HomeMy WebLinkAboutWetland Del & Buffer Enhancement Plan 940500006
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Terry Steben
Wetland Delineation
and
Buffer Enhancement Report
Parcel # 940 500 006 and 940 500 007
April 2004
Prepared for:
Terry Steben
6S Huckleberry Place
Port Townsend, WA 98368
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Terry Steben
Wetland Delineation
And
Buffer Enhancement Report
Parcel # 940 500 006 and 940500007
April 2004
Contents
Introduction
Description of Site
Applied Methodology
Washington State Wetland Identification and Delineation Manual
Soils
Vegetation
Hydrology
Classification
Determining Wetland Edges
Jefferson County Unified Development Code
Wetland Buffer Definition
Standard Buffer Requirements
Reducing Buffer Widths
Findings
Soils
Vegetation
Hydrology
Buffer Enhancement Plan
Stormwater Control
Summary
References
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Appendix
Sheet # 1 Location Map and Soil Survey of Jefferson County, Washington
Sheet #2 Findings Map
Sheet #3 Buffer Enhancement Plan with Reduced Buffer
Wetlands Rating Field Data Form
Data Forms, Routine Determination W A State Wetland Delineation Manual
Table # 1 Plant List and Landscape Specifications
Table #2 Re-seeding Recommendations and Quantities
Installation Specifications and Recommendations
Terry Steben
Wetland Delineation
And
Buffer Enhancement Report
Parcel # 940 500 006 and 940500007
April 2004
Introduction
At the request of Terry Steben a wetland delineation was conducted on April 13, 2004. A Level I
Assessment was conducted on March 22, 2004 prior to the purchase of the parcel to confirm the
presence of wetlands not mapped on the Jefferson County Critical Areas maps. A Type 5 Stream
has been mapped and is shown crossing the property. This mapping is in error, as the stream is
actually located off-site within a ravine designated as a park by the Cape George Community.
The stream will have an associated 50-foot buffer, which falls entirely within the public park
land. The goal of this wetland delineation was to determine wetland locations and associated
buffers that would restrict a building site location.
All wetlands within Jefferson County are subject to requirements outlined in the Jefferson
County Unified Development Code (UDC) dated January 1,2001. Land use restrictions will
apply to all future developments associated with this parcel.
Description of Site
. Legal Description: Parcel # 940 500 006 and 940 500 007 Section 13, Township 30, Range
2W W.M. .900 Acres
. Location: Cape George Village #3, Dennis Street, right on Marine View Avenue (Appendix
Sheet # 1 : Location Map)
. Soils: CmC Clallam sandy gravelly loam (Appendix Sheet # 1: Soil Map)
. Slopes: 65% to 15% slopes (as recorded in the field)
The subject property is adjacent to a steep ravine, which contains a Type 5 Stream with an
associated 50-foot buffer. Field measurements reveal that the parcel boundaries fall outside all
buffer restrictions (April 13, 2004). Located on the parcel is a Class II wetland, with 100-foot
buffers, that lies within a distinct swale on the southern portions of Lots 6 and 7. There is an
elevation gain of 27 feet from the stream bank and an elevation gain of about 7 feet from the
wetland to a proposed building location. The rolling topography of this property is forested with
large alders, maples, and cedars, with a healthy understory of native shrubs. Access to the
proposed building site, which is on the northwest portion of Lot 7, is across the wetland on an
existing road. The onsite wetland is along the southern portions of Lots 6 and 7 adjacent to the
cul-de-sac of Marine View Ave.
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Report File Number 2004-8642
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Applied Methodology
The following resources were consulted for this project:
. Jefferson County Critical Areas Map Wetlands (1995) and ESA Maps (Stream and Wetlands)
· Aerial Photographs (Soil maps pre-1975, and 2000, included in Appendix) r-.~ D' lE~ rr:' IJ "r ~'~~--:
. Jefferson County Unified Development Code (January 1,2001) r- . " ---=--.: I l'
. Soil Survey of Jefferson County (U.S. Soil Conservation Service 1975) n . : I :'
. National Wetland Inventory Map I L! II MAY - 3 2004 '.......
. Washington State Wetland Identification and Delineation Manual l.
· National List of Plant Species That Occur in Wetlands: Northwest (Region 9) __ ~~Pl OF C5!~~'>:~_ ~~r:'.opr;t: I
Washington State Wetland Identification and Delineation Manual
Fieldwork to determine the actual wetland boundaries was conducted according to the methodology
outlined in the Washington State Wetland Identification and Delineation Manual (Department of
Ecology #96-94). Chapter 173-22 of the Washington Administrative Code requires that all
wetlands within the State of Washington be delineated using this manual.
