HomeMy WebLinkAboutHabitat Managemnet Plan 936000216
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PRIORITY HABITAT AND SPECIES MANAGEMENT PLAN
Dickie Property
Jefferson County Project
February 2007
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Prepared by:
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Cindi Kunz
Wildlife scientist
Kunz Biological Consulting
780 Arcadia West
Port Townsend, WA 98368
cmkunz@olypen.com
(360) 385-6300
Kunz Biological Consulting
K. Dickie Habitat. Management Plan
February 5, 2007
KEViN DICKIE PROPERTY
PRIORITY HABITAT AND SPECIES MANAGEMENT PLAN
February 2007
INTRODUCTION
At the request of Kevin Dickie, landowner, a wildlife and critical habitat survey was
conducted for a proposed residential building construction. The purpose of the survey
was 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.
The Washington Department of Fish and Wildlife (WDFW) establish priority species and
critical habitat. 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 defined
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 in Brinnon, W A (FigUre 1). The
legal description is Township 26N, Range 02W, Section 23, parcel number 936000216.
The purpose of this plan is to protect the creek 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 an unnamed, intermittent
creek, which requires a 50-foot restrictive buffer.
SITE DESCRIPTION
The site is located due west of Highway 101 off Tog Road (Figure 2), at 283 Lee Way,
Brinnon, W A. A site visit was conducted on December 9,2006, which consisted of a
survey throughout 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, if any, were noted throughout the survey. The property lies
adjacent to an unnamed creek and the flow was very low at the time of the survey.
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Kunz Biological Consulting
K. Dickie Habitat Management Plan
February 5, 2007
Existinll Velletation and Conditions
The project site is located on 0.78 acres west of Highway 101 (Figure 3). The designated
building site is a cleared, open arealocated on the southwestern portion of the property,
as indicated in the photos (Appendix A). An unnamed, seasonal Type 5 creek runs north
of the proposed building site along the property line separating the landowner's two
parcels (#936000216 and #93000217). The level building site location was cleared in the
early 1990' s, 15 years prior to the septic system installation. This septic system extends
to the landowners northern lot (septic permit #: SEP05-00175 and parcel number
936000217). Lee Way and property boundary is located 30 feet from the proposed
building site. The vegetation. buffer located north, south and east of the proposed
building site is comprised of a mixed stand of cedar, Douglas fir, madrona, hemlock, big
leaf maple, and alder. The understory is blackberry, fern, and vine maple. The northern
property bordering the unnamed creek supports the ecological function of protecting
riparian areas, as it is comprised of dense structural layers with a diversity of native plant
species. The greenbelt will remain unaffected by the project. No trees or shrubs will be
removed from the project site, unless they form ahazard.
The greenbelt between the creek and upland property protects and generally produces a
higher quality riparian habitat for this area. Vegetation located on both sides of the creek
is well established, which improves water quality by reducing sedimentation and erosion'
and provides wildlife habitat. Impacts on wildlife will be minimal due to the lack of
trees or shrub vegetation on the building site.
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 species do not occur adjacent to this property. A bald eagle management area for
two eagle nests (#1104-1 and #1104-2) is located due east of the proposed site. Since
there will be no tree removal and the management area is outside the proposed
construction site, no affect is expected.
The WDFW database (WDFW 2006) and StreamNet (2007) did not indicate the presence
of anadromous or resident fish in the unnamed creekadjacent to the property. However,
the WDFW has classified the intermittent creek as a Type 5. stream, which requires a 50-
foot setback.
HABITAT MANAGEMENT
The maintenance of woody debris and riparian vegetation in and adjacent to streams is
important in providing wildlife habitat. The shrubs, tree roots and various groundcovers
stabilize, anchor and add strength to the soil. The preservation and enhancement of both
Figure 3 -
Lot and Building Plan
SITE PLAN
LEGAL DESCRIPTION:
SUBDMSlON: BRINNONWOtD
SECTION: 23
QlR SECTION: NE 1/4
TOWNSHIP: 26N
RANGE: 2W
BRlNNON
JEFFERSON COUNTY
WASHINGTON
ADDRESS: 283 lEE WAY.
BRINNON, WA 98320
,
Kunz Biological Consulting
K. Dickie Habitat Management Plan
February 5, 2007
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.
Plant roots slow and absorb runoff, releasing the water slowly to groundwater and
streams and back into the atmosphere. Vegetation also provides nutrients and habitat for
fish and wildlife (Murdoch and Cheo 1999). Riparian zones filter pollutants from
developed areas (Yates 1988).
The maintenance of riparian vegetation is essential for fish habitat enhancement by
controlling stream temperatures, providing cover, and protecting against lateral erosion
(WDFW 1991). The vegetative buffer provides erosion control, maintains natural stream
temperatures, and allows for diversity of aquatic invertebrates (Meachan et al. 1977 and
Newbold etal. 1980). Although this intermittent creek is ~ot a fish-bearing stre~ the
WDFW Management Recommendations for cutthroat trout and steelhead will be utilized.,
as follows:
. 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 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.
Increased structural layering and diversity in species occur on this property along the
entire northern property boundary. All native vegetation and shrubs will be retained
throughout the existing buffer and non-native, noxious vegetation will be remov~ if
needed.
The botanical and.structural diversity within this existing buffer will be increased an
additional 5 feet in average width by constructing a berm at the top of the slope above the
creek and planting additional trees and a shrub layer for habitat enhancement. The
objective of these plantings is to enhance flora and fauna throughout this project location.
