HomeMy WebLinkAboutImpact Analysis and Restoration Plan - PLN General - 1/30/2005 IMPACTS ANALYSIS AND RESTORATION PLAN
FOR THE KUKUK PROPERTIES
LAKE LIMERICK 5 TRACT 75 AND 76
SHELTON, MASON COUNTY, WASHINGTON
Prepared for:
Mr. Jack Kukuk
2591 S. White Tail Rd.
Gold Canyon, AZ 85218
Prepared by:
AGUA TIERRA ENVIRONMENTAL CONSULTING, INC.
506 EDISON STREET SE, SUITE 100
OLYNIPIA, WA 98501
360/754-3755
JANUARY 2005
KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by: Agua Tierra Environmental Consulting,Inc.
Olympia,WA
INTRODUCTION
This study reports the results.of a Fish and Wildlife Habitat Conservation Area
(FWHCA)buffer impacts analysis and restoration plan for two properties recorded as
Lake Limerick 5 Tracts 75 and 76, Shelton, Washington. The properties are recorded at
the Assessor's Office as parcel# 32127-54-00075 and 32127-54-00076. Both properties
are owned by Mr. Jack Kukuk. The study was conducted by Christian Fromuth,
Hydrologist, and Celina Abercrombie, Restoration Specialist from Agua Tierra
Environmental Consulting, Inc. (ATEC). This report has been prepared at the request of
Mr. Kukuk.
Tree removal and site preparation has recently occurred on-site. Un-permitted vegetation
clearing has occurred within the regulated FWHCA buffer. A Stop Work Order has been
placed on both properties. Vegetation on-site has been cut but not removed from the
subject lots. The objectives of this study include the following:
(1) Report the results of an impacts analysis for the recent un-permitted activities
that have occurred on-site; and
(2) Develop a Restoration Plan to meet Mason County Critical Area Enforcement
requirements for permitting(Chapter 17.01.210).
Location
The properties are recorded as Lake Limerick 5 Tracts 75 and 76, Shelton, Mason
County, Washington. The study area is situated in a portion of Section 27, T21N, R3W
(W.M.). Vicinity, assessor, and street maps are included in Appendix A.
Site Description
The project site is an undeveloped lot in the Lake Limerick tracts. Lot dimensions for
Tract 76 are approximately 130 feet along the northern property boundary by
approximately 142 feet along western property boundary by approximately 146 feet
along southern property boundary by approximately 70 feet along eastern property
boundary(Assessor Map, Appendix A). Lot dimensions for Tract 75 are approximately
190 feet along the northern property boundary by approximately 117 feet along western
property boundary by approximately 130 feet along southern property boundary by
approximately 93 feet along eastern property boundary(Assessor Map, Appendix A).
For the purpose of this report, both tracts will be treated as a single lot.
The properties slope downward from the east to the west to an unnamed Type-5 drainage
that flows to the south.
The majority of trees on-site have been harvested. A silt fence located approximately 40
feet landward of the OHWM exists along the entire length of the western property
boundary.
Native vegetation within FWHCA buffer on-site contains an upland forested area
dominated by Douglas-fir (Pseudotsuga menziesii), Western redcedar (Thuja plicata),
evergreen huckleberry (Vaccinium ovatum),red huckleberry (Vaccinium parvifolium),
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KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by:Agua Tierra Environmental Consulting,Inc.
Olympia,WA
salal (Gaultheria shallon), kinnikinnick(Arctostaphylos uva-ursi) and bracken fern
(Pteridium aquilnum).
Soils for the study area are included in the soils mapping performed in the Soil Survey of
Mason County Area, Washington (USDA, 1960). The mapping shows the property to
include mapped soil series: Alderwood gravelly sandy loam, 5-15 percent slopes(non-
hydric). Site observations made during site investigation generally agreed with the soil
survey mapping.
The surrounding area is forested and urban residential.
Representative site photos are included for reference in Appendix B.
IMPACT ANALYSIS
Un-permitted vegetation clearing has recently occurred on-site within the regulated
FWHCA buffer. A 75 foot minimum buffer is required for the unnamed Type-5
drainage. The impacted area is identified on the Restoration Sketch map included in
Appendix A.
