HomeMy WebLinkAboutHabitat Management Plan 702024018 (2)
HABITAT MANAGEMENT PLAN
for
LORDS LAKE LOOP ROAD PROPERTY
Quilcene, Washington
Prepared for
Richard A. Alexander
P.O. Box 3624
Bellevue, W A 98009
Jefferson County Project #MLA04-00234
Prepared by
Kunz Biological Consulting
Cindi Kunz, wildlife scientist
780 Arcadia West
Port Townsend, W A 98368
(360) 385-6300
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R.A.Alexander Habitat Management Plan
August 13, 2004
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RICHARD A. ALEXANDER
PRIORITY HABITAT AND SPECIES MANAGEME
August 2004
Jefferson County Project #MLA04-00234
INTRODUCTION
At the request of Richard A. Alexander, potential landowner, a wildlife and critical
habitat survey was conducted for a proposed residential building construction. The
purpose of the survey is to assess the project vicinity for critical wildlife habitat, to
determine if priority species are present, and to develop a habitat management plan for
the proposed project construction.
Priority species and critical habitat are established by the Washington Department of Fish
and Wildlife (WDFW). Management guidelines are addressed in the 1991 "Management
Recommendations for Washington's Priority Habitats and Species". Priority habitat is
defined by the WDFW as a habitat type with unique or significant value to many species.
An area classified and mapped as "priority habitat" must meet certain criteria as defmed
in the WDFW 1991 management guidelines. Priority species are defined as wildlife
species requiring protective measures for their perpetuation due to their population status,
their sensitivity to habitat alteration and/or their recreational importance. A priority
habitat may contain priority and/or non-priority species.
The subject property is located west of Highway 101 and east of the Little Quilcene
River, which originates from Lords Lake, along Lords Lake Loop Road (Figure 1) at
approximately river mile 2. The legal description is Township 27N, Range 02W, Section
2, parcel number 702024018. The purpose of this plan is to protect the stream from
degradation and provide habitat enhancement recommendations for priority species and
habitat in this project vicinity. The habitat management plan is prepared to meet
requirements of the Jefferson County Unified Development Code (adopted December 18,
2000) and is submitted in order to compensate for a buffer reduction on this private
property along the Little Quilcene River, which requires a ISO-foot restrictive buffer.
SITE DESCRIPTION
The site is located approximately 2 miles north of Quilcene, Washington, at 591 Lords
Lake Loop Road. West of the property is the Little Quilcene River (Figure 2). A site
visit was conducted on July 31, 2004, which consisted of a survey throughout the interior
of the property and a partial survey of the adjacent properties. Photographs taken of the
site are shown in Appendix A. The vegetation characteristics of the area and signs of
wildlife were noted throughout the survey. The flow ofthe Little Quilcene River was
relatively low at the time of the survey.
1
FIGURE 1
VICINITY MAP
QUILCENE quad
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Kunz Biological Consulting
R.A.Alexander Habitat Management Plan
August 13, 2004
Existing Vegetation and Conditions
The project site is situated on 2.2 acres at 591 Lords Lake Loop Road (Figure 3).
Vegetation on the site varies as portions were cleared for the installation of the well in
1985 and septic system in 1988 (Appendix B and C). The proposed building site is
partially open and consists primarily of ferns, trailing blackberry, vine maple, a variety of
grasses and a small stand of young red alder, 1-3" diameter breast height (dbh), on the
eastern portion adjacent to the Lords Lake Loop Road. The southwestern portion of the
property boundary borders the Little Quilcene River and slopes downward at a 75-800
slope for 85 feet to the riverbank. The steep bank to the river shows no sign of slides and
is well-vegetated with big leaf maple, western red cedar, Douglas fir, vine maple, alder,
Oregon grape, and ferns. This type of vegetation continues to the top of the slope and
transitions to the grassy level portion of the site. To the north of the bluff and buffer zone
the mixed 2nd growth stand is comprised of western red cedar, Douglas fir, western
hemlock, big leaf maple and red alder. The understory for this northern property consists
of ferns, vine maple, small alder, trailing blackberry and Oregon grape. Approximately
65-70 feet from the proposed building site to the north, the land slopes down to a small
depression/forested wetland, which is located on the northern property boundary line.