Following is a proposed planting list for the project location, which will provide habitat
diversity for wildlife:
Western red cedar (Thuja plicata)
Western hemlock (Tsuga heterophylla)
Evergreen huckleberry (Vacinnium ovatum)
Red flowering currant (Ribes sanguineum)
Red osier dogwood (Cornus stoloniftra)
Rhododendron (Rhododendron macrophyllum)
Sitka spruce (Picea sitchensis)
Oregon grape (Mahonia aquafolium)
Native crabapple (Malasfuscia)
Madrona (Arbutus menziesii)
Vine maple (Acer circinatum)
Kunz Biological Consulting
K. Dickie Habitat Management Plan
February 5, 2007
A native ground cover or grass seed layer planted south of this tree/shrub berm adjacent
to the residence, will be comprised of the following proposed grass species and
compositions:
Red fescue (Festuca rubra var. commutata) 40%
Tufted hairgrass (Dechampsia cespitosa) 30%
Annual ryegrass (Lolium multiflorum) 20%
Alsike clover (Trifolium hybridum) 10%
Kinnikinnick (Arctostaphylos uva-ursi)
PROPOSED DEVELOPMENT
The single family residence proposal consists of constructing a structure with a 20' x 30'
building footprint with a gravel access driveway. The setback buffer from the center of
the creek will be approximately 44 feet in order to accommodate the residence and
driveway. This allows for the 25% reduction of the 50-foot easement from a single
family residence foundation. The septic system was installed in 2006. The pretreatment
unit and pump chamber septic tanks are located in the southwest comer of the property.
The community water line runs along Lee Way. Water and power lines have been
installed from the road at the western edge of the property to the building site (Figure 2).
No construction work will occur in the vicinity of the creek to install pipelines.
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 smaller size. However, recommendations for stormwater management are
incorporated in this plan to provide maximum protection for stormwater entering the
adjacent creek. Erosion controls are presented in "Minimization of Construction
Impacts" .
Impacts on wildlife will be minimal due to the retention of existing vegetation along the
creek bank, lack of habitat in the proposed building location, and implementation of
proposed habitat enhancements.
The existing channel of flowing water in this intermittent stream is approximately 44 feet
from the proposed building site. The area between the building site and the creek
consists ofa small, narrow buffer of trees and shrubs (approximately 30 feet in width)
and an approximately 15 foot width cleared north of the proposed building site. This
level area delineates the upland from the riparian zone adjacent to the creek (see Photos
in Appendix A). A vegetated berm will be constructed at the top of the riparian zone
slope to provide additional delineation and riparian zone protection.
Kunz Biological Consulting
K. Dickie Habitat Management Plan
February 5,2007
MINIMIZATION OF CONSTRUCTION IMPACTS
Erosion and Sediment Control
. Drainage plans will protect and prevent unacceptable impacts to the fresh water
quality and creek channels from stonn water runoff and erosion.
. No materials will be stockpiled near the creek.. Excavated and imported material
will be stockpiled outside the buffer in the upland locations and will be protected
with plastic sheeting during construction to prevent runoff to the creek area.
. Areas of exposed soil will be planted with the above listed vegetation or covered
with a minimum of 2 inches of straw within 7 days of disturbance.
. 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 creek and filtered through a
grassy swale or sediment trap to prevent erosion or imp~t to creek channel.
. Construction equipment will have drip pans to contain potential leaks from
equipment. Vehicle fueling will be conducted away from the. project site, which
is sufficient distance upland from the creek.
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, as well as the above listed proposed vegetation plantings, within
the buffer area is critical in order to provide creek protection and enhancement.
. To increase plant community diversity within this buffer, native trees, shrubs, and
~asses will be planted. This improved plant community will promote diversity in
animal populations, as well.
. To verify compliance with this plan, the project will be inspected during
construction and one year after construction completion.
Kunz Biological Consulting
K. Dickie Habitat Management Plan
February 5, 2007
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 an unnamed creek has a natural and established buffer that provides
protection from erosion. Additionally, this riparian zone provides cover and habitat and
serves as a wildlife corridor along the creek.
Site surveys and database research have indicated that there are no priority habitat and
species located in the immediate project vicinity. The proposed plantings of coniferous
and deciduous trees, shrubs and grasses will aid in providing a more diverse habitat for
wildlife within the proposed project vicinity. The primary purpose of this plan is to
further enhance the priority habitat adjacent to the proposed project and to minimize any
construction impacts.
Compliance with this plan will be verified through site inspections both dwing and after
construction.
REFERENCES
Mechan, W.R., F.J. Swanson, and J.R. Sedell. 1977. Influences of riparian vegetation on
aquatic ecosystems with particular reference to salmonid 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.
Murdoch, Tom and Martha Cheo. 1999. Streamkeeper's Field Guide. Adopt-A-Stream
Foundation, Everett, W A.
Newbold, J.D., D.C. Ennan, and K.B. Roby. 1977. Effect oflogging on
macroinvertebrates in streams with and without buffer strips. J. Fish Aquat. Sci.,
37: 1076-1085.
StreamNet. 2007. Website with GIS Data for AnadromouslResident Fish Distribution.
WDFW. 1991.. Management Recommendations for Washington's Priority Habitats and
Species. Elizabeth Rodrick and Ruth Milner, ed.
WDFW. 2006. Washington Department ofFish and Wildlife Habitat and Species
Database Report for T27 ROl W Section 19.
Yates, Steve. 1988. Adopting A Stream: A Northwest Handbook. University of
Washington Press, Seattle, W A.
P~oto above: Building site with septic tanks (photo facing east)
Photo below: Mea~~~~~:~..~~.~,.~~~lding setback fro~ stream
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Photo above: Proposed building site facing north. Proposed vegetative berm
will be constructed at the top of the slope.
Photo below: North of proposed building site towards stream and vegetative
buffer. This is where the proposed berm and plantings will be
constructed in order to further protect this riparian zone.
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P;hoto above: Building site.facing southern portion.ofproperty. Septic tanks
shown in background.