The methodology outlined in the 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 regulated, regardless of size.
Soils
A hydric soil is a soil that forms under conditions of saturation, flooding, or ponding lasting long
enough during the growing season to result in an anaerobic upper layer. Hydric soils favor the
growth and regeneration of hydrophytic vegetation. The indicators for this type of soil include low
chroma, 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 the Munsell Color Charts (1992).
Vegetation
Wetland plant species must constitute greater than 51 % of 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 30-foot radius for trees, a 10-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 Wildlife Service (USFW) National List of
Plant Species That Occur in Wetlands: Northwest (Region 9) as to their frequency of occurrence
in wetlands and non-wetlands. During the fieldwork, each species was recorded and given a rating
based on indicator status and percent cover.
Hydrology
Wetland hydrology is defined in the Washington State Wetland Identification and Delineation
Manual as "areas that are periodically inundated or have soils saturated to the surface at some time
during the growing season." Areas must have seasonally inundated or saturated soil at least 12.5%
of the growing season. Indicators of hydrology include visual observation of inundation or soil
saturation, water-stained leaves, cracking of the soil surface, and/or sediment deposits. Positive
Steben Wetland Delineation and Buffer Enhancement
Report File Number 2004-8642
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Olympic Wetland Resources, Inc. 4/04
signs of hydrology are often absent during the summer and fall months but can be inferred if there
are positive indicators of hydric soil and hydrophytic vegetation.
Classification
Wetland categorization was detennined using the Washington State Department of Ecology
(DOE) Wetland Rating System (publication #93-74, August 1993), which assigns a numerical
value to any given wetland accorfling to wetland size, quality of surrounding buffers, vegetation
diversity, wetland types, and habitat value. Wetlands are rated as entire systems and quite often
exceed project boundaries. Ratings range from Class I to Class IV; Class I is the highest quality
wetland and is not replaceable and therefore receives the largest buffers and highest protection.
Determining Wetland Edges
Wetland edges were determined by establishing two 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. Measurements were taken with a Chainman II hip chain.
Jefferson County Unified Development Code (January 2001)
Wetland Buffer Definition Section 3.6.9 (2):
A designated area adjacent to a wetland that protects, and is integral to the
wetland ecosystem. Buffers provide shading, input of organic debris, and coarse
sediment, room for variation in the stream or wetland boundaries, habitat to
wildlife, and protection from harmful intrusion necessary to protect the public
from losses suffered when the functions and values of aquatic resources are
degraded.
Standard Buffer Requirements 3.6.9 (5 Hi):
Buffers shall remain naturally vegetated except where the vegetation has been
disturbed, invaded by highly undesirable species, or would substantially benefit
from the increased diversity of introduced (native) species. Where buffer
disturbance has occurred during construction, replanting with native vegetation
shall be required. Minor pruning of vegetation to enhance views and removal of
undesirable species (e.g. alders) may be permitted by the Director on a case-by-
case basis.
Reducing Buffer Widths 3.6.9 (6):
The Administrator may reduce the standard wetland buffer width, when the project
applicant demonstrates both of the following to the satisfaction of the Administrator:
i. Standard wetland buffer width averaging as set forth in this section is
unfeasible.
11. The project application includes a buffer enhancement plan using naJiye__ .. - --'--,
vegetation, which substantiates that an .nhanced buffer will il~~ ~ · · r iE_c~,
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functional attributes of the buffer to provide additional protection for the
functions and values.
Findings
The Jefferson County Critical Areas Map does not indicate the presence of wetlands on site. A
Class II wetland (29 points) was delineated during this assessment, measuring approximately 400
feet in length and varying in width from 10 to 90 feet. This Class II wetland will have associated
100-foot buffers measured perpendicular from the delineated edge (Jefferson County Unified
Development Code, Jan. 1,2001,3-30 Buffers Table 3-4).
The wetland lies within an open swale that is defined by a distinct drop in topography. This
wetland receives stormwater from upslope properties in addition to water that is directed to the
wetland via a ditch and culvert along Marine View Avenue. Wetland vegetation requiring year-
round water was identified in this wetland (horsetails and water parsley). The driveway to access
the upland portions of the site appears to act as a berm. The widest part of the wetland is above
the access driveway, which appears to hold water since there is no culvert. The wetland below
the drive narrows to fewer than 20 feet.
Only the north edge of the wetland was delineated; the southern edge coincides with the property
boundaries. The wetland appears to terminate in a distinct channel that eventually joins the Type
5 Stream. At this point, water is diverted through a 24-inch buried pipe with an outlet on the
beach along Discovery Bay.
