HomeMy WebLinkAboutHabitat Management Plan 50104105341 WOLF RD
HABITAT MANAGEMENT PLAN
MAY 10, 2021
BGE21_0300
BGE ENVIRONMENTAL, LLC.
WETLAND CONSULTING AND LAND USE PLANNING
41 WOLF RD
HABITAT MANAGEMENT PLAN
MAY 10, 2021
PROJECT LOCATION
41 WOLF RD
QUILCENE, WA 98376
TAX PARCEL
#501041053
S 4, T 25 N, R 01W, W.M.
PREPARED FOR
RICK GROSS
PO BOX 3010
SEQUIM, WA 98382
PREPARED BY
BGE ENVIRONMENTAL LLC
2102 BRASHEM AVE
BREMERTON, WA 98310
360.710.6066
www.bgeenvironmental.com
BGE21_0300
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41 WOLF RD HABITAT MANAGEMENT PLAN
INTRODUCTION
The proposed project is redevelopment over the existing use, slightly larger in area. The existing
use is non-conforming to the standard shoreline buffer of 150 ft and the stream buffer of 50 ft.
There are no other reasonable alternatives to support residential use of the parcel that results in
avoiding the stream and shoreline buffer.
Buffer modifications to the stream are defined as establishing the buffer to the existing access
and defined parking area. The impact is unavoidable. The project respectfully requests a buffer
reduction of forty (40) percent to comply with access and parking standards. Vegetation
alteration requires felling three mature red alders. The resultant stream buffer is established to
the perimeter of use and results in a buffer not less than 30 ft in width. The buffer modification
is not likely to have an adverse impact to the stream since the buffer is degraded and has a low
function supporting the associated Type N water, Chapter 18.22.640 of the Jefferson County
Code (JCC). The 5 ft setback is respected. A net gain of the buffers function and value is
anticipated with the proposed mitigation as recovery of native cover to the buffer.
The project respectfully requests a buffer reduction not less than 75 percent of the standard
shoreline buffer (JCC Chapter 18.25.270). The buffer is established at 112.5 ft. However, the
drainfield is closer to the shoreline than the established buffer. Shoreline buffer vegetation
disturbances include three mature Douglas fir, a coppiced hazelnut cluster, and some osoberry.
Upon construction retreat, the drainfield area shall provide dual use as a common area to the
shoreline. The 10 ft setback is respected. The proposed mitigation equally restores portions of
the shoreline buffer. The project preserves the ecological niche of the freshwater to marine
water confluence. No net loss of ecological functions and processes is achieved.
Mitigation for the buffer reductions is provided as 1,200 sq ft of restoration to degraded buffer.
Mitigation includes coniferous trees to the stream corridor and targets the lack in understory
with the installation of native shrubs and dense groundcover
This Habitat Management Plan (HMP) is provided for unavoidable buffer reductions to a Type N
water and the marine shoreline to Fisherman Harbor. The application of standards and
regulations applied for the project were completed under the guidance of JCC Chapter 18.22
Critical Areas and JCC Chapter 18.25 Shoreline Master Program and includes the following.
• Assessment of existing conditions;
• Assessment of priority habitat, species within the vicinity of the project;
• Impact assessment;
• Analysis of mitigation sequencing; and
• Mitigation plan.
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EXISTING CONDITIONS
The subject parcel is irregularly shaped, elongated from the north to south. The topography is a
gradual decline from the access to the existing structure and surrounding use. This existing use is
delineated in the east with a gradual top-of-slope to a moderate ravine and a Type N water. To
the south, the break in slope is more gradual, steepening with the approach as a moderate bluff
to the shoreline. Ordinary High Water Mark (OHWM) is delineated to the toe-of-slope along at
the vertical drop from the bank.
The parcel hosts a structure aligned along the western property boundary on a knoll like setting,
see Exhibit A. The existing and historic use is well observed to the surface. The entire parcel
setting is beneath a closed canopy of mixed mature native coniferous and deciduous trees.
Species include Douglas fir, Bigleaf maple, Western red cedar, and red alder. An understory is
absent within the use area surrounding the structure. Elsewhere the vegetation is rich with a
dense cover of Pacific rhododendron, evergreen huckleberry, salmonberry, osoberry,
oceanspray, red elderberry, and salal.
Groundcovers include bracken fern,
sword fern, lady fern, bleeding heart,
chickweed, ducks foot, and a variety of
grasses and weeds. Other nonnative,
noxious, or invasive species include
hedge laurel and bamboo.
A path is established along the creek to
the shoreline. The path crosses the
creek with a crude wooden bridge. A
ladder at the shoreline provides some
safety for the final drop to the beach.
The bank is a natural vertical from the
nearshore to the beach. The OHWM is
established at the toe-of-slope.
Surrounding land use include high,
moderate, and low land use. Character
is rural residential with large
undeveloped land tracts. Services are
Port Ludlow, Chimacum, Poulsbo.
The parcel habitat potential is native
and naturalized species.
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BACKGROUND INFORMATION
RESEARCH AND DATA SYNTHESIS
Background research and data review are essential for the assessment of known and
documented habitat and species within the vicinity of the project site. Data researched included
relevant mapping from U.S. Fish and Wildlife Service, Washington State Department of Fish and
Wildlife (WDFW), and Washington Department of Natural Resources (WDNR) Natural Heritage
Database. Reference sources are summarized and documented in Appendix A.
