HomeMy WebLinkAboutLog199
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G e oE ngi n ec r 5 \
Habitat Management Plan
Ludlow Cbve . Residentia I Development,
Port~udl()wj Washiogton
June6,20Q3
Pqrt Ludl()vvASsociates,lnc~
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GeOeEngineers
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June 6, 2003
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Port Ludlow Associates, Inc.
70 Breaker Lane
Port Ludlow, Washington 98365
Attention: Mark Dorsey
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We are pleased to submit our final report entitled "Habitat Management Plan, Ludlow Cove
Residential Development, Port Ludlow, Washington."
We appreciate the opportunity to be of service to you on this project. Please contact us if you
have questions, or require clarification regarding thc information presented in this report.
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Respectfully submitted,
GeoEnginccrs, Inc.
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Lisa Berntsen, PWS
Principal
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Attachments
File No. 10622-001-00
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Applied Environmental Services
1550 Woodridge Dr. SE
Port Orchard. WA 98366
Telephone (360) 769-8400
Fax (360) 769.8700
www.geoengineers.com
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TABLE OF CONTENTS
Pace No.
INTRODUCTION AND UNDERSTANDING...... ... ............. ............ ........ ......... ....... ..... .... .... ..............1
SCOPE........ ....................... ............... '............. ...... .................. ............... ................. .... .....................2
METHODS............................................................, ................ ......' ............................... ............... ......2
RESULTS................... ............................ ....... ................................... ...............................................,3
PRIORITY HABITATS AND SPECIES 4
Site Visit 5
Vegetation 5
Predicted Wildlife Species Use 6
DISCUSSION.. ... .... .......... .... ........., .............. .............. ........... .... ........... ................. ..... .... ........ ........ ..8
PROPOSED PROJECT 8
Wetland Areas 9
Wetland Buffer Areas 10
Native Growth Areas 10
Shoreline Setback Areas 10
Other Wildlife Features 11
Walking Trail System 11
POTENTIALlMPACTS 11
Water Quality of Streams 11
Great Blue Heron Habitat 12
Other Species Habitat 12
CONSTRUCTION AND OCCUPATIONAL PHASES 12
CONCLUSiONS..................................... ..,...................................................... .,. ............................ 13
REFERENCES ................ .......... ........ ................. ........... ... .... ....... .... .... .... ............ ............. ......... .....15
TABLES Pace No.
Table 1 - Anadromous Species in the Port Ludlow Bay Watershed 4
Table 2 - Possible Wildlife Species Use for the Ludlow Cover Property 6
Table 3 - Native Species to be Used for Revegetation of the Ludlow Cove Property 9
FIGURES Ficure No.
Ludlow Cove Vicinity Map 1
Ludlow Cove National Wetlands Inventory Map 2
Soil Survey of Jefferson County, Washington 3
Aerial Photograph of Ludlow Cove Site 4
Wetland Buffers and Shoreline Setback Areas 5
APPENDICES Pace No.
Appendix A - Site Photographs
Appendix B - Lisa Berntsen Resume
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HABITAT MANAGEMENT PLAN
LUDLOW COVE RESIDENTIAL DEVELOPMENT
PORT lUDLOW, WASHINGTON
FOR
PORT LUDLOW ASSOCIATES, INC,
INTRODUCTION AND UNDERSTANDING
This report presents the Habitat Management Plan (HMP) for the Ludlow Cove Residential
Development proposed by Port Ludlow Associates, Inc. (PLA). The development property is
26.75 acres ofland south of the intersection of Oak Bay Road and Paradise Road and west of the
North Bay Lane Condominiums along the shoreline of Port Ludlow Bay. The development will
be 17 residential lots, two future development tracts (Tracts A and B, which consists of 15.65
acres) and three open-space tracts on the subject property. The property is located in Section 17,
Township 28 north, Range I east. Figure I, Vicinity Map, shows the property and the
surrounding area.
Any proposed project in Jefferson County is subject to county code and in particular the
Interim Critical Areas Ordinance (05-0509-94). Jefferson County has identified areas considered
to be Critical Habitat based on their association with priority species listed by the Washington
State Department of Fish and Wildlife. The interim Jefferson County Critical Areas Ordinance
requires the need for a HMP for proposed development of critical areas, fish and wildlife habitat
or stream buffers. Jefferson County allows applicants to propose site-specific protection
measures, in the form of a HMP. An HMP demonstrates that protection of the ecosystem
functions and values will be provided.
PLA received a Shoreline Substantial Development Permit (SDP97-00009) on August 2,
2002. The SDP states that the development shall be undertaken subject to the applicable policies
and performance standards of the Jefferson County Shoreline Management Master Program and
36 conditions described therein. As part of Case #SUB95-00003, PLA must complete a Habitat
Management Plan for the proj ect in order to address Mitigation Measure 11 of the Final Modified
Mitigated Determination of Non-Significance (FMMDNS). Shoreline restoration has been
proposed by PLA for the project to avoid significant adverse impacts to wildlife habitat. The
shoreline restoration includes replanting with native trees and plants of historically disturbed
stream, wetland and marine shoreline buffer. As part of the "record" for the approval of Ludlow
Cove development (1995 through August 2, 2002), three off-site spaces have been set aside for
conservancy. These spaces are two islands called "The Twins" (Figure I), riparian zone of
Ludlow Creek southwest of the site, and a S-acre parcel adjacent to the site.
An important element of mitigation for Ludlow Cove Residential Development is the
reduction of the time period that heavy machinery and noise disturbances occur during the
construction phase of the development. Work requiring heavy equipment such as road building,
grubbing, cutting and filling will be conducted in one session, thus avoiding the prolonged
disturbance of the environment that would occur if portions of the work were done incrementally
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over several sessions. Following the completion of the work requiring heavy equipment, the
restoration and stabilization phases of the shoreline and buffers will be completed.
SCOPE
The Jefferson County Code (JCC 18.15.395) calls for specific report elements to be addressed
in the HMP. The scope of this investigation was focused toward meeting the following HMP
elements:
1. A description of the nature, density and intensity of the proposed development in sufficient
detail to alIow analysis of such land use change upon identified wildlife habitat;
2. The applicant's analysis of the effect of the proposed development, activity or land use
change upon the wildlife species identified by the Washington State Department of Fish &
Wildlife within the identified priority habitat, utilizing the management guidelines;
3. A plan by the applicant that shall explain how any adverse impacts created by the
development will be mitigated. Possible mitigation measures include, but are not limited to:
a. Establishment of buffer zones;
b. Preservation of critically important plants and trees;
c. Limitation of access to habitat area;
d. Seasonal restriction of construction activities; and
e. Establishing a timetable for periodic review of the plan.
To address the AMP elements, specific tasks were accomplished:
. Perform a detailed site habitat assessment that includes a basin description; verify
wetland areas, onsite stream status, and saltwater shoreline conditions.
. Note any fish presence and threatened and endangered species within the subject property
boundaries.