This wetland is approximately 500 square feet with no standing water at the time of site
inspection. This portion of the property will remain unaffected by the project as it is
located north of the proposed building site and no vegetation will be removed within this
area.
Impacts on wildlife would be minimal due to the lack of large trees on the building site.
The site supports the ecological function of protecting the riparian areas as it consists of
dense structural layers and contains a diversity of native plant species. The greenbelt
between the river and upland property protects and generally produces a higher quality
stream habitat for this area. The slope is stabilized by the vegetation and improves water
quality by reducing sedimentation and erosion and provides wildlife habitat. No trees
will be cut within the sloped portion of the property and only a few trees outside the 30
foot upland buffer zone and within the proposed building site will be removed.
A soil log conducted by Clayton Sartain, Engineer, (Appendix C) reports that the
property soil consists of brown silt loam and loamy sand.
PRIORITY HABITAT AND SPECIES
A recent WDFW database search was reviewed for sensitive or priority wildlife and/or
habitat that may occur within the project vicinity. This database indicates that WDFW
priority anadromous and resident fish are present in the Little Quilcene River. The
property is located approximately 0.5 miles southeast of a spotted owl management circle
(WDFW 2004).
Anadromous fish known to utilize the Little Quilcene River are fall Chinook, coho
'salmon, winter steelhead, and chum salmon and searun cutthroat (WDFW 2004 and
4
FIGURE 3 - LOT AND BUILDING PLAN
,,,0
Kunz Biological Consulting
R.A.Alexander Habitat Management Plan
August 13, 2004
StrearnNet 2004). WDFW priority resident fish present in this portion ofthe Little
Quilcene River include resident cutthroat and rainbow trout (StreamNet 2004).
Columbian black-tailed deer were observed in the vicinity of the project site. Columbian
black-tailed deer are also classified by the WDFW as a recreationally important species,
which are defined as species with high recreational importance or high public profile that
are vulnerable to habitat loss or degradation. Wildlife under this classification are game
species which are hunted, or otherwise harvested, by the public and are subject to hunting
and fishing regulations.
HABITAT MANAGEMENT
The maintenance of woody debris and riparian vegetation in and adjacent to streams is
important in providing wildlife habitat. The preservation and enhancement of both
horizontal and vertical structural plant diversity can be achieved by the retention and
development of shade tolerant understory trees, grasses and woody shrub plant species.
F or fish habitat enhancement, the maintenance of riparian vegetation is essential for
controlling stream temperatures, providing cover, and protecting against lateral erosion
(WDFW 1991). This vegetative buffer will provide erosion control and maintain
natural stream temperatures and the diversity of aquatic invertebrates (Mechan et al.
1977, Kuchell977, Newbold et al. 1980). The WDFW Management Recommendations
for cutthroat trout and steelhead include the following:
. Buffer zones of at least the width of the height of the tallest tree should be
maintained along stream banks.
. Road construction and maintenance activities should be avoided adjacent to
streams which provide fish habitat.
. In-stream structures such as bridges, piers, boat ramps, or culverts must not
impede the natural movements of these fish species.
. Waters inhabitated by these fish species should not be treated with metal based
herbicides during the period March 1 - June 15.
The proposed project is in compliance with all of the above WDFW recommendations.
Structural layers and diversity in species already occur on this property, which will create
habitat structure and opportunities for continued biological diversity. The large, downed
woody debris that occurs at the top of the slope will remain in order to define the buffer,
stabilize the top of the slope and provide habitat for wildlife including small mammals,
salamanders, insects and other arthropods. Although the upland portion of the property is
not functionally connected to the river, the owner will retain native vegetation and shrubs
from the top ofthe slope throughout the 30 foot buffer zone. The botanical and structural
diversity will be maintained throughout the property.
