated a Category lll. lf you have questions or
require clarification of this determination, please contact me.
Rick Mraz
Wetlands/Shorelands SpecialisL
Shorelands and Environmental
Assistance Program
SouLhwest Regional Office
(360) 4O7 -622r
rmra461@ecy.wa.gov
9/1312006
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