. Address the specific mitigation measures stated in Mitigation Measures 11 and 12 of the
FMMDNS. These impacts are:
. lmpacts to the quality of the streams located onthe subject property.
. Potential reduction of wildlife habitat related to the State-monitored species status of
the great blue heron (Ardea herodias).
. Evaluate existing conditions regarding aquatic and upland habitats.
. Analyze the effect of the proposed project on existing species.
. Determine feasibility of proposed project, with regards to existing ordinances.
. IdentifY any possible mitigation options that will restore habitat and compensate for the
impacts or modifications to the protection zone.
METHODS
To prepare for the site visit and habitat characterization, a search for pertinent and applicable
literature was conducted. Data sources that were reviewed for this HMP included a topographic
map (printed from TOPO 2001), the United States Fish and Wildlife Service (USFWS 1987)
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National Wetlands Inventory (NWI) map, Soil Survey of Jefferson County, Washington (USDA,
NRCS fonnerly SCS, 1975), the Washington State Department of Fish and Wildlife Priority
Habitat and Species (PHS) map, the Wetland Assessment of the Ludlow Cove Property by
Raedeke Associates (June 23, 1997) and aerial photographs as available.
Using field data and the resources listed above, GeoEngineers biologists determined the
existing site conditions on the subject property. Current habitat protection measures, including
buffers and setbacks, and land-use intensity, were noted. This data was used to determine the
possible effect(s) on any threatened, endangered or sensitive species and habitats within 150 feet
of the subject property.
Habitat areas were defined based upon site observations and descriptions from the U.S. Forest
Service Publication titled The Management of Wildlife and Fish Habitats in Forests of Western
Oregon and Washington (Brown, 1985). Brown (1985) has developed a two-part labeling system
to characterize specific habitat types for western Washington and Oregon. The first part of the
label identifies the plant community. Three wetland types, 12 upland types, and five special and
unique habitats of plant communities are defined. These range from lowland herbaceous
wetlands to subalpine forest parks. The second part of the habitat label refers to condition, which
means the size and density of plants in any given area. Brown (1985) was also consulted to
determine the potential occurrence of animal species based upon the comparison of the observed
habitat conditions on the site and on reported species-specific habitat preferences. It must be
noted that this comparison is not intended to be a fonnal wildlife survey of the property and it is
not an inventory of documented use. This list offers potential wildlife species use based on site
conditions, size of the parcel, and surrounding land uses.
Fish and wildlife habitat types found onsite could be broken up into four general systems:
shoreline, stream, wetland and upland (Cowardin, 1979). Topography and hydric conditions
usually define these systems. Upland habitats, dryland areas, typically have less hydrology than
the preceding areas. Upland areas adjacent to streams and wetlands include buffer areas that limit
development in order to preserve wildlife habitat and protect aquatic resources. Upland habitat is
available to development subject to zoning and other land use restrictions.
RESULTS
The USGS and NWI maps are tools used to assist with the overall site investigation.
Figure 2, Ludlow Cove National Wetland Inventory Map, shows several wetlands in the vicinity
of the site. The wetlands are mapped as Estuarine, Intertidal, Unconsolidated Shore and
Regularly Flooded. NWI maps are produced from interpretation of aerial photographs and
topographic maps and are therefore limited to the time they are produced. Forested areas are not
commonly identified as wetlands on NWI maps and changes in land use, forestry or development
may not be evident on these maps. This is also true for this site. The delineated wetlands
component, shown on the site plan, was not shown on the NWI map of the area. Raedeke
Associates delineated three wetlands on the site as part of their Wetland Assessment (June 23,
1997). These wetlands will be discussed later in the HMP.
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Figure 3, Soil Survey of Jefferson County, Washington, identifies Everett and Alderwood
series as the soils present onsite. The Everett series, designated as Eve on Figure 3, is a gravelly
sandy loam, 0 to 15 percent slopes, The Everett series, formed in glacial outwash, is excessively
drained and permeability is rapid. The Alderwood series, designated AIC on Figure 3, is a
gravelly sandy loam, 0 to 15 percent slopes. The Alderwood series, formed in glacial till, is
moderately well drained and permeability is moderately rapid, with a very slowly permeable
cemented layer (USDA, 1975).
Figure 4, Aerial Photograph of Ludlow Cove Site, is an aerial photograph of the project site
and neighboring vicinity. The aerial photograph, dated June 21, 1990, has been included to
illustrate the development conditions in the vicinity of the project area. Surrounding land use
consists of commercial development (Port Ludlow Village) to the north and residential
developments to the west and across the bay to the south.
PRIORITY HABITATS AND SPECIES
The property is located within the Port Ludlow Bay watershed. Protected or priority fish
resources in Hood Canal watershed include the presence of Hood Canal summer chum salmon
(Onchorhyncus keto). Table I illustrates when listed anadromous species may inhabit the Port
Ludlow marine area. Information was taken from the Washington State Salmon and Steel head
Stock Inventory (WDFW 1992), Hood CanaVEastem Strait of Juan de Fuca Summer Chum
Habitat Recovery Plan (Point No Point Treaty Council 1999), and the Catalog of Washington
Streams and Salmon Utilization (Williams 1975).
Common Name System Adult Presence Juvenile Presence
Coho Hood Canal September - October April- May
Summer Chum Hood Canal July - September January - April
Fall Chum Hood Canal October - January February - May
Winter steelhead Hood Canal December - May April - June
TABLE 1
ANADROMOUS SPECIES IN THE
PORT LUDLOW BAY WATERSHED
PHS maps provided by Washington Department of Fish and Wildlife (WDFW) do not
identify the small streams within the boundary of the site to support anadromous fish species.
These streams, described below, discharge into Port Ludlow (see Figure 4).
Great blue heron (A. herodias) rookeries have been documented by the Washington
Department of Fish and Wildlife, one less than 1 mile south and another approximately one mile
southeast of the project site. Twenty-five active nests were observed in alders along Paradise Bay
Road in 1999. A great blue heron was observed within the proposed project location during the
site investigation.=
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Site Visit
On March 19, 2003, GeoEngineers perfonned a site assessment. A Wetland Buffers and
Shoreline Setbacks Area exhibit (Figure 5) was developed by ESM Consulting Engineers and
modified by GeoEngineers. Areas shown and designated on Figure 5 are used as reference within
this HMP. Survey waypoints labeled on Figure 5 are also used as reference points within the
descriptions herein. Photographs taken during the site visit, and described herein, are presented
in Appendix A. During the visit the weather was overcast and raining lightly. The region had
experienced several days of significant rainfall prior to the visit.
There are two streams within the property. An unnamed stream (herein referred to as the west
stream) flows through Wetland #1 (Raedeke Associates, 1997) generally from the west to the east
along the northern border of Tract B. The west stream empties into Port Ludlow Bay at
approximately the midpoint of the shoreline. A larger stream (herein referred to as the east
stream) flows northwest to southeast and is within a deep ravine. The east stream, classified by
WDFW as a Type 3 stream, empties into the bay west of the Beach Point Picnic Area (Figure 5).