All wetlands and drainage corridors were flagged with orange plastic ribbon labeled "Wetland
Boundary," tied to vegetation along the drainage ditch at points 20 feet apart. The wetland edge is
contiguous with the drop in topography and distinct vegetation change. Flagging is labeled with
alphanumeric codes (AI through All). These data point locations, wetland edges, and buffers are
indicated on the Findings Map in the Appendix (Sheet #2).
Soils
Jefferson County Soil Survey (page 41) lists soils on site as CmC Clallam sandy gravelly loam.
This soil is not classified as a hydric soil on the Jefferson County Area Hydric Soil list (January
1991). However, wetlands have been recorded throughout Jefferson County in this soil type.
Wetlands often occur in the Clallam soil type since the clay layer is near the surface and water
will accumulate when there is soil disturbance or there is a distinct depression.
Even though the soils are not classified as hydric, data points and soil test pits confirmed the
presence of hydric soils in the wetland. The soils were low-chroma the entire depth of the soil
test, indicating frequent saturation and a rising water table. At Data Point #2 soil colors were
black (l0YR2/1 to 16 inches). At Data Point #1, upslope and to the north of Data Point #2, soils
were not hydric. Several 6-foot deep perk holes were dug on site; most holes revealed that the
soils consisted of sand to sandy loam the entire depth. This soil is extremely well drained and
did not indicate a regular rising water table (lOYR 3/3 to 10YR 4/4).
Steben Wetland Delineation and Buffer Enhancement
Report File Number 2004-8642
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Vegetation
The site contains a high diversity of plant species; below is a list of vegetation identified, along
with the indicator status for each species.
Scientific Name Common Name Status Layer
Wetland Plants
F AC Tree
F AC Herb
FAC Sed e
OBL Sed e
FAC Herb
OBL Herb
FACW- Herb
F AC+ Shrub
F AC+ Shrub
F AC Tree
FAC+ Herb
FACU
FACU
FACU+
NI
NI
FACU
FACU
FACU
FACU
FACU
NI
Tree
Tree
Herb
Herb
Shrub
Shrub
Herb
Tree
Shrub
Shrub
Herb
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UPL Upland Species, FACU Facultative Upland Species/Non Wetland, FAC Facultative Species,
FACW Facultative Wetland Species, OBL Obligate Wetland Species, NI No Indicator Assigned
The qualifier of + or - further defmes the status of the species.
Plants classified according to the Fish and Wildlife Service, 1988,1993 Update
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Hydrology
Water only needs to be present 20 days of the growing season for an area to qualify as a wetland.
The growing season is defined by the Jefferson County soil survey as March 12 to November 25.
Hydrology must be present for 12.5% (20 days) of these 258 days. The growing season is also
defined by soil temperature at 19.7 inches below the soil surface being higher than biological 0
(50C or 400F). Daytime temperatures were in the high 50's during this fieldwork; thus this
delineation was conducted during the growing season.
Hydrology was present only in the form of soil saturation in the soil test pits within the wetland.
Ongoing drought conditions for the past 4 years are causing wetlands to appear dry. When there
Steben Wetland Delineation and Buffer Enhancement
Report File Number 2004-8642
Olympic Wetland Resources, Inc. 4/04
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are positive indicators in both soils and vegetation (especially obligate Vegetati~n likF water. .
parsley and sedges) wetlands can be verified during dry seasons.
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Buffer Enhancement Plan
The primary goal of this buffer enhancement plan is to minimize buffer impacts by planting
appropriate native trees and shrubs to create sufficient separation between the building and the
wetland. The buffer will be reduced from the required 100- foot buffer to 35 feet near the
building site. The remainder of the buffer not associated with the building and septic site should
remain in its natural condition. Trees and shrubs that are currently found on site should be
protected during the construction and revegetation process. Secondary goals for this plan include
increasing plant species diversity, thereby increasing habitat value for wildlife.
The buffer to be enhanced is an area of approximately 2,500 square feet and is located along the
6-degree slope between the home site and the wetland edge. After the construction project is
complete all disturbed areas will be planted in native trees and shrubs, as recommended in the
plan. The planting plan includes vine maple, cedar, hazelnut, red-flowering currant, and Oregon
grape (Appendix Sheet #3). Complete landscape specifications are listed, including quantities,
sizes, optimum locations, and spacing for each plant. All remaining bare areas should be re-
seeded with the seed mix included in the recommendations (Appendix Table #1 and Table #2).
Plantings may be rearranged to suit landscape and aesthetic choices.
Also included in the Appendix (Table #1 and Table #2) is a directory of local nurseries, which
supply native plants, and this report's Installation Specifications and Recommendations. It is
critical for the success of any newly planted trees and shrubs to be maintained for the first two to
three years. Maintenance includes watering and weeding and replacement of plant material that
does not survive after the initial planting.