U.S. FISH & WILDLIFE SERVICE NATIONAL WETLAND INVENTORY (NWI)
The US Fish and Wildlife Service National Wetland Inventory identifies intertidal estuarine waters
to Fisherman Harbor. These waters are classified under the Cowardin system as E2USN.
System Estuarine (E): The Estuarine System consists of deepwater tidal habitats
and adjacent tidal wetlands that are usually semi-enclosed by land but have open,
partly obstructed, or sporadic access to the open ocean, and in which ocean water
is at least occasionally diluted by freshwater runoff from the land. The salinity may
be periodically increased above that of the open ocean by evaporation. Along
some low-energy coastlines, there is appreciable dilution of sea water.
Subsystem Intertidal (2): The substrate in these habitats is flooded and exposed
by tides; includes the associated splash zone.
Split Class Unconsolidated Shore (US): Includes all wetland habitats having two
characteristics: (1) unconsolidated substrates with less than 75 percent areal
cover of stones, boulders or bedrock and; (2) less than 30 percent areal cover of
vegetation. Landforms such as beaches, bars, and flats are included in the
Unconsolidated Shore class.
Water Regime Regularly Flooded (N): Tides alternately flood and expose the
substrate at least once daily.
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U.S. FISH & WILDLIFE SERVICE IPAC TRUST RESOURCES REPORT
The U.S. Fish & Wildlife IPaC Trust Resources Report identifies federally listed species and
designated critical habitats, Essential Fish Habitat (EFH), and/or Distinct Population Segment
(DPS). The report provides information for compliance with Endangered Species Act (ESA) listings
identified through USFWS and National Marine Fisheries Service (NMFS). The identified EFH or
DPS conform to the Magnuson Stevens Fishery Conservation and Management Act (Magnuson
Stevens Act). The following table identifies the occurrence of these species in or near the project
site.
ENDANGERED SPECIES AND HABITAT
Species ESU/DPS Federal Status
Designated Critical
Habitat
Marbled Murrelet
(Brachyramphus marmoratus) Washington Threatened Yes
Streaked Horned Lark
(Eremophila alpestris strigata)
Pierce County
Mason County Threatened Yes
Yellow-billed Cuckoo
(Coccyzus americanus) TBD Threatened None Currently
Bull Trout
(Salvelinus confluentus)
Coastal-Puget
Sound Threatened Yes
Dolly Varden
(Salvenlinus malma) TBD Threatened
PSAT Wherever found
FLOWERING PLANTS
Golden Paintbrush (Castillefa levisecta) Threatened
CRITICAL HABITATS
Potential effects to critical habitat(s) in this location must be analyzed along with the endangered
species themselves.
There are no critical habitats at this location
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MIGRATORY BIRDS
Migratory bird information listed below are birds of particular concern either because they occur
on the USFWS Birds of Conservation Concern (BCC) list or warrant special attention in the project
location.
Common Name (Genus species) Occurrence/Use
Bald Eagle (Haliaeetus leucocephalus) Breeds Jan 15 to April 30
Great blue heron (Ardea Herodias fannini) Breeds Mar 1 to Aug 21
Red-throated Loon (Gavia stellate) Breeds elsewhere
Rufous hummingbird (Selasphorus rufus) Breeds April 30 to July 21
There are no Wildlife Refuges or fish hatcheries in this location. Estuarine and Marine Wetlands
overlaps the property vicinity.
WDFW PRIORITY SPECIES AND HABITAT (PHS)
The Washington Department of Fish and Wildlife Priority Habitats and Species database identifies
estuarine and marine aquatic habitat in the project vicinity. In addition, the northern spotted
owl is represented is a masked polygon which represents species and/or habitat to the north of
the subject parcel. This species is a Federal ESA-listed Threatened species and a Washington
State listed Endangered species.
WDNR NATURAL HERITAGE DATABASE
According to Washington Department of Natural Resource (WDNR) records, no threatened or
endangered species of plants within the vicinity if the parcel.
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IMPACT ASSESSMENT
The proposed project is redevelopment over existing, see Exhibit B. The site design is
considerate to all JCC Titles providing drainfield, access and reuse to the structural footprint.
Due to the size, shape, and bounding critical areas, impacts to the stream and shoreline buffers
are unavoidable. Redevelopment is proposed as the most reasonable alternative available to
support the residential use. The assessed impacts are within a building envelop considered
existing nonconforming, see Exhibit C. To comply with current standards for the redevelopment,
reduction of buffers cannot be avoided. Mitigation is applied to ensure that the reduced
buffer(s) will not adversely affect the habitat function and values to the stream, Fish and Wildlife
Conservation Areas (FWCA), and that no net loss of shoreline ecological function is achieved.
The assessed impacts are located to historic use. This area is degraded having compromised
surfaces noted as typical paths and random materials (wood, broken concrete, denuded surfaces,
lawn, weeds, and forbs). Mixed mature native trees dominate the parcels complexity with a
closed canopy. Outside of the use areas, the vegetation cover is rich native shrubs and
groundcovers.