Upland areas generally slope from north to south toward the shoreline of Port Ludlow Bay.
The slopes of the upland areas range from less than 5 to 30 percent grade with a steep slopes (>50
percent) near the stream in the eastern portion of the property and shoreline banks. A 30-foot
building setback would be maintained from the ordinary high water line along the shoreline.
Three wetland areas have been delineated on the property. These wetlands are shown on
Figure 5 as Wetland # I, #2 and #3. Wetland # 1 is located in the western portion of the property
and is associated with the west stream. Buffer averaging was proposed for Wetland # I, a Class n
wetland based on the Ecology (1991) wetland rating system (Raedeke Associates, 1997).
Wetlands #2 and #3 are located within the deep ravine in which the east stream flows. Wetlands 2
and 3 are both Class III wetlands. The buffers for Wetlands '2 and 3 will be the required 50 feet
(Raedeke Associates, 1997).
Vegetation
The majority of the property consists of upland habitat. The specific habitat type identified
onsite is a conifer-hardwood forest, closed sapling-pole-sawtimber stand condition. In this
habitat type, hardwoods make up 30 to 70 percent of the tree crown cover. The vegetation in the
vicinity of the existing and proposed property consists of a matUre upland forest community
consisting of species such as Douglas fir (Pseudotsuga menziesii), western red cedar (Thuja
plica/a), western hemlock (Tsuga he/erophylla), red alder (Alnus rubra), and bigleaf maple (Acer
macrophyllum). The understory vegetation condition is also quite heavily vegetated, consisting
of: red elderberry (Sambucus racemosa), sword fern (Polystichum munUum), salmonberry (Rubus
spectabilis), red huckleberry (Vaccinium parvifolium), evergreen huckleberry (Vaccinium
ovatum), Solomon's seal (Smilacina racemosa), salal (Gaul/heria shallon), sapling trees (of the
same species above), and Oregon grape (Mahonia nervosa) along with several miscellaneous
herbaceous species.
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Vegetation conditions of the wetlands include salal (G. shallon) on hummocks, skunk
cabbage (Lysichiton americanum), salmonberry (R. spectabi/is), sapling trees (maple and alder),
Oregon grape (M nervosa), along with several miscellaneous herbaceous species.
Shoreline habitat forms the southern border of the property. Vegetation conditions of the
shoreline include miscellaneous saltgrasses (Distich lis spicata), isolated pickleweed (Salicornia
virginica), sea lettuce (Ulvafenestrata) along with several miscellaneous herbaceous species.
Historically disturbed areas such as roads and open areas are either bare of vegetation,
graveled or overgrown with invasive species such as Himalayan blackberry (Rubus procerus),
and other more desirable species like alder (Alnus rubra), salmonberry (R. spectabilis) and
willow.
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Predicted Wildlife Species Use
Species presence was verified by direct observations, signs (tracks, nests, etc.) and general
habitat available to determine the likelihood of a particular species presence onsite. The seasonal
and often secretive habits of many wildlife species make it difficult to confirm habitat use in only
one of a few site visits. Specific habitat areas were defined based upon site observations as well
as descriptions from the U.S. Forest Service publication titled The Management of Wildlife and
Fish Habitats in Forests of Western Oregon and Washington (Brown, 1985).
The expected occurrence of animal species is based upon available habitat characteristics and
reported habitat preferences. The species listing is intended to be rather all encompassing with
respect to any wildlife known to have preferred habitat similar to that offered on the proposed
project site. For general wildlife inventories it is typically assumed that if the required or
preferred habitat is present the wildlife species are likely to be present. Table 2 presents this list
by common and scientific names of those wildlife species likely to be present on the site at least
on a seasonal basis.
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Common Name Scientific Name Observed Expected
Amphibians
Ensatina Ensatina eschscholtzi X
Roughskin newt Taricha granulose X
Clouded salamander Ane/des ferreus X
Westem toad Sufo bareas X
Pacific tree frog Hyla reg/lla X
Red-legged froo Rana aurora X
Reptiles
Painted turtle Chrysemys pieta X
Western pond turtle C/emmys marmorata X
Northem alligator lizard Elgaria eoerulea X
Westem fence lizard Sceloporus occidentaJis X
Ring-neck snake Diadophis punetatus X
Westem garter snake Thamnophls spp. X
Common garter snake Thamnoph/s sirtaJis X
TABLE 2
POSSIBLE WILDLIFE SPECIES USE FOR THE
LUDLOW COVE PROPERTY
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Common Name Scientific Name Observed Expected
Birds
Bald eagle Hafiaeetus /eucocepha/us X
Sharp-shinned hawk Accipiter striaWs X
Coopers hawk Accipiter cooperii X
Merlin Falco co/umbarlus X
Ruffed grouse Sonasa unbe/fus X
Rock dove Columba /lvia X
Band-tailed pigeon Columba fasciata X
Mourning dove Zenaida macroura X
Anna's hummingbird Cafypte anna X
Rufous hummingbird Sefasphorus Rufous X
Allen's hummingbird Sefasphorus sasin X
Homed lark Eremophifa alpestris X
Purple martin Progne subis X
Barn swallow Hirundo rustica X
Stellar jay Cyanocitta stellen X
American Robin Turdus migratorius X
Northern flicker CoIaptes auratus X
Downy Woodpecker Picoides pubescens X
Hermit thrush Catharus guttatus X
Townsend's solitaire Myadestes townsendi X
Orange-crowned warbler Vermivora celata X
Nashville warbler Vermivora runcapi/la X
Yellow-rumped warbler Dendroica coronata X
Black-throated gray warbler Dene/roica nigrescens X
Great blue heron Ardea herodias X X
Black-headed grosbeak Pheucticus mefanocephafus X
Spotted towhee Plpifo erylhrophthalamus X
Chipping sparrow Spize//a passerina X
Fox sparrow Passerella iIIaca X
Song sparrow Melospiza melodia X
Dark-eyed junco Junco hyemalis X
House Sparrow Passer domesticus X
American crow Corvus brachyrhynchos X
Black-capped chickadee Parus atricapif/us X
Chestnut- backed chickadee Parus rufescens X
Golden-crowned kinglet Regulus satrapa X
Solitary vireo Viera sofilar/us X
TABLE 2 (continued)
POSSIBLE WILDLIFE SPECIES USE FOR THE
LUDLOW COVE PROPERTY
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Common Name Scientific Name Observed Expected
Mammals
Opossum Didelphis virgiiniana X
Coast mole Scapsnus orsrius X
Long-legged myotis Myotis volans X
Coyote Canis latrans X
Gray fox Urocyon cinereoargenleus X
" X
Raccoon Procyon J%r
Spotted skunk SpiJogaJe pu/orius X
Mule deerl Black-tal1ed deer OdocoiJeus hemionus X
Western gray squirrel Scurius griseus X
Chipmunk Tamias spp. X
Porcupine Ereth/zon dorsatum X
Dusky-footed wood rat Neotoma fuscipes X
TABLE 2 (continued)
POSSIBLE WILDLIFE SPECIES USE FOR THE
LUDLOW COVE PROPERTY
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Notes:
Shaded species are those confirmed State Status of Endangered andlor Threatened. Information on species
presented in this lable has been adapted trom Manaaement of Wildlife and Fish Habitats in Forests of Western
Dreaon and Washinaton Part I and II, 1985, edited by Reade Brown,
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DISCUSSION
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PROPOSED PROJECT
The 26.75-acrc site is currel1lly undeveloped with some open areas historically used for log
storage. Most of the property is vegetated with a mature forest of mixed coniferous and
deciduous trees. The understory is also mature and well established with a variety of plant
species. Wetland areas are densely vegetated well established. Disturbed arcas and open arcas arc
either unvegetated or overgrown with invasive species. There are two streams that transverse the
property. A gravel road enters the property from Paradise Bay Road and leads to a large open
area (Track B on Figure 5) near the shoreline. A system of nature trails runs along the northern
portion of the property and to Beach Point Picnic Area (Figure 5). The proposed project will
consist of shoreline restoration and revegetation of wetland and wetland buffer areas. The sito:
will require a Forest Practice Application approval to remove merchantable timber. The clearing
limits on this site have been approved and are currently staked. The application will be
selectively logging outsite of the clearing limits on an as-needed basis. Forested areas will be left
on the site within wetlands, wetland buffers, steep slopes, and shoreline areas with native growth.