Stormwater Control
All stormwater from the house and garage will be directed away from the ravine and stream.
Sediment or runoff during the construction of the structure should be minimized with the use of
straw bales or sediment fences. This will be required during the entire building process and will
continue to be required until the vegetation becomes established and can act as a natural filter. A
gravel base will be placed on driveways and parking areas.
Summary
A Class II wetland not indicated on the Jefferson County Critical Areas Maps was delineated on
April 13, 2004. The wetland is confined to a drainage swale and roughly parallels the southern
boundary of the two parcels (Lots 6 and 7) within Cape George. The on-site wetland is from 10
to 90 feet wide and approximately 400 feet long, eventually joining the off-site Type 5 Stream.
This wetland will have associated 100-foot buffers measured perpendicular from all wetland
edges.
The majority of his parcel falls within the 100-foot wetland buffer; therefore a buffer reduction
will be required. This delineation report includes a buffer enhancement plan to minimize
construction impacts, increase species diversity, and create sufficient separation between the
Steben Wetland Delineation and Buffer Enhancement
Report File Number 2004-8642
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Olympic Wetland Resources, Inc. 4/04
wetland and the building site. The buffer enhancement will further protect the Class II wetland
and ensure the long-term function and values of the buffer. After the construction project is
completed, 12 trees, 16 shrubs, and a native seed cover will be planted, as specified in the plan.
All bare areas should be covered with straw until the native vegetation becomes established, in
order to prevent sediment or runoff. To verify compliance with this planting plan, the project
will be inspected for approval during the final inspection.
The final authority over this wetland determination, buffer reduction, and buffer enhancement
plan rests with the Jefferson County Department of Community Development; restrictions will
apply to any development near the wetlands or buffers associated with this parcel. 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.
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References
Buckingham, et al., 1995. Flora of the Olympic Peninsula. Northwest Interpretive Association
and the Washington Native Plant Society, Seattle, Wash.
Cooke, Sarah Spear, 1997. A Field Guide to the Common Wetland Plants of Western
Washington and Northwest Oregon. Seattle Audubon Society, Seattle, Wash.
Cowardin, L.M.V. Carter, F.C.Goblet, and E.T. LaRoe, 1979. Classification of Wetland and
Deep Water Habitats ofthe U.S. U. S. Fish and Wildlife Service, Washington, D.C.
Hitchcock and Conquest, 1973. Flora of the Pacific Northwest.
Federal Interagency Committee for Wetland Delineation, 1987. Federal Manual for Identifying
and Delineating Jurisdictional Wetlands. July 1994 update. 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.
Jefferson County Unified Development Code. January 2001.
Leonard, William P., 1993. Amphibians of Washington and Oregon. Seattle Audubon Series.
MacBeth, Div. of Kollmorgen Instruments Corp., 1992. Munsell Soil Color Charts.
Mitsch and Gosselink, 1993 . Wetlands.
Pojar, Mackinnon, 1994. Plants of the Pacific Northwest Coast.
Reed, Porter, 1988. National List of Plant Species That Occur in Wetlands, Region 9. 1993
update.
Washington State Wetland Department of Ecology, March 1997. Washington State Wetland
Identification and Delineation Manual, #96-94.
U.S. Department of Agriculture, 1994. Keys to Soil Taxonomy. Pocahontas Press.
U.S. Department of Agriculture, Soil Conservation Service, 1975. Soil Survey of Jefferson
County .