Actions of the project resulting in stream buffer impacts is from the establishment of the parcel
access off Wolf Rd, see Exhibit C. There is no vegetation to the surface. Three mature red alders
are present to the eastern side and need to be removed for construction logistics and the
establishment of on-site parking. The established stream buffer is at the approximate edge of
existing use. The resultant buffer ranges from 30 to 42 ft from stream. The 5 ft setback is
respected.
Similarly, the shoreline buffer impacts are limited to the existing use, see Exhibit C. The new
structure is slightly larger than the existing but is not set closer to the shoreline. The remainder
of the buffer impact is to surfaces that are mostly void of vegetation, exposed, and utilized for
residential parcels. There is no significant change to the use and character is anticipated. The
new structure is located off (landward) of the established shoreline buffer of 112.5 ft. The 10 ft
set back is applied, see Exhibit D. The drainfield is proposed in the shoreline buffer, below the
112.5 ft buffer. As we understand the design, two mature Douglas firs will be cut for the needs
of the drainfield, however the stumped roots will remain intact. Any additional vegetation
removed in this area is a coppiced Hazelnut and some osoberry. The vegetation impact is
minimal apart from the two conifers. Post construction the drainfield is pervious, commonly
grassed surface. It is reasonable to identify this area as a dual use providing the common area to
the shoreline.
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MITIGATION SEQUENCING
Permitted uses shall be designed and conducted to minimize, in so far as practical, any resultant
damage to the ecology and environments. Impacts shall be mitigated according to Chapter
18.22.660 JCC, in a sequential analysis to avoid, minimize and mitigate. The mitigation analysis
sequence for the shoreline in question is provided below.
MITIGATION MEASURE MITIGATED ACTION(S)
AVOID the impact altogether by
not taking a certain action or
parts of an action
• The project cannot completely avoid all impacts to the
shoreline buffer by avoiding certain actions or parts of
actions and still have a viable project.
MINIMIZE impacts by limiting
the degree or magnitude of the
action and its implementation
by using appropriate technology
or by taking affirmative steps to
avoid or reduce impacts
• The magnitude of the project has already been minimized
to the maximum extent practicable while still maintaining
enough developable area to have a viable compliant
project.
RECTIFY the impact by repairing,
rehabilitating, or restoring the
affected environment
• The affected environment will generally not be able to be
re-established, rehabilitated or restored. Impacts are
permanent.
REDUCE or eliminate the impact
over time by preservation and
maintenance operations
• The affected environment will generally not be able to be
re-established, rehabilitated or restored. Impacts are
permanent.
COMPENSATE for the impact by
replacing, enhancing, or
providing substitute resources
or environments
• Plant a minimum of twelve (12) native conifers.
• Restore areas of the established buffer currently
degraded or compromised in native vegetation cover.
MONITOR the impact and the
compensation project and take
appropriate corrective measures
• Implementation of mitigation plan completed prior to
receipt of Certificate of Occupancy pending seasonal
conditions persist.
• Five-year post planting compliance record.
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MITIGATION
This parcel is defined with a historic residential use. Outside of the observable use area exists a
closed native canopy and complex understory to a Type N water and the moderate bluff
shoreline to Fisherman Harbor. Project impacts are located to the existing use. Buffer
modifications are applied as the minimum necessary to delineate the existing use and
accommodate upgrades with the redevelopment. Mitigation potential is observed to the
perimeter of the existing use which is delineated as the established stream and shoreline buffer,
see Exhibit E.
The mitigation consists of twelve (12) native conifers and a variety of shrubs and groundcovers.
The approximate area of restoration is 1,200 sq ft. A total of fifty-four (54) shrubs should be
planted in groups with a dense spacing. The remainder of the mitigation area is to be infilled
with a mix of evergreen, fruiting, and flowering groundcovers. The established buffer shall be
retained as a rich native complex. Assess shall be retained and respects for shoreline access.
Native landscaping to the structure and associated use is recommended. Choose native, low
maintenance species of trees, shrubs, and groundcovers. Use deciduous, broad leaf evergreen,
and coniferous species. Wildflowers are aesthetically pleasing and are excellent habitat niches
for hummingbirds and butterflies. Denuded or bare soils should be avoided.
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GOALS AND STANDARDS
GOAL
Restore 1,200 sq ft of stream and shoreline buffer with native trees, shrubs and
groundcover.
PERFORMANCE STANDARDS
The standards listed below will be used to judge the success of the plan over time. If the
standards are met at the end of the five-year monitoring period, Jefferson County shall approve
as conditioned.
SURVIVAL
YEAR ONE
100% survival of all planted individuals at the end of Year One per the supplier contract.
This standard may be met through establishment of installed plants or by replanting as
necessary to achieve the required numbers.
YEAR FIVE
100% survival of all planted trees at the end of Year Five. 80% survival of all planted shrubs
at the end of Year Five. This standard may be met through establishment of installed plants
or by replanting as necessary to achieve the required numbers.
NOTE: Individual groundcover species is difficult to track. Areas of significant mortality shall be
estimated and replanted at densities enough to establish 100 percent cover to the established
buffer.
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NATIVE WOODY VEGETATION COVER
YEAR THREE
Achieve at least 70% cover of native vegetation by the end of Year Three. Volunteer native
species may count towards this standard.
YEAR FIVE
Achieve 100% cover of native vegetation by the end of Year Five. Volunteer native species
may count towards this standard.