Vegetation Impacts
Approximately 24,000 square feet of forested native vegetation was mechanically cut and
remains on-site. Approximately 6,000 square feet of the cut vegetation lies within the
regulated FWHCA buffer. The majority of vegetation cut consists of Douglas fir
(Pseudotsuga menziesii). Understory vegetation containing Western redcedar saplings
(Thuja plicata), evergreen huckleberry (Vaccinium ovatum),red huckleberry (Vaccinium
parvifolium), salal (Gaultheria shallon), kinnikinnick(Arctostaphylos uva-ursi) and
bracken fern (Pteridium aquilnum) appears to be in a healthy condition.
RESTORATION PLAN
Goals and Performance Standards
The overall goal of this restoration plan is to restore disturbed forested area by achieving
specific goals and performance standards listed in Table 1 below. It is recommended that
a minimum of 6,000 square feet of disturbed buffer be restored through native plantings
and seeding.
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KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by:Agua Tierra Environmental Consulting, Inc.
Olympia WA
Table 1
Restoration Goals and Performance Standards
Restoration Goal Objectives Performance Standards
1. Restore 6,000 square feet of disturbed 1. Restore regulated buffer area with
forested area with native vegetation native trees, shrubs, and herbaceous
(Planting Area A). perennials at the following average
densities per 1,000 square feet:
Trees: 10 Ct b)
Shrubs: 40 ,.40/1 z--
Groundcover: 111 /-333
2. Ensure establishment of intended 2. Minimum 80% survival and growth of
densities and coverage of transplanted all transplants or natural volunteer
vegetation. substitutes for duration of monitoring
period. Substitute plants subject to
approval by Mason County Department of
Community Development.
3. Ensure establishment of 6,000 square 3. Establish low density cover crop of
feet of buffer area(Planting Area A)with native grasses in disturbed soil areas to
effective erosion control native grasses. achieve 80%soil cover by all vegetation at
the end of the first growing season and
95%cover from end of the second growing
season to end of the monitoring period.
One hundred percent compensation is not being recommended. Existing native
understory vegetation including Western redcedar saplings ('Thuja plicata), evergreen
huckleberry (Vaccinium ovatum),red huckleberry (Vaccinium parvifolium), salal
(Gaultheria shallon), kinnikinnick(Arctostaphylos uva-ursi) and bracken fern (Pteridium
aquilnum) appears to be in a healthy condition. Once removal and clearing of trees on-
site has occurred, an estimated 3,000 square feet of understory vegetation will remain
(Restoration Map, Appendix A). It is recommended that approximately 6,000 square feet
of native tree species be planted and approximately 3,000 square feet of native shrub and
groundcover species be planted.
Location of Restoration Areas
The location for proposed restoration activities is identified as Restoration Area A on the
Impacts and Restoration Plan Sketch Map in Appendix A.
Overseeding of Restoration Areas
It is recommended that Restoration Area A(approximately 6,000 square feet)be seeded
with the following native erosion control grass seed mix. This seed mix will provide
native perennial coverage to Planting Area A. Straw shall be placed on the ground after
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KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by:Agua Tierra Environmental Consulting,Inc.
Olympia,WA
seeding to prevent erosion during seed establishment(approximately 2-inch minimum
uniform cover).
Native Erosion Control Grass Seed Mix:
Perennial rye (Lolium perenne) 40% applied at approximately 2.75 lbs per 1500
square feet;
and
California poppy (Eschscholzia californica) 10%,
small-flowered Blue-eyed Mary (Collinsia parviflora) 3%,
white dutch clover (Trifolium repens) 20%,
columbine (Aquilegia formosa) 4%,
orange honeysuckle (Lonicera ciliosa) 3%,
large-leaved lupine (Lupinus polyphyllus) 10%,and
sicklekeel lupine (Lupinus albicaulis)10%applied at approximately 1 lb per 1500
square feet.
The grass seed mix should be applied by one of the following application methods:
1. An approved hydroseeder, with options of combining seeding,
tackifiers, and tracers;
2. Approved blower equipment with adjustable disseminating device
capable of maintaining a constant,measured rate of material discharge
that will ensure an even distribution of seed at the rate specified;
3. Approved power-drawn drilling equipment or seeders; and
4. An approved manual seeding method.
Seed mixture can be obtained from the following licensed regional supplier:
Inside Seed Passage,Port Townsend,WA(360)385-6114
Planting Plan
It is recommended that Restoration Area A(approximately 6,000 square feet)be planted
with native vegetation to restore the regulated buffer area.