The extent of the landscaping of the property for this project will be predicated on the type of
area, as follows:
. Wetland Areas: All existing trees and other vegetation is to be left undisturbed, except
as shown on Figure 5 and where previous disturbance occurred and restoration is
planned.
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. Wetland Buffer Areas: Existing trees and other vegetation is to be left undisturbed,
except that some larger trees and shrubs along the shoreline may be limbed up or pruned
to enhance views. Previously denuded areas within wetland buffer areas will be replanted
with appropriate native plant material as described in the Landscape Plan and listed
herein in Table 3.
. Native Growth Areas: The native vegetation theme will be retained. Management of
vegetation in these areas may include pruning, limbing or removal of existing trees or
vegetation for partial view enhancement; and removal of diseased, invasive or
undesirable species and enhancement with planting of native species (Table 3),
. Shoreline Area (Tracts A and B): A shoreline Landscape Plan, in preparation, will
retain the native vegetation theme. The plan shall allow fot the management of vegetation
in these areas, including pruning, limbing or removal of existing trees or vegetation for
view enhancement and removal of diseased, invasive or undesirable species and
enhancement with planting of native species (Table 3).
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Common Name Scientific Name Use Areas
Slough sedge Carex obnupta Wetlands
Willow, undergreen Salix commutata Wetlands
Sword fern Po/yst/chum munitum Wetlands, Wetland Buffers
Salal Gaultheria shall on Wetlands, Wetland Buffers
Indian plum Oem/eria cerasiformis Wetlands, Wetland Buffers
Salmonberry Rubus spectabilis Wetlands, Wetland Buffers
Willow, Hooker's Sa/;x hookeriana Wetland Buffers, Shoreline
Douglas Fir Pseudotsuga menliesii Wetland Buffers, Shoreline
Saltgrasses Distich/is spicata Shoreline
Dune grass Efymus mollis Shoreline
Twinberry Lonicera invofucrata Shoreline
Shore pine Pinus contorta Shoreline
Wild rose Rosa nutkana Shoreline
TABLE 3
NATIVE SPECIES TO BE USED FOR REVEGETATION OF THE
LUDLOW COVE PROPERTY
Wetland Areas
As previously stated, the vegetation in the wetland areas will remain undisturbed, Historical
use of the area has impacted asmaU area of Wetland #1 between survey point (SP) 2794 and
2795 (Figure 5). The brush that was pushed into the wetland (Photograph A-I) will be removed
and the soil will be left as undisturbed as possible and replanting will occur if necessary. For the
disturbed area of Wetland #1 between SP2795 and SP2797 (Photograph A-2), fill will be
removed if necessary, clean soil will be brought in and the area will be revegetated with wetland
species such as slough sedge (Carex obnupta), willow (Salix c0111mutata) and Indian plum
(Oemleria cerasiformis).
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Wetland Buffer Areas
To show the outline of the buffer areas based on butTer averaging, the exhibit of Figure 6
Area of Wetland and Shoreline Buffer Averaging was developed. The project will create buffers
zones 25 feet from the wetlands and streams. In the previously cleared area from SP2789 to
SP2794 (Photograph A-3), the invasive species such as Himalayan blackberry will be removed
and the buffer will be revegetated with native species such as Salmonberry and Indian plum in the
wet areas and salal, sword fern and Douglas fir in the drier areas. No clearing or revegetation will
be done within the buffer area between SP2797 and SP2798 (Photograph A-4). Between SP2798
and SP2801 (Photograph A-5), near the west stream, selective clearing of invasive species will be
done without disturbing or removing the existing sword fern. At the trail crossing of the west
stream near SP2798 to near SP2764 (Photograph A-6), selective clearing of invasive species,
selective pruning, limbing, and removal of alder, and revegetation as necessary will be done.
There are numerous logs in this area remaining from previous use of the property. The majority
of the existing logs in this area are to remain others will be removed.
Native Growth Areas
The native vegetation themewill be retained for the project. Forested and wetland areas with
established native vegetation that have no invasive species will not be disturbed.
Shoreline Setback Areas
Shoreline setback areas will be maintained along Port Ludlow Bay 30 feet from either the
Ordinary High Water Line (OHWL) or from the crest of the bank if the bank is over 10 feet high
(Figure 6). From the western extent of the shoreline setback from SP2833 to SP2821, mostly
along the shoreline of Tract A, the shoreline will remain undisturbed. From SP2821 to SP2801,
along the shoreline of Tract B, the shoreline will undergo extensive vegetation management. The
invasive species will be removed and the area will be revegetated with native species. Existing
logs will remain in place. Berms and large piles of fill located outside the buffer area, e.g. at
SP2923 (Photograph A-7) shall either be removed, landscaped, or modified to conform to natural
topography. A large cement structure (Photograph A-8) and logs (Photograph A-9) are located on
the shoreline where historically logs were skidded to the bay. Soil will be brought in to contour
the ground and partially cover the exposed vertical face on the landward side of each. This area
will be revegetated with native species. The historical nature of this area will be retained.
Along the shoreline of Tract C between the west stream and Beach Point Picnic Area
(Figure 5), selective clearing of invasive species, selective pruning, limbing, and removal of
alder, and revegetation as necessary will be done. For the vegetation management of the shoreline
setback areas at Beach Point Picnic Area (Figure 5) between SP2931 to SP2936 (Photographs
A-IO and A-II), invasive species such as Himalayan blackberry will be removed and revegetated
with native species. The vegetation within the shoreline setback area from SP2136 to the
southeast property comer at SP2668 (Photograph A-12) will be left undisturbed.