INVASIVE SPECIES REMOVAL AND CONTROL
No tolerance of invasive species in the established wetland and stream buffer. Species
intolerance includes all Class A, B, or C noxious weeds as listed by the Washington state
Noxious Weed Control Board.
A conceptual planting plan is provided in Exhibit E. Adaptive management is acceptable for
placement and species alternatives with prior approval from BGE. Once planted the details and
vegetation specifications shall be documented in an as-built.
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PLANTING DETAILS AND SPECIFICATIONS
The provided planting plan is conceptual for the restoration area, see Exhibit E. Generally the
species prescribed are chosen to have a high probability of establishment in the landscape and
provide natural function and parcel aesthetics. Alternatives are acceptable as long the species
are native and commonly occur within the Central Hood Canal lowlands. Counts and quantities
require a pre-construction review prior to purchasing materials to ensure that the area is
adequately covered to meet the performance standards long-term. The species detail and
summary for buffer plantings is provided below.
SPECIES COMMON NAME QNTY SPACING SIZE MIN
TREES
Pseudotsuga menziesii
Thuja plicata
Douglas fir
Western red cedar
8
4
10 ft o.c.
10 ft o.c.
1 gal
1 gal
SHRUBS
Gaultheria shallon
Symphoricarpos albus
Myrica gale
Salal
Snowberry
Sweet gale
18
18
18
4 ft o.c.
4 ft o.c.
4 ft o.c.
1 gal
1 gal
1 gal
GROUNDCOVER
Arctostaphylos uva-ursi
Armeria maritima
Sedum spathuliforium
Lupinus polyphyllus
Kinnikinnick
Sea thrift
Broad-leaved stonecrop
Large leaf Lupine
INFILL
--
--
--
--
2 ft o.c.
2 ft o.c.
2 ft o.c.
2 ft o.c.
4” pot
4” pot
4” pot
4” pot
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CONSTRUCTION AND SPECIFICATIONS
The details provided in this section are combined principles and practices necessary to
implement the conceptual mitigation plan.
GENERAL NOTES
BGE Environmental personnel shall monitor the following:
1) A conceptual planting plan is provided with the proposed mitigation. Action areas are
identified as buffer restoration. Conceptual planting guidelines are designed with an
anticipated standard error and allows for flexibility to the landscape conditions.
a. The recommended mitigation shall be overseen by BGE for all actions to ensure
that the standards and conditions of the mitigation are met. Planting schedules
and placements will be reviewed, approved and recorded by BGE to produce an as
built and baseline for measuring mitigation success.
2) Review of restoration area, post-planting.
3) Creation and submittal of as-built report.
4) Restoration specialist required for yearly monitoring and Five-Year compliance
assessment
PROJECT SEQUENCING
Planting shall occur during the dormant season, October 1 through March 31. Site preparation,
may be completed in the dry season but shall be stabilized with clean straw in the interim of
scheduled planting and installation of silt fencing in accordance with the SWPPP prior to initiating
any work within the restoration area.
1) Prepare the planting surface.
2) Amend existing topsoil, if deemed necessary, by incorporating two inches of compost into
the top six inches of soil.
3) Prepare a planting pit for each plant and install per planting details.
4) Once planted, cover the entire planting area with a three-inch layer of mulch.
5) As-built production and submittal to Jefferson County within 60 days of planting.
6) Annual monitoring, late summer, and reporting Year 5.
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EROSION CONTROL & SITE PREPARATION
Temporary erosion and sediment control (TESC) measures shall be implemented under the
guidance of approval conditions using BMP’s outlined in the project’s SWPPP and TESC Plan
prepared by the Project Engineer. Approval by the responsible Restoration Specialist prior to
mowing, hand-clearing and planting activities on-site is recommended.
PLANT SCHEDULING, SPECIES & DENSITY
Planting should occur between October 1 and March 31. All materials to be used on the site will
be nursery grown stock from a reputable, local source. Only native species are to be used; no
hybrids or cultivars will be allowed. All plant material shall be inspected by the
consultant/contractor upon delivery.
Plant material provided will be typical of their species or variety and shall be sound, healthy,
vigorous plants free from defects, and all forms of disease and infestation. Plant material not
conforming to the specifications will be rejected and replaced by the contractor or supplier.
Rejected plant materials shall be immediately removed from the site.
PRODUCT HANDLING, DELIVERY & STORAGE
All precautions customary in good trade practice shall be taken in preparing plants for moving.
Workmanship that fails to meet industry standards will be rejected. Plants will be packed,
transported, and handled with care to ensure protection against injury and from drying out. If
plants cannot be planted immediately upon delivery they should be protected with soil, wet peat
moss, or in a manner acceptable to the project biologist.
Plants, fertilizer, and mulch not installed immediately upon delivery shall be secured on the site
to prevent theft or tampering. No plant shall be bound with rope or wire in a manner that could
damage or break the branches. Plants transported on open vehicles should be secured with a
protective covering to prevent windburn.
PREPARATION & INSTALLATION OF PLANT MATERIALS
Contractor shall verify the location of all elements of the mitigation plan with the materials count
upon clearing of invasive vegetation and prepping surface for installation. Plant quantities are
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based on field measurements and density calculations which have a standard error association
with planning and implementation. Locations of proposed materials are conceptual,
representation natural distribution character, and may be moved for consistency in final grade,
topographical features, and defined use. All installed vegetation will be marked to a site plan for
general areas and quantities. The documented actions will be used to produce an as-built once
the mitigation actions are complete.