6
Kunz Biological Consulting
R.A.Alexander Habitat Management Plan
August 13, 2004
PROPOSED DEVELOPMENT
The single family residence proposal consists of constructing up to an approximately
1,500 square foot building with an access driveway and possible garage. The setback
buffer proposal is an approximate 85 foot buffer from the river to the top of the slope and
an additional 30 foot buffer from the top ofthe slope to the residence, drainfield and
driveway on the remaining level, buildable property. The size ofthe proposed
development consists of an approximate 30 X 45 foot building (1350 square feet). The
proposed building will be located in the existing partially cleared area. New single
family residences, with over 3,000 square feet of impervious surface, are required by
Jefferson County Stormwater Management Ordinance to provide a Small Parcel Erosion
and Sediment Control Plan. This project is exempt from this requirement due to its small
size. However, recommendations for stormwater management are incorporated in this
plan to provide maximum protection for stormwater entering the adjacent salmon-bearing
river. Erosion controls are presented in "Minimization of Construction Impacts".
Impacts on wildlife will be minimal due to the retention of most existing trees throughout
the property, with the exception of the removal of a small stand of red alder (1 - 3" dbh)
and four larger trees within the proposed building site. There are possibly four trees
larger than 6" dbh that may be removed in order to accommodate a 30 foot buffer from
the top of the slope and a 25 foot setback from Lords Lake Loop Road. The trees that
may be removed are a IS" dbh Douglas fir, 12" alder, II" dbh western hemlock and 14"
dbh western hemlock. No other trees greater than 6" dbh will be removed for the
proposed structure unless they present a safety hazard.
The existing channel of flowing water is approximately 85 feet from the top of the bluff.
The proposal is to maintain an additional 30 foot buffer from the top of the bluff to the
proposed project construction. The vegetation within this 30 foot buffer consists of a few
large western red cedar, red alder, big leaf maple, vine maple, ferns, salal, and Oregon
grape.
MINIMIZATION OF CONSTRUCTION IMPACTS
Erosion and Sediment Control
. Drainage plans will protect and prevent unacceptable impacts to the water quality
and stream channels from stormwater run off and erosion.
. No materials will be stockpiled near the stream. Excavated and imported material
will be stockpiled outside the buffer zone in the upland locations and will be
protected with plastic sheeting during construction to prevent runoff, erosion or
impact to the Little Quilcene River.
. Areas of exposed soil will be covered with a minimum of 2 inches of straw within
7 days of disturbance.
7
Knnl BiDIDI!;jJill CDnsulting
R.A.Alexander Habitat Management Plan
August 13, 2004
. Temporary erosion control measures such as sediment barriers and mulching will
be used as necessary after initial disturbance of the soil. These sediment barriers
will be installed along the edge of the construction area to contain spoils and
sediments. These temporary erosion controls will be properly maintained
throughout the construction (on a daily basis) and reinstalled as necessary (such as
after backfilling) until replaced by permanent erosion controls or until
construction is complete.
. Upland drainage will be directed away from the river channel and filtered through
a grassy swale or sediment trap to prevent erosion or impact to the Little Qui1cene
River.
. Runoff from house gutters will be directed away from the river channel and
filtered through a grassy swale or sediment trap before entering the river channel.
Buffer Protection
. Installation of temporary signage during construction in order to define buffer.
. Storage and preparation of materials will not be placed within buffers during
construction.
. Existing woody vegetation, which serves as a physical separation between the
river and residence within the buffer, will be retained. Preservation of all existing
trees and shrubs within the buffer area is critical in order to provide river
protection and enhancement.
. A permanent physical separation along the buffer will be installed after
construction, such as the placement of logs.
. Invasive species will be controlled and removed (such as Himalayan blackberry).
. To verify compliance with this plan, the project will be inspected during
construction and one year after construction completion.