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The forthcoming Landscape Plan will contain the complete list of species that will be used for
revegetation in the shoreline setback areas. In general, species to be used in this area for
revegetation will include wild rose (Rosa nu/kana), dune grass (Elymus mollis), willow (Salix
hookeriana), saltgrass (D. spkata), Douglas fir and twinberry (Lonicera involucra/a).
Other Wildlife Features
Areas of the property contain abundant logs left over from the historical use of the site. A
majority of these logs will be left in place to provide habitat. Therefore, there is no need to import
large woody debris for habitat enhancement on the property. Bird boxes will be added to the site
to provide nesting habitat. Their locations will be shown within the landscape plan.
Walking Trail System
An intricate walking trail system exists in the Port Ludlow area. Portions of the walking trail
exist on the property along Paradise Bay Road and Oak Bay Road. New trails proposed for the
property will be integrated with the existing trails. The new trails will reach to Beach Point
Picnic Area and traverse the ravine of the east stream. A picnic area is to be provided for wildlife
viewing. The trails will be several feet wide with a wood chip or gravel base. Engineered
crossings of streams will be done such that the existing flow is unimpeded and the structure will
be esthetically pleasing and ecologically sensitive. Further details of the walking trails will be
provided in the Landscape Plan. This trail system will address Shoreline SDP Condition 8.
To mitigate impacts to the wetlands, that portion of the trail located within Wetland #l's
buffer shall be abandoned and replanted with native vegetation consistent (FMMDNS Measure
7). The WDFW will be contacted regarding WDFW's requirements for Hydraulic Project
Approval to construct a bridge over the stream (FMMDNS Measure 9).
POTENTIAL IMPACTS
As part of the FMMDNS, several mitigation measures were stated. The following section
addresses the specific mitigation measures of the potential impacts.
Water Quality of Streams
The water quality of the streams and the related wetlands located on the property will be
maintained for the project. Forested buffer and wetland areas around the east stream will not be
disturbed. The wetlands and wetland buffers will be enhanced and revegetated. Permanent
physical separations along the boundary of the streamside buffer will be installed and
permanently maintained (FMMDNS Measure 13). The buffer perimeters will be marked
(FMMDNS Measure 14). The signage for the buffer perimeters of both the wetland and streams
will be similar to those previously approved in other projects in Port Ludlow. The buffers will be
posted with permanent signage constructed of placards on 2~inch diameter PVC posts. The posts
will be 6 feet above ground and set 3 feet into the ground.
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Great Blue Heron Habitat
The habitat requirements of the great blue heron include colony breeding in nests in tall trees
near wetlands and forage areas near the colony. The mitigation .measures to address these
requirements are the maintenance and enhancement of the wetland and shoreline areas and related
buffers. These measures will protect the feeding areas near the existing colonies. Nesting and
perch habitat of the shoreline and wetland canopy will be maintained, with much of the tree
canopy layer of the wetland, shoreline and buffer corridors remaining undisturbed. Again, the file
for this project includes mitigation measures in the form of conservation areas (e.g. "The Twins")
for this site.
Other Species Habitat
Of the species expected to occur on the site, most bird, bat and terrestrial mammal groups
should be relatively unaffected by the project. Although some habitat will be affected by the
clearing of the 17 lots and logging, the project will maintain and enhance habitat for these species
in most of the other areas of the property. Those species dependent upon small, discreet habitats
such as forest dwelling amphibians will be displaced by the project.
CONSTRUCTION AND OCCUPATIONAL PHASES
An increase in impervious surfaces is an expected result from the proposed project. Storm
water is a major force behind soil erosion in urban and developed areas. Impermeable surfaces
such as roads, rooftops and parking lots cause more rain to run off at accelerated rates and less
water seeps into the soil (Leedy and Adams 1984). Increased runoff from the developed area will
require adequate treatment to prevent decreases in water quality, increases in erosion, or changes
in local hydrographic conditions. The proposed project has included appropriate stormwater
features to trap and treat runoff prior to discharge into the bay.
Best Management Practices will be followed throughout the construction phase. Appropriate
erosion control devices such as; silt fencing, mulch berms, and erosion control matting will be
used during all aspects of construction to prevent erosion and runoff into the stream.
Construction activities during the driest season of the year minimize the risk of erosion related
impacts to downstream resources. It is recommended that construction staging and debris
stockpiling be confined to discreet areas of the site to minimize native vegetation disturbances.
No construction debris will be placed in the stream buffer or along steeper portions ofthe site.
During the occupation phase of the project, residents will be made aware of the responsibility
associated with living in close proximity to stream environments. Soil or yard waste must not be
dumped over the slope or into the stream buffer. Native vegetation will be encouraged to
dominate the property not closely associated with the dwelling units. Landscaping will target
native species and wildlife habitat features such as downed logs and small wet cells (man.made
wetlands) that trap landscape runoff and create seasonal wet pockets.
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An important goal of the construction phase is the reduction of the time period that heavy
machinery and noise disturbances occur. This will largely address FMMDNS Measures 18, 19,20
and 21. Construction sequencing on this property will begin with the installation of the erosion
control devices (silt fences at the toe of slopes, hay-bale barricades, etc.) as required by the Storm
Water Site Plan (Shoreline SOP Condition 2). Secondly, logging outside the marked clearing
limits will occur. Thirdly, clearing, grubbing and grading will take place in the roadways and
utility corridors. All major cuts and fills will occur at this time (Shoreline SDP Conditions 23 and
24). Work requiring heavy equipment such as logging, road building, grubbing, cutting and filling
will occur as one event, thus avoiding the prolonged disturbance of the environment as would be
the case if the work occurred over several sessions. Coincidentally with, or immediately
subsequent to, the completion of the work requiring heavy equipment, the restoration and
stabilization phases will be conducted. These phases include the application of mulch and
hydroseed, stabilization of cut and filled areas, construction of bioswales, and the planting of
revegetated areas in the late fall.
CONCLUSIONS
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The 26.75-acre site is designed and permitted to support 17 residential lots. The Habitat
Management Plan provided describes the current conditions of the entire site, possible wildlife
use based upon vegetation characteristics, and outlines separate treatment areas and prescriptives
throughout the wetland buffer and shoreline setback areas.
Key features ofthe plan include:
. Restoration of impacted wetland buffer areas through revegetation with native species.
. Restoration of the shoreline area (near the existing west stream and Beach Point Picnic
Area) through selective removal of invasive species and revegetation.
. Restoration of the shoreline area in the vicinity of the old log storage and skid area. The
applicant will be considering either invasive species removal and replanting or removal
of some of the berm system, followed by replanting. The skid area and small vertical
concrete wall will remain as part of the historical legacy of the site.
. Wildlife features will also be added to the site. There are adequate levels of large woody
debris on the site for distribution to other strategic locations. Bird boxes will be added to
the site. Both the locations of the large woody debris and the bird boxes will be shown in
the Landscaping Plan.
. Invasive species will be removed as noted throughout the site.