Circular plant pits with vertical sides will be excavated for all bare root and container stock. The
pits should be at least 6 inches greater in diameter than the root mass or container. The pit
should accommodate the entire root system. The bottom of each pit will be scarified to a depth
of 4 inches. Set plant material upright in the planting pit to proper grade and alignment. Water
plants thoroughly midway through backfilling and add slow release Agroform tablets.
Water pits again upon completion of backfilling. No filling should occur around trunks or stems.
Do not use frozen or muddy mixtures for backfilling. Form a ring of soil around the edge of each
planting pit to retain water. Once planted, the entire area shall be covered with clean straw or
mulch to a depth where the denuded surface is not visible.
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MONITORING
This monitoring program is designed to track the success of the mitigation actions over time by
measuring the degree to which the performance standards listed above are being met.
Monitoring for evaluation of the standards is defined below.
YEAR DATE MAINTENANCE
REVIEW
PERFORMANCE
MONITORING
REPORT
DUE
Implementation/Planting: As-built production and submittal within 60 days to Jefferson
County Department of Community Development
1
Spring X
Fall X X
2
Spring X
Fall X X
3 Spring X
Fall X X
4 Spring X
Fall X X
5
Spring X
Fall X X X FINAL
Monitoring shall occur annually for all monitoring years to ensure vegetation is establishing,
healthy, and likely to sustain ecological integrity for long term protection on shoreline ecological
processes. Quantitative monitoring shall occur for all years. A progress report documenting
qualitative and quantitative measures of success cumulated for each monitoring year will be
submitted to Jefferson County for Year 5, for consideration of approval as conditioned.
Additional monitoring needs are at the recommendation of BGE and discretion of Applicant,
Owner.
During monitoring inspection, BGE Environmental shall quantify plant survival, estimate
groundcover establishment, and measure native and invasive cover. Photo-stations shall be
established once the planted materials are in place. Cover measurements will be completed as
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visual estimates and/or random sectional plots within the planting area. Areas outside the plots,
if used, will be visually monitored to verify that performance standards are being met, with
attention to invasive species at the perimeter (off-site). Monitoring will occur in the late summer
or early fall and will record the following.
1) Counts of surviving and dead/dying vegetation by species in the planting areas.
2) Estimates of groundcover planting survival, noting any areas of significant mortality.
3) Estimates of native woody species cover within random plot.
4) Estimates of invasive species cover within random plot.
5) Photographic documentation from permanent stations.
6) Intrusions into the planting areas, erosion, vandalism, trash, and other actions
detrimental to the overall health of the planting area.
7) Recommendations for maintenance in the mitigation area.
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MAINTENANCE
The applicant is committed to compliance with the proposed restoration plan and overall success
of the project. The site will be maintained for five years following completion of the plant
installation. Anticipated actions and necessary guidelines to meet the performance standards are
as follows:
1) Replace each plant found dead in the summer monitoring visit after the first year of planting
and subsequent years if mortality approaches 20 percent of the total individuals.
2) Invasive species maintenance plan:
a. Any invasive species that crop up, Himalayan blackberry, Japanese knotweed, Scotch
broom, English ivy, or other invasive vegetation, will be dug out by hand to prevent
establishment and disruption of native species.
3) At least twice a year, hand remove all competing weeds and weed roots from beneath each
installed plant and any desirable volunteer vegetation to eighteen (18) inches from the main
plant stem. Weeding should occur as needed during the spring and summer. Frequent
weeding will result in lower mortality and lower plant replacement costs.
4) Do not weed the area near the plant bases with string trimmer (weed whacker).
5) Mulch the weeded areas beneath each shrub with wood chips as necessary to maintain a
minimum two-inch thick, eighteen-inch diameter mulch ring around shrubs.
6) Temporary irrigation may be necessary and installed at the recommendation of the
restoration specialist. Irrigation shall operate to ensure that the planted area receives a
minimum of one inch of water per week from June 1 through September 30.
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CONTINGENCY
There is an applied standard error of success applied to the buffer enhancement area due to the
existing drainfield. As the exact area (boundary) of the drainfield is unknown, the limits of the
planted buffer may suffer mortality. In the case that survival consistently fails after replacing
individual post installation year one, the limits of the enhancement should be reviewed by BGE
for contingency measures to ensure no net loss is achieved.
If any part of the planting area fails to satisfy the goals and performance standards of this plan to
such an extent that the failure cannot be adequately addressed through standard maintenance
activities, a contingency plan shall be developed. A detailed contingency plan cannot be
developed until the specific items that need to be addressed are known. Compliance with the
installation procedures and maintenance plans are measures to properly promote a successful
restoration. Where the performance is less than satisfactory, attention shall be given to, but not
limited to, soil conditions, species installation, and temporal variations. Adaptive management
actions taken to ensure success, when practical, are an acceptable means to ensure survival and
growth of the planted species.