Recommended plant densities are as follows:
Trees: 10 feet on center
Shrubs: 5 feet on center
Groundcover: 3 foot on center
The overall transplant densities have been selected to eventually provide a moderately
dense, structurally diverse plant community in the buffer area. Natural volunteer
vegetation of the species listed for planting shall be counted towards the desired densities
of restoration plants. Volunteer vegetation not listed above may substitute for the
specified plants with the approval of the reviewing Mason County staff,provided the
plants are not invasive, undesirable species such as reed canary grass, non-native
blackberries, or English ivy.
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KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by: Agua Tierra Environmental Consulting,Inc.
Olympia WA
Native plant species, densities, size and quantities that may be used within the restoration
planting areas are listed below in Table 2.
TABLE 2
Restoration Planting Area Species, Density, Size, and Quantity
(Restoration Area A=6,000 s uare feet
Planting Strata Species Density Size Qty
Area (feet on
center
A Tree Douglas fir(Pseudotsuga 10 1 gallon or 60
menziesii) bare root
A Shrub evergreen huckleberry 5 1 gallon or 60
accinium ovatum bare root
A Shrub red huckleberry(Vaccinium 5 1 gallon or 60
arvi olium) bare root
A Groundcover salal (Gaultheria shallon) 5 1 gallon 166
A Groundcover kinnikinnick(Arctostaphylos 5 4 inch 167
uva-ursi
Plant material can be obtained from one or more of the following licensed regional
nurseries:
Colvos Creek Nursery, Vashon Island, WA (206) 749-9508
Sound Native Plants, Olympia, WA (360) 352-4122
Black Lake Organic Nursery, Olympia, WA(360) 786-0537
Watershed Garden Works, Longview, WA (360)423-6456
Woodbrook Nursery, Gig Harbor, WA (253)265-6271
McComb Road Nursery, Sequim, WA (360) 681-2827
Planting Procedure
Planting pits for transplants shall be 1.5 times the depth and twice the diameter of the
transplant root balls. Remove the plant from the container and scarify the sides of the
root ball. Place approximately 1-2 gallons(depending on size of root wad) of nutrient
rich topsoil in planting hole. Place plant in the planting pit. Backfill the planting hole
with topsoil to finish grade. Water the plant well during and after planting. Example
drawings are provided in Appendix C.
Overall, plant species can be placed randomly throughout the identified revegetation area
at the densities previously discussed. It is recommended that the shrub species be planted
in clusters (example: 10 salal all in same area,each plant spaced 5 foot on center).
Silt Fence Removal
It is recommended that the silt fence be removed after site preparation and installation of
native plantings.
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KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by: Agua Tierra Environmental Consulting,Inc.
Olympia WA
Maintenance and Exotic Plant Control
Maintenance shall consist of irrigation,replacement of dead/dying or undesirable
transplants with appropriate vegetation, and removal of native noxious and invasive
weeds. No post-planting applications of fertilizer are anticipated. Deep irritation of
native plantings is recommended no less than twice monthly during May 15 —October
15a'of the first two years.
Monitoring
Under Mason County regulations (Chapter 17.01.210 2.)monitoring of the site will be
required to periodically evaluate the success of the restoration and provide amendments
to the plan, which may become necessary to achieve its purpose. Plants should be
monitored for a minimum of 80% survival and visible growth of all transplants or natural
volunteer substitutes for a period of 3 years. Any natural volunteer substitute plants are
subject to approval by Mason County Department of Community Development.
The owner shall provide for seasonal monitoring of the site by a qualified biologist or
other qualified professional, for a period of three years after completion. The applicant
shall submit an annual report to the County that meets the requirements of Chapter
17.01.210 2.
Restoration Schedule
Recommended timing and sequence of restoration and required monitoring activities are
provided below in Table 3.
TABLE 3
Schedule for Restoration
Restoration Action Proposed Timing
1. Complete site preparation Winter 2004/2005 (Dec.-Feb. -
prior to overseedin )
2. Overseeding of Restoration Area A Winter 2004/2005 (Dec.-Feb.
2. Install native plants Spring 2005 Feb —March
3. Remove silt fence Spring 2005
4. 1 year monitoring report(call Agua Tierra biologist) October 2005
5. 2 na year monitoring report call Agua Tierra biologist) October 2006
6. 3` ear monitoring report call Aguat Tierra biologist) October 2007
It is recommended that the vegetation area replanting occur during winter dormancy. Site
conditions permitting,the optimum time for planting most native woody plant material
appears to be the later part of winter and early spring(February-March). Plants installed
early in the dormant season tend to be subject to winter kill and die back. Conversely,
plants installed during the late spring and early summer have been observed to be much
less drought tolerant during the dry summer period.