CONCLUSIONS
This Priority Habitat and Species Management Plan has been prepared to meet the
requirements of an Administrative Reduction or Reasonable Economic Use Variance as
defined by the Jefferson County Community Development Department. This project site
adjacent to the Little Qui1cene River has a natural and established buffer that provides
riverbank: protection from erosion. Additionally, this riparian zone provides cover and
habitat and serves as a wildlife corridor along the river.
8
Kunz Biological Consulting
R.A.Alexander Habitat Management Plan
August 13, 2004
Site surveys and database research have indicated that there are priority habitat and
species located in the immediate project vicinity. Since the existing vegetation is already
dense and well established, no additional planting will be required. Additionally, the
retention of all trees and shrubs within the proposed 120 foot buffer will allow for the
continued plant community diversity and promote diversity in animal populations, as
well. The intent ofthis plan is to preserve existing conditions with a minimal amount of
clearing for the construction of a single family residence. Construction impacts will be
kept to a minimum. Compliance with this plan will be verified through site inspections
both during and after construction.
REFERENCES
Kuchel, C. R. 1977. Some aspects of the behavior and ecology of harlequin ducks in
Glacier National Park, Montana. Thesis, University of Montana, Missoula, Montana.
Meehan, W. R., F. J. Swanson, and J. R. Sedell. 1977. Influences of riparian vegetation
on aquatic ecosystems with particular reference to salmnid fishes and their food supply.
Pp. 137-145 in Proceed. Symp. On the Importance, Preservation and Management of the
Riparian Habitat. July 9, 1977, Tucson, AZ.
Newbold, J. D., D. C. Erman, and K. B. Roby. 1977. Effect oflogging on
macroinvertebrates in streams with and without buffer strips. J. Fish Aquat. Sci.,
37: 1076-1085.
StreamNet. 2004. Website with GIS Data for Anadromous and Resident Fish
Distribution.
WDFW. 1991. Management Recommendations for Washington's Priority Habitats and
Species. Elizabeth Rodrick and Ruth Milner, ed.
WDFW. 2004. Washington Department ofFish and Wildlife Habitat and Species
Database Report for T27R02W, Section 2.
9
APPENDIX A
PHOTOGRAPHS OF PROJECT AREA
ABOVE: VIEW OF PROPOSED BUILDING LOCATION
BELOW: VIEW NORTH FROM SEPTIC SITE
ABOVE: ALDER STAND WITHIN BUILDING SITE
BELOW: VIEW FROM BUILDING SITE TOWARD SEPTIC
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BELOW: VEGETATION ALONG NORTHERN BOUNDARY
APPENDIX B
WELL WATER REPORT
PAGE
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APPENDIX C
SEWAGE DISPOSAL PERMIT
.03/18/2004 15: 08 3503794473 JEFF CO DCD PAGE 82
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JNS1Allf:.R'S SIGNATURE . DATE DATE INSTALLED (1:1: 1 .U
I
JEFF. COUH'fY.
-v-.,.~_YE""~~
. Little Quilic:ene River
INSTALL NEW SYSTEM ua
SJTE . So. as' d.c...
2:!: acres
TYPE. OF . NO. OF
eUIl..DING Residence BEDROOMS
P~evious aite evaluation by
Health Department .
Yes X No
2 BASEMENT
SOIL TYPE DESCRIPTION
1) 1-2411 Type 3 soil..
sandy loam,
Dk bro. silty .
Organic root zone
Depth to maximum seanonal
lIater table ./ 4811 .~
$ource of potable water supply
Public Prlva1;:/ill X". .
Source type: Drilled' well.: .r"
-
,D1.lg woll '.:
Other ..
2)
24-48" Type 4u5 soiL Lt brl1. sandy
silt foam. Sticky w/moisture
(SoH In 24"'4811 lone varie!i between
. ..:.......- 3) soil fQgs - type 3-type 5)
.~;.
4)
;".~e.:~74.8~' . ~ /~.I.f' ."
:1.._ .__..~~.....~iz I-rf#.~~ . ,,-:o(t<<t:~..-.,-- .,. -:,.,.
I r J"F": ,1""-
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