Wetland Consulting & Land Use Planning
BGE Environmental, LLC
EXHIBIT A EXISTING CONDITIONS BGE21_0300
SFR
SCALE TO MAP
NOT A SURVEY
0 4020
GROSS
41 WOLF RD
501041053
150 FT
SHORELINE
BUFFER
200 FT
SHORELINE
JURISDICTION
•DOUGLAS FIR
•WESTERN RED CEDAR
•BIG LEAF MAPLE
•RED ALDER
•SALAL
•OCEANSPRAY
•RED HUCKLEBERRY
•EVERGREEN HUCKLEBERRY
•OSOBERRY
•RHODODENDRON
•OREGON GRAPE
•SWORD FERN
FISHERMAN
HARBOR
50 FT
STREAM
BUFFER
VEGETATION INVENTORY 1
WOLF RD
ACCESS
•SALMONBERRY
•LADY FERN
•RED ELDERBERRY
•BLEEDING HEART
•BRACKEN FERN
•CHICKWEED
•BAMBOO
APPROXIMATE
EXISTING
USE
1 SHADING REPRESENTS APPROXIMATE LIMITS OF VEGETATION
BENEATH THE CANOPY
Wetland Consulting & Land Use Planning
BGE Environmental, LLC
EXHIBIT B PROPOSED OVER EXISTING BGE21_0300
SFR
SCALE TO MAP
NOT A SURVEY
0 4020
GROSS
41 WOLF RD
501041053
150 FT
SHORELINE
BUFFER
200 FT
SHORELINE
JURISDICTION
FISHERMAN
HARBOR
WOLF RD
ACCESS
DRAINFIELD
RESERVE
50 FT
STREAM
BUFFER
APPROXIMATE
EXISTING
USE
Wetland Consulting & Land Use Planning
BGE Environmental, LLC
EXHIBIT C IMPACT ASSESSMENT BGE21_0300
SFR
SCALE TO MAP
NOT A SURVEY
0 4020
GROSS
41 WOLF RD
501041053
150 FT
SHORELINE
BUFFER
NEW IMPERVIOUS
FISHERMAN
HARBOR
WOLF RD
ACCESS
DRAINFIELD
RESERVE
UNCHANGED EXISTING USE
50 FT
STREAM
BUFFER
112.5 FT
SHORELINE
BUFFER
APPROXIMATE
EXISTING
USE
Wetland Consulting & Land Use Planning
BGE Environmental, LLC
EXHIBIT D ESTABLISHED BUFFERS BGE21_0300
SFR
SCALE TO MAP
NOT A SURVEY
0 4020
GROSS
41 WOLF RD
501041053
FISHERMAN
HARBOR
WOLF RD
DRAINFIELD
RESERVE
50 FT
STREAM
BUFFER
112.5 FT
SHORELINE
BUFFER
30 ft
36 ft
42 ft
NOTES:
PLANT ALL TREES (12) TO STREAM BUFFER.
REMAINDER OF BUFFER TO BE RESTORED AND INFILLED
WITH A MIX OF NATIVE SHRUBS AND GROUNDCOVERS.
PLANT SHRUBS IN GROUPS OF LIKE SPECIES OFF-SET
FROM EACH OTHER. GROUND COVER IS PROVIDED
FOR INFILL TO GAPS BETWEEN SHRUBS. ADAPTIVE
MANAGEMENT PRACTICES APPLIED FOR EXISTING
VEGETATION OR EXITING TRAILS FOR ACCESS TO
THE STREAM AND SHORELINE. LANDSCAPE NEW
STRUCTURE WITH NATIVE SPECIES IS
RECOMMENDED FOR LOW MAINTENANCE
AND SUPPORT TO REGIONAL HABITAT
FEATURES AND LIFE CYCLE NICHES.
ALTERNATIVE SPECIES FOR SHRUB &
GROUNDCOVER IS PERMISSABLE AS
LONG AS THE SPECIES ARE NATIVE.
Wetland Consulting & Land Use Planning
BGE Environmental, LLC
EXHIBIT E CONCEPTUAL PLANTING PLAN BGE21_0300
SCALE TO MAP
NOT A SURVEY
0 4020
GROSS
41 WOLF RD
501041053
200 FT
SHORELINE
JURISDICTION
WOLF RD
112.5 FT
SHORELINE
BUFFER
50 FT
STREAM
BUFFER
SCIENTIFIC NAME COMMON NAME QTY SPACING
SIZE
MIN
TREES
PSEUDOTSUGA MENZIESII
THUJA PLICATA
SHRUBS
GAULTHERIA SHALLON
SYMPHORICARPOS ALBUS
MYRICA GALE
GROUNDCOVER
ARCTOSTAPHYLOS UVA-URSI
ARMERIA MARITIMA
SEDUM SPATHULIFOLIUM
LUPINUS POLYPHYLLUS
DOUGLAS FIR
WESTERN RED CEDAR
SALAL
SNOWBERRY
SWEET GALE
KNNIKINNICK
SEA THRIFT
BROAD-LEAVED STONECROP
LARGE LEAF LUPINE
8
4
18
18
18
--
--
--
--
10’ O.C.
10’ O.C.
4’ O.C.
4’ O.C.
4’ O.C.
2’ O.C.
2’ O.C.
2’ O.C.
2’ O.C.