. Conducting the use of heavy machinery in one phase and the stabilization, hydroseeding,
and revegetation coincidentally or immediately afterward will reduce the disturbance of
the construction and occupation phases.
. Public access to the site will be enhanced through the addition of an improved trail
system along the shoreline, a designated pic:nic area at the Beach Point Picnic Area. and
interpretive signage throughout the trail system.
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. The clearing limits on this site have been approved and are currently staked. The
application will be selectively logging outsite of the clearing limits on an as-needed basis.
. Of the species expected to occur on the site, most bird, bat, and terrestrial mammal
groups will be relatively unaffected by the project. Those species dependenl upon small.
discreet habitats such as forest dwelling amphibians will be displaced by the project.
. Designation of "The Twins" islands, the riparian corridor of Ludlow Creek. and 11lL'
adjacent 5-acre parcel as conservation areas.
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By following best management practices and environmental awareness during the
construction and human occupation phases, there should be no signiticant impacts to waler
quality or quantity to the small slreams on the site or Port Ludlow Bay. Timber will be removed
from the site, as authorized by the FPA, but native understory will be left.
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We appreciate the opportunity to be of service on this project. We trust the above provides
the information you require. Please contact us if you have questions or if we can be of further
assistance.
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Respectfully submitted,
GeoEngineers, Inc.
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Lisa Berntsen, PWS
Principal
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ORCH\ 1 0\ 1062200 I \OO\Finals\ I 062200 I OOFin.llRcport.Doc
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Disclaimer: Any eleclronic furm, facsimile or hard copy of the original document (email. lcxt, table, and/or figure), if provided, and
any auachments arc only a copy of the original document. The original documCn! is slored by GeoEngim:crs. tnc. and will scrvc as
lhc official document of record,
Attachments
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REFERENCES
Brown, E. R., Editor, 1985, Management of Wildlife and Fish Habitats in Forests of Western
Oregon and Washington. Part I andU. U.S. Department of Agriculture Forest Service:
Pacific Northwest Region. Portland, Oregon,
Butler, R. W., 1992, Great Blue Heron, No. 25 in A. Poole, P. Stettenheim, and F. Gill, editors.
The Birds of North America, American Ornithologists Union and Academy of Natural
Science: Philadelphia, Pennsylvania, USA.
Cooperrider, A. Y., R. J. Boyd, and H. R. Stuart, eds. 1986, Inventory and Monitoring of Wildlife
Habitat: U.S. Department of Interior, Bureau of Land Management Service Center,
Denver, Colorado.
Cowardin, L. M., V. Carter, F. C. Golet, and E. T. LaRoe, 1979, Classification of Wetland and
Deep Water Habitats of the United States, Performed for Office of Biological Services,
Fish and Wildlife Service: U. S. Department of the Interior, Washington, D.C.
Desbonnet, A., P. Pogue, V. Lee and N. Wolff, 1994, Vegetated Buffers in the Coastal Zone - A
Summary Review and Bibliography: Coastal Resources Center, Rhode Island Sea Grant,
University of Rhode Island.
Environmental Laboratory, 1987, Corps of Engineers Wetlands Delineation Manual, Technical
Report Y-87-1: US Army Engineer Waterways Experiment Station, Viksburg.
FEMAT, 1993, Forest Ecosystem Management: An Ecological, Economic, and Social
Assessment: Forest Ecosystem Management Assessment Team.
Jefferson County Department of Community Development, 1998, Jefferson County Interim
Critical Areas Ordinance.
Leedy, D. L. and L. W. Adams, 1984, A Guide to Urban Wildlife Management: National Institute
for Urban Wildlife, Columbia, Maryland.
Point No Point Treaty Council, et aI., 1999, Hood CanaVEastern Strait of Juan de Fuca Summer
Chum Habitat Recovery Plan: Hood Canal Coordinating Council, Shelton.
Quinn, T., and R. Milner, 1999, Management Recommendations for Washington's Priority
Species, Volume IV: Birds Great Blue Heron (Ardea herodias).
Raedeke Associates, Inc., 1997, Wetland Assessment, Ludlow Cove Property, Jefferson County,
Washington, June 23, 1997.
Reid, L. M., and S. Hilton, 1998, Buffering the Buffer, in: Ziemer, Robert R., technical
coordinator, Proceedings of the Conference on Coastal Watersheds: The Caspar Creek
Story, 1998 May 6; Ukiah, California, General Tech. Rep. PSW GTR-168, Albany, CA:
Pacific Southwest Research Station, Forest Service, U. S. Department of Agriculture.
GcoEnginccrs
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age of
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U.S.D.A. Soil Conservation Service (NRCS fonnerly SCS), 1979, Jefferson County Soil Survey.
Jefferson County.
V.S.D.A., 1985, Management of Wildlife and Fish Habitats in Forests of West em Oregon and
Washington, Part 2 - Appendices: U.S. Department of Commerce - National Technical
Information Service.
US.D.A. Soil Conservation Service (NRCS fonnerly SCS), 1988, Hydric Soils of the State of
Washington.
U.S. Geological Survey, 1981, Topographic Map, Port Ludlow Quadrangle, 1:24,000.
Washington State Department ofFish and Wildlife, 1987, National Wetlands Inventory (NWI)
Map, Port Ludlow Quadrangle, 1 :24,000.
Washington State Department ofFish and Wildlife, 1992, Washington State Salmon and
Steelhead Stock lnventory-Puget Sound Stocks-Hood Canal and Strait of Juan de Fuca:
Washington Department ofFish and Wildlife, Olympia.
Washington State Department ofFish and Wildlife, 2003, Priority Habitat and Species Map, Port
Ludlow Quadrangle, produced May 23,2003, 1:24,000.
Washington Department of Natural Resources, 1999, Forest and Fish Report: Olympia,
Washington.
Washington Department of Ecology, 1994, Shoreline Management Guidebook, Second Edition:
Department of Ecology, Olympia, Washington.
Williams, R. W., et aI., 1975, A Catalog of Washington Streams and Salmon Utilization, Volume
1, Puget Sound Region: Washington Department of Fisheries. Olympia, Washington.
L()G ITEM
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Data Source: Topography trom Sure!Maps at scale of 1 :24K.
Note: The locations of all features are approximate. This map is for information
purposes. II is inlended to assist in the identification of features discussed in a
related document Data were compiled from multiple sources as listed on the
map. The data sources do not guarantee these data are accurate or complete.
There may have been updates to the data since the publication of this map.
The master file is stored by GeoEngineers, Inc, and will serve as the official
record 01 this communication.
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Data Source: Topography Irom SurelMaps at scale of 1 :24K. ~NATIONAL WETLAND INVENTORY DATA
National Weiland Inventory Data of 1974
provided by lhe Uniled Slates Fish and Wildlile
Service.
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Note: The locations of allfealures are approximate. This map is for information
purposes. II is intended 10 assist in Ihe identification 01 lea lures discussed in a
related document. Dala were compiled Irom mulliple sources as lisled on Ihe map.