Contingency Procedures
Contingency actions could include, but are not limited to, replacement of plants which
have not achieved the standard survival or coverage goals according to the proposed
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KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by: Agua Tierra Environmental Consulting,Inc.
Olympia WA
planting density; substitution of specified plant species; additional irrigation
requirements; repair of damage due to erosion or other topographical changes to the site;
and amendments to the restoration plan during monitoring as necessary to achieve its
purpose.
CONCLUSION
This study reports the results of an impacts analysis and restoration plan conducted on
two parcels recorded as Lake Limerick 5 Tract 75 and 76, Shelton,Mason County,
Washington.
Recent vegetation clearing disturbed approximately 6,000 square feet of forested
FWHCA buffer on-site. This Restoration Plan has been designed to restore these impacts
by replanting disturbed areas with native vegetation and seeding.
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KUKUK IMPACT ANALYSIS AND RESTORATION PLAN
Prepared by:Agua Tierra Environmental Consulting, Inc.
Olympia WA
REFERENCES
Reed, P.B. Jr. 1988. National List of Plant Species that Occur in Wetlands: 1988
Northwest(Region 9). U.S. Fish and Wildlife Service, Inland Freshwater Ecology
Section,Biological Report 88 (26.9), St. Petersburg, Fla.
Reed, P.B. et al. 1993. Supplement to List of Plant Species that Occur in Wetlands:
Northwest(Region 9). U.S. Fish and Wildlife Service, Inland Freshwater Ecology
Section, Supplement to Biological Report 88 (26.9), St. Petersburg, Fla.
Washington Natural Heritage Program(WNHP). 2001. Field Guide to Washington's
Rare Plants. In cooperation with Washington Department of Natural Resources
and Spokane District U.S.D.I. Bureau of Land Management. Olympia, WA.
Washington State Department of Agriculture (USDA). 1960.Mason County Washington
Soil Survey. Soil Conservation Service.
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APPENDIX A
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APPENDIX B
Representative
Photographs
LAKE LIMERICK RESTORATION
Prepared 1
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of impacted FWHCA buffer looking' northwest)
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APPENDIX C
Example Drawings
AGUA TIERRA ENVIRONMENTAL CONSULTING, INC. (ATEC)
OLYMPIA, WASHINGTON
PREVIOUS GROWING LEVEL
AT FINISH GRADE
FERTILIZER — PLACE PRIOR
TO BARK MULCH APPLICATION
"�'"'>•:?.....'. (IF REQUIRED IN PLANT MATERIALS
UST AND SPECIAL PROVISIONS)
3' WATER RETENTION BASIN. MULCH (BARK OR OTHER AS SPECIFIED
USE SURPLUS SOIL IN PLANT MATERIALS UST AND SPECIAL
PROVISIONS) — 3' DEPTH FEATHERED TO
BASE OF PLANT OR OTHER AS SPECIFIED.
FINISH GRADE
' REMOVE ALL FOREIGN WEDIA
SPREAD ROOTS EVENLY' a (BURLAP, PLASTIC, TAGS, TWINE,
OVER MOUND ETC.). REMOVE CONTAINER
POTTING SOIL MEDIA. TRIM
CREATE MOUND WITH ;.;:.,;...,` t.,;:;;:.___� EXCESSIVELY LONG ROOTS PRIOR
FIRM BACKFILL SOIL _- - TO PLANT PLACEMENT.
EXISTING SOIL I BACKFILL SOIL — THOROUGHLY
2 % (ROOT SPREAD) WATER BACKFILL SOIL
AFTER PLANTING
CONIFER TREE PLANTING DETAILS
CONTAINER B&B, AND BAREROOT NTS
PREVIOUS GROWING LEVEL
AT FINISH GRADE
FERTILIZER — PLACE PRIOR
TO BARK MULCH APPLICATION
(IF REOUIRED IN PLANT MATERIALS
UST AND SPECIAL PROVISIONS)
3' WATER RETENTION BASIN. MULCH (BARK OR OTHER AS SPECIFIED
USE SURPLUS SOIL IN PLANT MATERIALS UST AND SPECIAL
PROVISIONS) — 3- DEPTH FEATHERED TO
FINISH GRADE BASE OF PLANT OR OTHER AS SPECIFIED.