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rille: Findings Maps Salle: Sheet
Olympic Wetland Resources, Inc. Parcel #940 500060 1"=50'
856 50th Street #940500007
Port ilwnsend, WA 98368 ctJellt: April 2004 #2
Terry Steben
360 385.6432 65 Huckleberry Place Joh #: 2004-8642
Port Townsend, WA 98368
Stream Mapped
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Buffer
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Cull-de-Sac
All wetland locations
and sizes are approximate,
to establish exact points
a formal survey is required
Delineated Wetland Edge
100' Buffer From Wetland Edge
. Flagged delineation markers
. Data Points
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Olympic Wetland Resources, In And Reduced Buffer Proposal
Parcel # 940 500 0060&7 #3
856 50th Street April 2004
Port Townsend, WA 98368 ctJeRt: Terry Steben
360 385-6432 65 Huckleberry Place Job#: 2004-8642
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Buffer Enhancement Location
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., Red-flowering
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Cedar (4)
Oregon Grape (10)
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Adjusted Buffer
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Appendix
Sheet #1 Location Map and Soil Survey Of Jefferson COWlty Of Washington
Sheet #2 Findings Map
Sheet #3 Buffer Enhancement Plan with Reduced Buffer
Wetlands Rating Field Data Form
Data Forms, Routine Determination W A State Wetland Delineation Manual
Table #1 Plant List and Landscape Specifications
Table #2 Re-seeding Recommendations and Quantities
Installation Specifications and Recommendations
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Wetlands Rating Field Data Fonn
Background information: ()l..t.1m PtL
NamcofRaler: 0./ /~1 LJ..I AftiIladoa:~~ '/r..z.{rA-
Name ofwdaod (lfblowD):
GoYemmc:atJurJsdlc:doaofwalaDd: JcFFtil5~ /'/),)"'T'1 r~ a=/aV'tJ~fJ$
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LocaIioD: IJ4 ScctIoa: _ of U4 $: _ SeclIoa: 1.3- TowIIsbIp: ~ Range: Z,}J,l
Sources of Infonn8IIon: (Check 81. SO!Jrcea that eppIy)
Sitnlsit: 1-USOSn.;oMap: ..2SNWlIIIIp: --':"'AaIaIPboto:~SoI1ssurvey: x.
Otber:X- Desaibe: ~&..\ caT1utt ~ f1Af05
WheIl Tbe ReId DaIa form Isc:omplefe'eaIa'Catqory~ [K] 2 q fD(NU
,
Q.1. HIgh Quality NaluraJ WeUand Ckde Answers
Answer Ibis quesdoa 1f)'Qll bne IIdequate ilIformaIIoa or apedcace to do so.
If DOt IiDd _ wIlb 1be CllpCitiIe to uswer1beqaesdoas. 11a.lf1be
lIDSWeCto queIIioas II, Iblllld Ie _Ill NO. COIIIiICl1beNmnI HedlIge
prognmofDNR. '
lL~__~
-
Is lIIcae~eWlelaof"""~ ~'to1OpOplplyor
hydrology of1be wc.cI..s. ~ by Illy of 1be IbIIowID& COIdlIoaI?
CoasIdc:c 0IIIy c:IuaIps lbIt mayllaft IItza pIIce ilI1be... S decIdeI. Tbe
impacts of dID&a daae edcr ~JlI'llbIIlIy beca IlIIIlIbed lIIId 1be 'ftCllIIId
ocosystaIl wDI be dole to aac:biDg IOIIIe _ eqai1IxIum tbat may &qIIaeat
a high quIl1ty -'-1 ,
lat. Upslram WIfenIIed > 121& ImpcrvIoas. Yes: go to Q2
1a2. WedaIId Is dI1icbcd ad _ flow Is DOt obslnIcIed Yes: go to Q2
1a3. WedaIId bas beca paded. filled. Joaed. Yes: go to Q2
1a4. W"iD wdaodls ~ by cIlta. wars. ClC. Yes: go to Q2
laS. WedaIId Is gnzed. Yes: go to Q2
I a6. Olber iDdIc:-.s of cIisludIace (1jst below) ~'O~
No: go to lb.
2a.3. Is !be .egetaIioD alllixluft: of oaly bedIaceous pIaDts lIIId Sphapum
mosses with 110 scnabI1Iwb or forated classes?
Is !be area ofhcrbace.s plants, Spbagnum, lIIId deep 0IpIlic .
soils > 112 acre? -
Is !be area ofhcrbace.s p1ants, Spbagnum, 8DcI deep orpnic
soils Y...112 eae?
YES: Category I
YES: Category U
NO: Go to 0.3.
Q.2b. Matve r.re.ted wetIaad.
"
2b. L Does SO% of !be _ of upper forest canopy consist of evergreen
trees older ""'" 80 ,ears oe decicIuous bees older ""'" SO years?
N_: The sim of_ is often DOt a __ of age, ond size_
be used as a surrogate for age (see guidance).
2b.2. Does SO% of!be _ of fon:st canopy consist of evergreen _ older
than SO years, AND is !be structural di~ty of !be forest high as
charac:terized by ....dditiooallayerof_ 20'-49' talI. shrubs 6'- 20'.
tall. IDd a herbaceous gn>undcover?
YES: Category I
NO: Go to 2b.2
YES: Go to lb.3
NO: Go to Q.3
2b.3. Does < 25% of !be an:aI cover ill !be beIbaceousIgroundco_ oe
!be shrub laver consist of iII_ivelcxolic DIant soecies from lhc list 011 p. 191
Q.2c. EstuariH wedaads.