1 GAL
1 GAL
1 GAL
1 GAL
1 GAL
4” POT
4” POT
4” POT
4” POT
150 FT
SHORELINE
BUFFER
SHORELINE BUFFER
COMMON AREA
BGE ENVIRONMENTAL, LLC MAY 25, 2021 19 | PAGE
41 WOLF RD HABITAT MANAGEMENT PLAN
REFERENCES
Creative Design Solutions. Septic system design Gross parcel #501041053. Date
01/27/2021
ESA Adolfson, et all. Jefferson County shoreline Master Program Update Project. Final
Shoreline Inventory and Characterization Report. (Final – Revised November 2008)
ESA Adolfson, et all. Jefferson County Shoreline Master Program Update Project. Final
Shoreline Restoration Plan. Ecology Grant #G0600343. October 2008.
Stratum Group. Geologic Hazard Assessment JC Parcel 501041053. August 18, 2021.
Washington Department of Fish and Wildlife. 2002. Landscaping for Wildlife in the Pacific
Northwest. University of Washington Press Seattle & London.
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
PHOTOGRAPHS
ENTRY AND PARKING OFF WOLF RD
BREAK IN SLOPE TO RAVINE (LEFT), EXISTING USE TYPICAL
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
EXISTING USE TYPICAL. VIEW FROM WOLF RD
VIEW TO OFF-SITE STREAM CORRIDOR
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
EXISTING USE TYPICAL
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
SHORELINE FACING FRONTAGE
DRAINFIELD AREA
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
SHORELINE BUFFER TYPICAL
VIEW TOWARD TOP-OF-SLOPE FROM RAVINE
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
STREAM COORIDOR TOWARDS SHORELINE. PATH TYPICAL
CONFLUENCE OF STREAM TO SHORELINE
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
SHORELINE TYPICAL
BGE ENVIRONMENTAL, LLC MAY 25, 2021
41 WOLF RD HABITAT MANAGEMENT PLAN BGE21_0300
APPENDIX A – REFERENCE SOURCES
WETLAND DELINEATION
USACE 1987
Wetland
Delineation
Manual
http://el.erdc.usace.army.
mil/elpubs/pdf/wlman87.p
df
Environmental Laboratory. 1987. Corps of Engineers Wetlands
Delineation Manual. Technical Report Y-87-1, US Army Engineer
Waterways Experiment Station, Vicksburg, Mississippi.
Western
Mountains,
Valleys, and Coast
Region Interim
Regional
Supplement
http://www.usace.army.m
il/CECW/Documents/cecw
o/reg/west_mt_finalsupp.
pdf
U.S. Army Corps of Engineers. 2010. Regional Supplement to the
Corps of Engineers Wetland Delineation Manual: Western
Mountains, Valleys, and Coast Region (Version 2.0), ed. J. S.
Wakeley, R. W. Lichvar, and C. V. Noble. ERDC/EL TR-10-3.
Vicksburg, MS: U.S. Army Engineer Research and Development
Center.
WETLAND CLASSIFICATION
USFWS /
Cowardin
Classification
System
http://www.fws.gov/nwi/P
ubs_Reports/Class_Manua
l/class_titlepg.htm
Cowardin, L. M., V. Carter, F. C. Golet, E. T. LaRoe. 1979.
Classification of wetlands and deepwater habitats of the United
States. Government Printing Office, Washington, D.C.
Hydrogeomorphic
Classification
(HGM) System
http://el.erdc.usace.army.
mil/wetlands/pdfs/wrpde4
.pdf
Brinson, M. M. (1993). “A hydrogeomorphic classification for
wetlands,” Technical Report WRP-DE-4, U.S. Army Engineer
Waterways Experiment Station, Vicksburg, MS.
WETLAND RATING
Washington State
Wetland Rating
System
https://fortress.wa.gov/ec
y/publications/SummaryPa
ges/1406029.html
Hruby. 2014 Update. Washington State wetland rating system
for western Washington –Revised. Publication #14-06-029.
WETLAND INDICATOR STATUS
Northwest
(Region 9) (Reed,
1988) and
Northwest
(Region 9)
Supplement
(Reed et al., 1993)
http://www.fws.gov/nwi/b
ha/list88.html
Reed, P.B. Jr. 1988. National list of plant species that occur in
wetlands: Washington. Biological Report NERC-88/18.47 for
National Wetlands Inventory, Washington, D.C.
Reed, P.B. Jr. 1993. Northwest supplement (Region 9) species
with a change in indicator status or added to the Northwest
1988 list, wetland plants of the state of Washington 1988. U.S.
Department of Interior Fish and Wildlife Service WELUT - 88
(26.9), Washington, D.C.
SOILS DATA
NRCS Soil Survey http://websoilsurvey.nrcs.
usda.gov/app/WebSoilSurv
ey.aspx
Website GIS data based upon:
McMurphy, Carl J. 1980. Soil Survey of King County,
Washington. United States Department of Agriculture, Soil
Conservation Service in cooperation with Washington State
Department of Natural Resources.
THREATENED AND ENDANGERED SPECIES
Washington
Natural Heritage
Program
http://www.dnr.wa.gov/n
hp/
and
http://www1.dnr.wa.gov/
nhp/refdesk/datasearch/w
nhpwetlands.pdf
Washington Natural Heritage Program (Data published
10/15/08). Endangered, threatened, and sensitive plants of
Washington. Washington State Department of Natural
Resources, Washington Natural Heritage Program, Olympia, WA
Washington
Priority Habitats
and Species
http://wdfw.wa.gov/hab/p
hspage.htm
Priority Habitats and Species (PHS) Program Washington
Department of Fish and Wildlife (WDFW).