REMOVE ALL FOREIGN MEDIA
SPREAD ROOTS EVENLY (BURLAP, PLASTIC, TAGS, TWINE,
OVER MOUND ETC.). REMOVE CONTAINER
s,a POTTING SOIL MEDIA TRIM
CREATE MOUND WITH EXCESSIVELY LONG ROOTS PRIOR
FIRM BACKFILL SOIL TO PLANT PLACEMENT.
EXISTING SOIL I BACKFILL SOIL — THOROUGHLY
2 X (ROOT SPREAD) WATER BACKFILL SOIL
AFTER PLANTING
DECIDUOUS TREE DETAILS
CONTAINER B&B, AND BAREROOT NTS
506 EDISON STREET SE FIGURE:TREE PLANTING DETAIL
SUITE 100
OLYLPIA, WA 9b501
TEL (360) 754-3755
tC-C ec ro,;ectS WET L v^a^nan�drennan.gwG - r , (fU6j iLmt. icja P,
D PLACE FERTILIZER IN
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n n BACKFILL SOIL-THOROUGHLY INSTALLATION (IF SPECIFIED 0
£ WATER AFTER PLANTING IN PLANT MATERIAL UST.) C
R FINISH GRADE
FINISH D m
GRADE m
� 2SS REMOVE ALL FOREIGN MEDIA
D
i a ROOT
pTM LL e (BURLAP, PLASTIC. TAGS, TWINE. >
< w ' ETC.). REMOVE CONTAINER POTTING = m
SOIL MEDIA. TRIM EXCESSIVELY Z
ri• LONG ROOTS PRIOR TO PLANT Z
r PLACEMENT. O
Z AGCFTLL SOIL- --� M
EXISTING THOROUGHLY WATER Q O
e SOIL 2 x ROOT SPREAD --, AFTER PLANTING Z Z
� K
Fccac:; 12
GROUND COVER PLANTING DETAIL zo CONTAINER, B&B. AND BAREROOT
� NT5 D
D r� PLACE FERTILIZER IN
`° Z PLANTS SET VERTICALLY- PLANTING PIT DURING n
v NOT PERPENDICULAR TO INSTALLATION (IF SPECIFIED O
SLOPE IN PLANT MATERIAL UST.) Z
m In
O PREVIOUS CROWING ,''.• PREVIOUS GROWING LEVEL C
LEVEL AT FINISH GRADE PLACE FERTILIZER IN AT FINISH GRADE
Z PLANTING PIT DURING
INSTALLATION (IF SPECIFIED Z
FABRIC
EROSION CONTROL MEDIA (BURLAP,
ALL FOREIGN IN PLANT MATERIAL LIST.)LAP, REMOVE ALL FOREIGN O
3
(IF SPECIFIED) ' WATER RETENTION (BURLAP, PLASTIC. TAGS. TWINE,
O PLASTIC, TAGS. TWINE. ETC.), BASIN (USE SURPLUS ETC.). REMOVE CONTAINER Z
C REMOVE CONTAINER POTTING SOIL) POTTING SOIL MEDIA TRIM (�
m SOIL MEDIA. TRIM EXCESSIVELY EXCESSIVELY LONG ROOTS PRIOR
PROPOSED LONG ROOTS PRIOR TO PLANT PLACEMENT.
SLOPE LINE TO PLANT PLACEMENT. D
m COURSE ORGANIC MULCH FINISH GRADE / / m>
D 5' DEPTH FEATHERED �
TO SHRUB STEM f
r \ n,.:.•:.•.. SPREAD ROOTS EVENLY OVER ROOT BALL COURSE ORGANIC MULCH
OUNDED BACKFILL SOIL. DEPTH .s•�• 3' DEPTH
ROOT BALL !• ° t': i�`�t FINISH _t° FEATHERED TO
DEPTH 1 v- +' GRADE `'` i` 44 SHRUB STEM
FILL SOIL \ \\ / \ 13AOCFILL SOIL-
EXISTING THOROUGHLY WATER
TWO TIMES AS WIDE SOIL 2 x ROOT SPREAD --� AFTER PLANTING
AS ROOT BALL
SHRUB OR TREE PLACEMENT ON SLOPE SHRUB PLANTING DETAIL
CONTAINER, B&B. AND BAREROOT NTS CONTAINER, B&B. AND BAREROOT NTS