YES: Category I
NO: Go to 0.3
2c.I. Is !be wctIaud listed as National Wildlife Refuge, National Park,
National Esbwy Reserve. Natural Area Ptaerve, State Padt, or
EducatiooaI. Ea~ or Scientific Reserves designated UIIcIer
WAC 332-30-15I?
YES: Category I
NO: Go to 2e.2
2c.2.1s!be wetIancI > 5 acres; ......................................................... YES: Category I
N_: If aa ..... contains patches of sak lolerant veget&lion thaI are
I) less ""'" 600 feet apart IDd that In: scp8l'lIted by mudflats that go
dry 011 . Mean Low Tide, oe
2) separated by tidaI channels that In: less than 100 feet wide;
all !be vegetated aras are to be consiclcred together in calculating !be
wctIaud area.
or is !be wetllDd 1.5 acn:s; ......................................................... YES: Go 10 2c.3
or is !be wetland < I acre? .......................................................... YES: Go 10 2c.4
Ib Ale then: populations of non.....live plaDlS which are curraatly present. cover YES: go tD Q.2
more lban 10% of!be wetland, and appear to be illvaditt& IIIlive populations? No: go to Ie.
Briefly describe any lIOn-native plant popuJations 8DcI
IafonnatiOll ~s):
Ie. Is then: evidence ofbwnan-ausec1 disturbaaces which bave visibly
clcgr.IdecIwater quality. Evidence of the c1epdatiOD of water quality include:
direct (untrated) nmotr from roads or parIdnc Iols; pcaeace. oe historic
evidcnc:e. of wasti'C1Wnps; Oily sheeM; !be smell of 0IpIlic cbanicals; or
livestock use. B~ describe; f) _ . I r;
IaJfDbj)n;. (Jl= rrr>T .t')q'"1'M1
Q.2.1rnpI_ble EcoIoglcaI FunctIona:
Does !be MllancI:
have at 1east 1/4 acre of orpnic: soi1s c1eepcr ""'" 16 iDches
IDd !be wctIaud is ~latively undistudlecI; OR
[If !be answer is NO because !be wctIaud is disturbed briefly
clescribe:
IDdicators of disturbance may include:
- Wetland bas been graded, fil1ed, 1oggecI; .
- Orpnic soils on lhc surface are dried-oul for more ""'" balf
of the year;
- Wetland RlCeives direct stonnwater nmotr fiDm urban or
agricultural areas.];
OR
have a forated class grater ""'" I eae;
OR
have c:baractcristics of aD estuarine system;
OR
have IIleI oe __ beds?
%a.1lop uti F_
Ate Illy of!be t1uee following conditioas DId tot the area of 0IpIlic aoi1?
2&.1. Ale Spbapum. mosses. _ JRlIBl-(>3O%) aad the_of
invasive species (see Table 3) is less than IO%?
Is the area of sphagnum mosses and deep cqanic soils > 112 aae?
Is !be area ofspltagnum mosses 8DcI deep 0IpIlic ~Is Y..112 acre?
2a.2. Is then: aD area of organic soil which bas aD etneIgCIIl class with a11east
one species fiom Table 2, IDd cover of invasive species is < 10% (see Table 3)?
Is the area ofhetbaceous pIants 8DcI deep 0IpIlic soils > 112 acre?
Is the area ofherbaccous plants ad deep orpnic soils 114-112acn:?
2c.3. Does the wetIancI meet at 1east 3 of!be following 4 crUoria: ...un
_ minimum existing evidence of"- rdaIed di-'>aace such as
cIikiDg. ditching. fiUing. cu1tivatioD, puing oe!be presence of IlOIl-
aaIjve p1ant species (see guidaace foe defiaitioA);
_ surface water connection with tidal sa!tw*t oe tidaI fieshwaIer;
-a11east 7S%of!bewetland basalOObuffi:rof~pastme,
open wat.... sbrub oe forest;
_ bas at 1east 3 of !be fo11owiDg featun:s: low marsh; hip marsh; tidaI
cbaane1s; Iagoon(s);woody debris; oe contiguous &eshwater wetland.
2c.4. Does !be wetland meet all of!be four criteria UIIcIer 2c3? (above)?
Q.2d. Eel GnSlud Kelp Beds.
2d.1. Ale eelgrass beds p<esenl? ............u..................................-
2d.2. Ale their floating or DOn-floating kelp bed(s) preseut with greater than
SO% macro algal cover in !be month of August or ~............u.
Q.3. Category IV wetlands.