The data sources do not guaranlee lhese dala are accurate or complele.
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01 Agriculture Soil Survey of Jefferson County. Washington,
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not guarantee these data are accurate or complete. There may
have been updates to the data since the publication of this map.
The master lile is stored by GeoEngineers. Inc. and
will serve as the ollicial record ollhis communication,
EvC . Everett Series.gravelly sandy loam (till)
0-15% slopes.
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Photograph A-2
Disturbed area in Wetland No.1.
LOG ITEM
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A-2
File No, 10622-001-00/060603
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Photograph A-3
Area to be revegetated within the wetland buffer.
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A-3
File No. 10622-001-00/060603
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Photograph A-4
Wetland area of no clearing or revegetation.
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A-4
File No. 10622-001-00/060603
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A-5
File No_ 10622-001-00/060603
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Photograph A.6
Wetland buffer area near the west stream to be selectively cleared of invasive
species and alders will be partially limbed and revegetated as necessary.
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A-6
File No, 10622-001-00/060603
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Photograph A-7
Previously fill areas. To be restored.
LOG lTEM
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A-7
File No. 10622-001-00/060603
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Photograph A-8
Historical cement structure along shoreline.
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A-8
File No. 10622.001-00/060603
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Photograph A.9
Skid logs along shoreline (to remain in place). Invasive species to be removed.
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A-9
Filc: No, 10622-001-00/060603
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Photograph A-10
Beach Point Picnic Area.
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File No. I 0622-0Q I-OOI06Q603
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Photograph A-11
Beach Point Picnic Area.
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A-ll
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Page. '3 6 f
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Photograph A-12
Native vegetation along shoreline in Tract A.
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LISA BERNTSEN. PWS. PRINCIPAL SCIENTIST
EDUCATION
M.S., Fisheries, University of Washington
B.S., Biology, Pacific Lutheran University
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REGISTRATION
Certified Professional Wetland Scientist
PADI Certified SCUBA Diver
SSI Advanced SCUBA Diver
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AFFILIATIONS/RECOGNITIONS
Society of Wetland Scientists, American Fisheries Society
Washington Native 1)lant Society Board Member
Northwest Association of Environmental Professionals
Association of State Wetland Managers
Washington Dept. of Fish & Wildlife GeoducklMacroalgae Diver Training
Washington Dept. of Fish & Wildlife Surf Smelt and Sand Lance Assessment Training Certified
Northwest Association of Environmental Professionals
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EXPERIENCE
Lisa is a certified Professional Wetland Scientist and has performed wetland delineations
throughout the Pacific Northwest and Alaska. She is an expert in wetland inventories and fonnal
delineation utilizing the three-parameter methodology (1987 & 1989 manuals) of hydrology, soi Is
and hydrophytic vegetation. Many projects have required Lisa's expertise in wetland mitigation,
planning, and design. She has prepared environmental mitigation designs and scientific
monitoring plans improving fish and wildlife habitat, providing for enhanced wetland function,
furthering general wetland knowledge and satisfying regulatory agency concerns. With respect to
pennitting, Lisa has performed numerous Corps of Engineers permit applications including the
detailed 404 individual wetland fill pennit for the Seattle District. Lisa has prepared and
successfully obtained a variety of Nationwide Permits under the 404 permits in the state.
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Lisa is also an expert with preparation of detailed environmental documentation such as
environmental impact statements, shoreline management plans, comprehensive management
plans and critical areas ordinances. Biological Assessments for threatened and endangered species
listed under the Endangered Species Act have been a very active part of her professional effort
sinee Puget Sound Chinook and Hood Canal Summer Chum salmon were listed under ESA. She
has completed over 20 Biological Assessments prepared for local jurisdictions for public works
projects such as roads, bridge stabilization, storm water facilities and stream culvert replacement.
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Lisa is a recognized scientific diver for eelgrass habitat and geoduck clam resource assessments.
She has performed underwater habitat surveys throughout Puget Sound diving on new outfall
sites proposed by King County, marine expansions, the Narrows Bridge Expansion and many
other sites being considered for marine development. Lisa has extensive experience on critical
area and shoreline and welland inventory projects in the Puget Sound. The following are projects
that Lisa has completed with GeoEngineers or as Principal with Applied Environmental Services.
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USA BERNTSEN, p~, PRINCIPAL SCIENTIST
PAGE 2
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Pacific County, Salmon Recovery Strategy
South Bend, Washington ,
Pacific County was awarded a h1fant through the Salmon Recovery Funding Board (SRFB) to
develop a countywide strategy to address salmon recovery. Through community involvement
and technical input from resource agencies and outside consultants, Pacific County compiled a
large amount of infonuation as the basis for salmon recovery strategy. Lisa was hired by Pacific
County to organize collected data, review community group directions and technical guidance,
and produce a comprehensive document defining and presenting Pacific County's salmon
recovery strategy. Limiting factors for each sub-watershed within WRIA 24 were summarized
and discussed in ternlS of salmon recovery project opportunities. In addition, the strategy report
provided straightforward guidance to restoration project applicants and reviewers alike.
Coal Creek Permitting & Restoration
Chehalis, Washington
Developed a restoration plan for Coal Creek in Chehalis, W A as a mitigation program for a small
wetland fill permitted to Providence Medical Center for their expansion construction. Completed
the wetland delineation, received concurrence from the US Anny Corps of Engineers and
proceeded with developing a wetland fill mitigation plan. The mitigation plan was "out of kind"
and focused on restoring habitat structure to Coal Creek that had been straightened and ditched
for about 40 years. Coal Creek still supports coho salmon and resident trout species. The
restoration involved transforming over 500 lineal feet of ditch into over 800 feet of stream
channel with large woody debris, boulders, and new spawning gravel. The project was
constructed in summer 1999 and was fully supervised by Applied Environmental Services, Inc.
The US Army Corps of Engineers and Washington Department of Ecology reviewed the project
during construction and received solid support and satisfaction with the construction effort.
Plants were installed in the stream buffer and associated wetland areas in February 2000.
Monitoring will be conducted for a period of I 0 years.
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City of Gig Harbor Public Works Department, Biological Assessments for Road
Improvement Projects, Rosedale Street Improvcments Biological Assessment
Gig Harbor, Washington
Completed a Biological Assessment for Gig Harbor to address the potential impact and
environmental effects to species listed under the Endangered Species Act (ESA) for planned
improvements to Rosedale Street This included specific information regarding the Puget Sound
Chinook salmon and other species listed since Rosedale Street lies perpendicular to puget Sound
and storm water runoff flows into marine water. Reviewed the design drawings and
environmental conditions in the project vicinity to develop the assessment. The BA was
completed within three weeks of notice to proceed. The "not likely to effect" conclusion was
recently accepted by the Washington State Department ofTmnsportation, the US Fish & Wildlife
Service and National Marine Fisheries Service.