Jefferson County, WA., Pro-West &³These data are provided on an "AS-IS" basis, without warranty of any type, expressed or implied, including but not limited to any warranty as to their performance, merchantability, or fitness for any particular purpose.This map is not a substitute for accurate field surveys or for locating actual property lines and any adjacent features.
Jefferson County, WA
Date: 3/25/20211:2,257
Wetlands
Source: Esri, Maxar, GeoEye, Earthstar Geographics, CNES/Airbus DS,USDA, USGS, AeroGRID, IGN, and the GIS User Community
Wetlands
Estuarine and Marine Deepwater
Estuarine and Marine Wetland
Freshwater Emergent Wetland
Freshwater Forested/Shrub Wetland
Freshwater Pond
Lake
Other
Riverine
May 10, 2021
0 0.1 0.20.05 mi
0 0.2 0.40.1 km
1:7,284
This page was produced by the NWI mapperNational Wetlands Inventory (NWI)
This map is for general reference only. The US Fish and Wildlife Service is not responsible for the accuracy or currentness of the base data shown on this map. All wetlands related data should be used in accordance with the layer metadata found on the Wetlands Mapper web site.
5/10/2021 PHS Report
1/3
PHS Species/Habitats Overview:
Occurence Name Federal Status State Status Generalized Location
Esturine Zone N/A N/A No
Estuarine and Marine Wetland N/A N/A No
Northern Spotted Owl Threatened Endangered Yes
Priority Habitats and Species on the Web
Report Date: 05/10/2021
PHS Species/Habitats Details:
5/10/2021 PHS Report
2/3
Esturine Zone
Priority Area Aquatic Habitat
Accuracy 1/4 mile (Quarter Section)
Notes
BAY/ESTUARY-COASTAL ZONE ATLAS CODE 54-MODERATELY
PROTECTED MARINE EMBAYMENTS WITH FREE
CONNECTIONS WITH THE OPEN SEA. BLUFFS, REACH
SUBSTRATES MARSHES, EELGRASS BEDS, AND OTHER
INTERTIDAL HABITATS ARE ASSOCIATED WITH IT.
Source Record 904754
Source Dataset PHSREGION
Source Name JOHNSON, TERRY
Source Entity WA Dept. of Fish and Wildlife
Federal Status N/A
State Status N/A
PHS Listing Status PHS Listed Occurrence
Sensitive N
SGCN N
Display Resolution AS MAPPED
ManagementRecommendations http://wdfw.wa.gov/conservation/habitat/planning/ahg/index.html
Geometry Type Polygons
Estuarine and Marine Wetland
Priority Area Aquatic Habitat
Site Name N/A
Accuracy NA
Notes Wetland System: Estuarine and Marine Wetland - NWI Code:
E2USN
Source Dataset NWIWetlands
Source Name Not Given
Source Entity US Fish and Wildlife Service
Federal Status N/A
State Status N/A
PHS Listing Status PHS Listed Occurrence
Sensitive N
SGCN N
Display Resolution AS MAPPED
ManagementRecommendations http://www.ecy.wa.gov/programs/sea/wetlands/bas/index.html
Geometry Type Polygons
5/10/2021 PHS Report
3/3
Northern Spotted Owl
Scientific Name Strix occidentalis
Notes
This polygon mask represents one or more records of the above
species or habitat occurrence. Contact PHS Data Release (360-902-
2543) for obtaining information about masked sensitive species and
habitats.
Federal Status Threatened
State Status Endangered
PHS Listing Status PHS Listed Occurrence
Sensitive Y
SGCN Y
Display Resolution TOWNSHIP
ManagementRecommendations http://wdfw.wa.gov/publications/pub.php?id=00026
DISCLAIMER. This report includes information that the Washington Department of Fish and Wildlife (WDFW) maintains in a central computer database. It is not an attempt to provide you with an official agency response as to the impacts of your project on fish and wildlife. This information only documents the location of fish and wildlife resources to the best of our knowledge. It is not a complete inventory and it is important to note that fish and wildlife resources may occur in areas not currently known to WDFW biologists, or in areas for which comprehensive
surveys have not been conducted. Site specific surveys are frequently necesssary to rule out the presence of priority resources. Locations of fish and wildlife resources are subject to
variation caused by disturbance, changes in season and weather, and other factors. WDFW does not recommend using reports more than six months old.
WA Wetlands of High Conservation Value
County of Kitsap, Bureau of Land Management, Esri, HERE, Garmin,
Counties
5/10/2021, 11:41:34 AM 0 0.2 0.40.1 mi
0 0.3 0.60.15 km
1:18,056
Washington Natural Heritage Program
County of Kitsap, Bureau of Land Management, Esri, HERE, Garmin, INCREMENT P, NGA, USGS | U.S. Fish and Wildlife Service, National Standards and Support Team, wetlands_team@fws.gov | Washington State Department of Natural Resources | Washington
2102 Brashem Ave
Bremerton, WA 98310
(360) 710-6066
www.bgeenvironmental.com
BGE ENVIRONMENTAL, LLC.
Wetland Consulting and Land Use Planning