3&. Is !be wetland: less lban I acre I!Il!.
hydrologically isolated I!lI!.
comprised of one vegetated class thaI is dominated (> 80% areal cover)
by ooe species ftom Table 3 (page 19) or Table 4 (page 20)
3b. Is lhc wetIancI: less than two acn:s
and, hydro1ogically isolatec1, , .
with ooe vegetated class.1Dd > 90% of area1 cover ill any combination of
species from Table 3 (page 19)
3c. Is !be wctIaud excavated from upland 1IllI. pood smaller ""'" I acre
without . surface water connection to streams. lakes, rivas. or other
wet IDdbas<O.l acreofve lion.
rw ({; , ic: n · r
\[\ MAY 3 2004
\
YES: Go to 2b
Yes: Go to 2c
Yes: Gotold
YES: Category I
YES: Category U
NO: Go to 2&.3
YES: Category I
YES: Category U
NO: Go to 2&.3
YES: Category I
NO Category U
YES: Category 11
NO: m
YES: Category I
NO: go to 2d.2
YES: Category I
NO: Category U
IV
NO: go to 3b
~ TI:
-- \
..:- .:\ !
, '
'1 ,,'
, \ I'
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--
DATA FORM 1
Routine Wetland Detennination
(W A State Wetland Delineation Manual or
1987 Co s Wetland Delineation Manual)
Project/Site: aPe C1l:i)t.4E M ~ It q qu ')l5V () 0 10 Date: 4 1:3 01-
Applicant/owner: ~ S-re 5c:H .f1 '14u $tO au 7 County: \ft;"'FFtJ1...SCN LD~-rv\
State: I)/ASt1tf\Vtt tuN
srrlR: t;/,? -r 0 f?-2V..}
Community ID:
Transect IDp: ~'
Pibt 10: D T+"' I
Investi tor(s): .' aDt'-1
Do Normal Circumstanc~ exist on the site? c::::fii? no
Is the site significantly disturbed (atypical situation)? yes ~
Is the area a tential Problem Area? es c:::::n:o::?
VEGETATION
Dominant Plant S ies
Stratum
T
T
067+ S
Ru US sPEL-m u
HYDROPHYTIC VEGETATION INDICATORS:
% of dominants OBL. FACW. &@ 4 2- ~
Check all indicators that apply & explain below:
Regional knowledge of plant communities v
-fr
Physiological or reproductive adaptations ~
Technical Literature ~
Hydrophytic vegetation present?
Rationale for decisionlRemarks:
L&s "TifTW 5"\70 uvn IN Ar\l (E
HYDROLOGY
Is it the growing season? ~
Based on: ~\lL DIL D 1/<7
Dept. of inundation: j--f otAfe inches
Depth to free water in pit: N~ inches
Depth to saturated soil: JVbNf
Check all that apply & explain below:
Stream, Lake or gage data:
Aerial hoto hs:
Wetland hydrology present?
Rationale for decisionlRemarks:
inches
Other:
yes
Indicator Dominant Plant S ies
Indicator
Stratum
f1\LV
FALU
f1\cv
PALo{-
yes
Wetland plant list (nan or regional)
Morphological adaptations
Wetland Plant Data Base
~
~
-.L
-L
OTHER _
no Water Marks:
Drift Lines: es no
Oxidized Root (live roots)
Channels <12 in. es no
FAC Neutral: yes no
no
no
yes no
Waler-stained
Leaves:
yes no
Other:
~
~'
~ln' ,
"
,tJ
, ,
Ie
MAY - 3 2004
<:..:-
" .
;'t:Pl Of CJ\ r;.:, , . _,l:"L..OP~L.
DATA FORM 1
Routine Wetland Detennination
(W A State Wetland Delineation Manual or - '
1987 Co s Wetland Delineation ManuaI)
Project/Site: C-ft?e 0EO~e p/tfU!.a.:::> 0 5W ODp Date:
Cft)o 9)J 007
Applicant/owner: ~ S~B8'-'
Investi to' s): D. t4 6 rn l
Do Normal Circumstances exist on the site?
Is the site significantly disturbed (atypical situation)?
Is the area a tential Problem Area?
VEGETATION
4{' J 04- :
County: ~~
State: U/ A-
srrlR:Sl3 3D'eZ IA/
Community 10:
Transect 10:
Plot 10: p=f:f
Stratum
Indicator Dominant Plant S ies
Stratum
Indicator
H
\1 () BL
Check all indicators that apply & explain below:
Regional knowledge of plant communities
Physiological or reproductive adaptations
Technical Literature .
Hydrophytic vegetation present?
Rationale for decisionlRemarks: 11)
~t4::}tTtrl --,rtAA <S" I '1>
L-
X
~
Wetland plant list (nat'l or regional) :::L.-
Morphological adaptations 1-
Wetland Plant Data Base x
no
OTHER _
HYDROLOGY
Is it the growing season?