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Mason County, Intcrim Resource Ordinance Fish & Wildlife Habitat Revision
Shelton, Washington
Provided Mason County services to revise its Resource Ordinance (RO) to integrate protection
measures for streams and wildlife species supported by the best available scientific infornlation
defined by the Growth Management Act (GMA). Our work involved active negotiations with
petitioners to the existing RD. A member of the Eastern Washington Growth Management
Hearings Board mediated these negotiations. Our focus was to determine appropriate ordinance
language and text addressing concerns and issues not complying with the GMA. After a
significant number of meetings and public involvement, produced a revised RO section
combining Fish and Wildlife Habitat Conservation Areas into one primary zone associated with
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liSA BERNTSEN, P., PRINCIPAL SCIENTIST
PAGE 3
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riparian areas. Species oflocal importance were also defined along with the process needed to
nominate and add species to the list as future concerns arise for protection. Following text
development and RO revision, we formulated a recommendation for riparian buffer widths
representing best available science. Our recommendation included both fish and wildlife species,
and the associated text provided examples of appropriately added or reduced buffers. Our recent
work focuses on public review and the Mason County adoption process. Project staff presented
testimony and input to Mason County and the State Shoreline Hearing Board in response to
comments received Ii'om the public, Skokomish Tribe, Squaxin Island Tribe, and natural resource
agencies.
Kitsap County Department of Public Works, Holly Road Widening, Wetland & Strcam
Delineation and Permitting
Seabeck, Washington
A five-mile stretch of Holly Road was planned for widening as part of the long-range road plans
in Kitsap County. Our services were retained for "on-call" professional services for 1996/97 and
was assigned the task of delineating the jurisdictional aquatic resources in the project area.
Sixteen aquatic resource areas were delineated in this effort. Streams and wetlands were
identified separately and mapped accordingly. The project report included a description of all
resource areas and a conceptual mitigation plan to compensate for impacts resulting from road
widening.
Kitsap County Department of Public Works, Biological Assessmcnts for Road Improvement
Projects, On-Call Serviccs
Kitsap County, Washington
Lisa provides "on-call" consulting services for Kitsap County Public Works Department. Since
the listing of the Puget Sound Chinook salmon, Hood Canal Summer Chum salmon and Bun
trout. We have been preparing Biological Assessments fonowing US Fish & Wildlife Service
consultation with Washington State Department of Transportation and National Marine Fisheries
Service review. Upwards of 30 projects are under way or have been completed for this client
under this on-call contract.
Washington Natural Gas Fir Tree Road Reinforcement Phase I
Thurston County, Washington
Due to the high demand for natural gas in southern Thurston County, Washington Natural Gas
contracted us to perform the necessary environmental investigations and prepare the permitting
documents to expedite the installation of a new 16 inch high pressure gas pipeline (8000 feet).
Specific tasks performed included the delineation and rating of the wetlands located within the
pipeline route. Three wetlands were delineated. One was smaller than the jurisdictional limit for
wetlands in rural Thurston County. The other two wetlands were jurisdictional and were
addressed in the project design to minimize impacts. Pipeline placement options were limited to
the existing easements associated with two existing smaller gas pipelines. Therefore, the new
pipeline had to cross-regulated wetlands. Due to the sensitive areas limitations and the
expeditious nature of the project, directional boring was selected as the construction method for
wetland areas. With our input, the project design was developed to include directional boring of
approximately 3000 lineal fect of wetland area. We prepared an expanded SEPA Checklist for
the project and submitted the permit documents to Thurston County for jurisdictional review and
approval. In addition, the Department of Ecology and US Anny Corps of Engineers were .
contacted to review the need for a federal permit or a water quality certification. All tasks were
completed within one month.
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USA BERNTSEN, P_, PRINCIPAL SCIENTIST ,.
PAGE 4
Washington Natural Gas Company, East Olympia Reinforcement Phase II
Lacey, Washington
The continuation of Phase I involved running the pipeline from the terminus of the Phase I project
to 14th Ave in the City of Lacey (approximately 4.5 miles). Route selection was an important
issue in this project. Several alternatives were considered and since we were working with
Thurston County Parks Dept. on the Chehalis Western Trail, we suggested a cooperative route
development alternative that would save WNG a significant amount of work in obtaining
numerous private easements, heavy traffic impacts during constnlction and increased
environmental concerns. The Chehalis Western Trail runs directly to Lacey and the terminus of
Phase I was at the Burlington Northern Tracks near the Trail intersection. We were contracted to
provide the environmental permitting and project coordination for the Phase II project. Wetlands
along the Trail had been assessed for the Trail and delineation was completed for the Phase II
project. The Trail crosses Chambers Lake and its outlet, Chambers Creek. Aquatic resource
impacts were limited to the trestle area where the segments of Chambers Lake connect and flow
into other wetlands. The US Army Corps of Engineers were notified and have agreed to issue
Nationwide 26 and 12 (Wetland Fill and Utility Crossing) permits. A detailed wetland mitigation
plan along with an erosion control plan, emergency response plan, and other pertinent project
related documentation were integrated into a "Project Binder" and submitted for final review and
acceptance by the lead agency (City of Lacey). The City of Olympia and Thurston County were
also included in this project and coordinated throughout. The "Project Binder" was also prepared
to assist WNG with the contractor bidding and selection process. The binders were provided to
contractors so they would be totally knowledgeable of the environmental constraints of the
. project and the actions to be taken to avoid impact and what to do if an impact occurred. This
project is complete.
Washington Natural Gas Company, Rosedale Ridge 'Vetland Delineation
Gig Harbor, Washington
Washington Natural Gas Company wished to install natural gas service toa new residential plat
in Gig Harbor. The planned route crossed a small wetland present on adjacent property, which
was influenced by runoff from the newly constructed plat. We identified the runoff problem and
worked with thc land owners and Pierce County to corrcct the uncontrolled nature of the storm
water runoff This reduced the hydrologic input the wetland to normal conditions. The wetland
was then delineated and mapped. Field assessment indicated that a horse trail has been developed
in the proposed pipeline route. This posed further problems due to animal and human safcty.
The construction plan for the pipeline was then altered to include a directional boring option to
remove potential impacts to thc horse trail userS.
Washington Natural Gas Company, Yelm Natural Gas Pipeline Reinforcement
Yelm, Washington
Services were retained by Washington Natural Gas Company to assist with the permitting of 1.5
miles of pipeline installation. The planned pipeline route crosses three wetlands and Yelm Creek.
We performed the necessary wetland and shoreline delineations and prepared detailed reports to
guide the project plan and design to minimize wetland impacts. All permit applications (SEP A,
shorelines, USACOE, etc.) was conducted through the JARP A process and coordination by
project staff. Thurston County was the lead agency for this project. In addition, wc worked
closely with WNG to determine best construction actions to minimize impacts to Yelm Creek.
The Washington Department ofFish & Wildlife was consulted to gain their input to the project
plan. This resulted in the preparation of a mitigation sequence surrounding Yelm Creek that will
result in improved instream habitat and no visible negative alteration to the character of the
stream. lC)(j 'TEIM.
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