Based on:
Dept. of inundation:
yes
P61V(ttL'7
- 0 - inches
,ev WaterMarks: es no
11 Drift Lines: es no
Oxidized Root (live roots)
Channels <12 in, es no
FAC Neutral: yes no
no
no
yes no
Depth to free water in pit:
<.....- - 0- inches
Water-stained
Leaves:
yes no
Depth to saturated soil: -. D ~ inches
Check all that apply & explain below:
Stream, Lake or gage data:
Aerial hoto hs:
Wetland hydrology present?
Rationale for decisionlRemarks:
Other:
Other:
yes
rm.._- -rg 11 fIr
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Installation Specifications and Recommendations
All areas of exposed soil will be revegetated with species known to tolerate local soils
and local conditions. Individual plant species have been selected because they have a
high habitat value, are consistent with surrounding vegetation, and are known to thrive in
east Jefferson County.
Fall Installation
Planting should be installed between mid-September and mid-November, unless the new
plantings can be watered throughout the summer. Plantings installed in the fall generally
outperform those installed in the late winter or spring. Plants put in the ground in the fall
have the advantage of an extended period for root growth before rapid top growth in the
spring. In the fall, the soil is warmer and more aerated than in the spring and most plants
experience active root growth during this time.
The cool, cloudy days and frequent precipitation of fall and winter also provide ideal
transplanting conditions. Until sufficient root systems develop, newly installed plants will
undergo transplanting stress that can be exacerbated by hot sunny days. Fall and winter
weather allows for reduced transpiration and provides ample moisture for the roots while
the plant recovers from transplant shock.
Root Disturbance
Immediately before installation, plants with broken, damaged, or twisted roots
must be pruned. Matted or circling roots of containerized plantings must be
pruned or straightened and the sides of the root ball must be roughened from top
to bottom in two to four places to a depth of approximately half an inch. If
circling roots are left, they may eventually girdle the plant as they grow and
thicken in place. If the roots at the edge of the root ball are straightened and
extended, they will have access to a greater volume of soil in the planting hole.
Also, the roughened edges of the root ball will have better contact with the
backfill soil.
Disturbing and removing one-fourth to one-half of the roots in the outer inch of
the root ball will damage only the most sensitive plants; most often, this treatment
actually stimulates increased plant growth.
Plant Depth
The finished height of each plant's root ball will be slightly higher than that of the
surrounding soil. The exception is for sandy soils, in which case the soil heights
will be even. The top of the root ball will not be covered with backfill soil. A
watering basin will be formed around each planting by building a berm of soilIjlL., -----re, ~- -" 11 "[!'
least 30 inches in diameter. ; I ii' l.b ll,r rr _ _'
iIU<c-, .
pr\
ill \ MAY - 3 20C
I
I !
.. ;",,:PT. OF Cl~t';..:" . ~.:
When planting a container-grown plant, the top of the root ball should not be
covered with any other soil. Covering the root ball with soil, particularly if it has a
finer texture than the potting or field-growing soil, will generally cause water to
flow around the root ball instead of into it; root balls covered in this way may
receive water only from below. To allow direct wetting of the root ball from
above, install the plant so that the top of the nursery soil is slightly higher than the
surrounding soil level. If the soil is sandy, or of a large particle size, then the
nursery soil should be level with the surrounding soil.
A watering basin made of mounded soil around each planting will further help to
catch water from above-the berm should be at least 30 inches in diameter,
surrounding the plant. Mulch placed within the basin and on the berm will limit
moisture loss from the root ball and surrounding soil, but care must be taken that
it does not come into contact with the stem of the plant as pathogens living in the
mulch may attack the bark. Rodents living in the mulch may also be a problem.
Re-seeding
After the completion of the construction and planting projects, a seed mix (included in
the Appendix, Table 1) will be evenly spread on all bare areas. An inspection by a
wetland biologist or Critical Areas staff of Jefferson County Department of Community
Development will be required after all planting is completed.
Maintenance: Weeding and Irrigation
The use of appropriate native species and careful planting ensures that the need for
ongoing maintenance will be minimized. However, some maintenance is required to
ensure that the young plants become established. It is recommended that weeding around
new plants be conducted once or twice a year during the months of May and September
for the first five years, and as often as needed after that. All Scot's broom, Himalayan
blackberry, and thistle should be monitored and eliminated from the site.
Irrigation may be required for upland species (vine maple, red-flowering currant, and
pine) for the first three years or until plants are well established. Hand watering or
irrigating with overhead sprinklers once a week should be adequate during the hot
summer months. Wetland species that are planted near the creek corridor may require
less watering.
r:'""'-"-'- ,..'. -'-.'-,
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