HomeMy WebLinkAboutHMP Habitat Managment Plan - 8/31/2021 Habitat Management Plan
Parcel# 12216-75-90031
XXX State Route 302
Belfair, WA 98528
Mason County
Report prepared for:
Philip Zamagne
1212 NW Tahoe Ln APT 201
Silverdale, WA 98383
Prepared by:
Rob Nagel
680 E Philura Ln
Shelton, WA 98584
arctosaerial@gmail.com
(425) 344-9315
(360) 229-3118
A RCTOS
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Environmental Consultation I Drone Imagery
Project: 2021-H M P-002
August 2021
Project: 2021-HMP-002 August 2021 ARMS
Table of Contents
Overview................................................................................................................1
PropertyDescription ..............................................................................................2
Analysis of Potential Impacts.................................................................................3
MitigationMeasures..............................................................................................5
Monitoring .............................................................................................................9
Summary................................................................................................................9
References............................................................................................................12
List of Figures
Figure1: Vicinity Map ............................................................................................2
Figure 2: Map depicting stream buffer on project site ..........................................3
Figure3: Site Plan.................................................................................................10
Figure 4: Site Plan with drone imagery................................................................11
Project: 2021-HMP-002 August 2021 A RCTOSAERIAL
Habitat Management Plan
12216-75-90031
XXX State Route 302
Belfair, WA 98528
Overview
This report details a Habitat Management Plan (HMP) for the above referenced
property in Mason County, Washington. The purpose of this report is to address
potential adverse impacts from the construction of a driveway serving two
proposed Single-Family Residence (SFR) within the buffer of a non-Fish bearing,
seasonal (Ns) stream, which is a tributary to Case Inlet. The Mason County
Resource Ordinance requires a 75-foot buffer with an additional 15ft building
setback for Type Ns streams. (see figure 1). The SFR is proposed on the opposite
side of the subject parcel as the existing access road, with a driveway crossing the
stream and stream buffer, with ±600ft2 within the stream buffer on the subject
lot. The proposed driveway route is currently dominated primarily by invasive
species, mostly Himalayan blackberry, with a few native tree species mixed in.
Mitigation measures have been designed to offset the potential impacts of this
activity on the ecological functions of the stream buffer. The mitigation ratio
proposed is 1:1 for Re-establishment of a portion of the vegetated stream buffer.
The objectives of this report are as follows:
• Identify potential impacts of the construction of the proposed driveway
within the stream buffer on the buffer's ecological functions and fish and
wildlife habitat.
• Determine mitigation measures that would offset those impacts and result
in a net benefit to ecological functions and fish and wildlife habitat within
the remaining buffer.
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Project: 2021-HMP-002 August 2021 AERIAL
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Figure 1:Vicinity map of project.
Property Description
The parcel is 1.32 acres in size and located in the SW% of the SE% of section 16,
Township 22 North, Range 1 West. The Type-Ns stream runs through the west
half of the parcel from the south to the north. The proposed driveway
development route is currently characterized primarily by invasive Himalayan
blackberry and scotch broom with a few native red alders along the stream
channel. The existing access road to the property runs along the western parcel
boundary. An approved septic design locates the system on the opposite side of
the creek as the access road.
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Figure 2:Map showing the seasonal stream and the regulated buffer. The solid yellow lines are the 75ft buffer for the stream.
The dashed yellow lines are the 15ft building setback.The red polygon is the parcel in question.
Analysis of Potential Impacts
Vegetated buffers serve an important role in protecting critical public resources,
as well as fish and wildlife habitat from adverse impacts associated with
development. Below are the potential adverse impacts to ecological function
associated with the construction of this proposed SFR within the Type-Ns stream
buffer.
- Increased storm-water runoff and erosion
Impervious surfaces such driveways contribute to increased flow of runoff
during storm events. This increased flow could contribute to erosion and
increased sediment reaching the stream waters without a proper storm
water management plan.
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Project: 2021-HMP-002 August 2021 ARCTOSAERIAI.
- Stream bank stabilization
Removing of buffer vegetation and increasing storm water run-off can
speed erosion of stream banks and make them unstable. No risk of erosion
is expected with this project due to mild slopes and construction BMPs
listed in the mitigation measures.
- Loss of wildlife habitat
The development footprint of this driveway within the buffer is only ±600ft2
and little native vegetation will be removed in the construction process
since the project site is currently dominated by invasive species. Mitigation
measures will in fact increase the amount of wildlife habitat and have a net
ecological benefit to the stream buffer by removing invasive species, re-
establishing native species, and increasing species richness and structural
diversity of the stream buffer.
- Increased disturbance from noise pollution
A temporary increase in noise from construction activities is likely to occur.
but activities will be limited to daylight hours, and the project is located in a
residential area where human noises are a common occurrence. Also, no
known nesting sites or priority habitats and species have been identified
near the project site.
- Increased Solar input
The proposed driveway requires a few native trees to be removed in the
process of construction. Native plantings within the mitigation area will
offset the impact and benefit the stream by eventually increasing shade
and reducing solar input as the mitigation area matures.
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Project: 2021-H M P-002 August 2021 AERIAL
Mitigation Measures
To avoid, minimize, and mitigate for the potential adverse impacts identified
above, the following have been identified as appropriate measures for this
project:
- Minimizing/avoiding impact
The proposed project minimizes the impact to the stream buffer by
taking a direct route across the stream buffer in an area currently
dominated by invasive species.
- Mitigation area
An area along the stream totaling ±600ft2 will be restored to vegetated
buffer per the planting guidelines below. The mitigation area is currently
dominated by invasive species. This area will be identified as a Habitat
Preservation Area (HPA). Access to this area will be restricted, and it will
be marked with signs identifying it as such. The minimum number of
trees, shrubs, and ferns/groundcovers to be planted in order to meet
the required densities are as follows:
-Trees = 6
-Shrubs = 24
-Ferns/groundcovers = 38
- Best Management Practices for construction
Construction activities related to this project will be restricted to
favorable weather conditions and best management practices for
reducing disturbance and erosion will be followed, including placing
straw over exposed areas, and erecting silt fencing below the project
area. Equipment will be checked daily for leaks and all fuel, lubricant,
and chemicals will be stored outside the stream buffer.
- Clustering of development
All activities related to this project will be clustered to the extent
possible without impacting more of the stream buffer than necessary.
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Project: 2021-HMP-002 August 2021 ARCtOSAtR'AL
Equipment and materials will be parked/stored outside the stream
buffer.
- Removal of invasive species
All occurrences of invasive species in the vicinity of the project site and
mitigation area will be mechanically removed without the use of
herbicides.
- Landscaping with native plant species
Any landscaping within the developed area of the stream buffer will be
limited to native plant species typically found in undisturbed riparian
areas. Species selected will include common riparian vegetation not
currently on the property which will result in a net increase in species
richness and biodiversity within the buffer.
Planting Guidelines for the Mitigation Area (adapted from Appendix C
of the Mason County Resource Ordinance)
Earthwork
Machinery earthwork will be restricted to the minimum necessary in order to
implement this plan; planting holes for specified vegetation installation will be
hand dug.
Native Plantings
Native plantings will be installed within the mitigation area parallel to the edge of
the buffer to achieve the following minimum densities:
Trees— 10' on center
Shrubs— 5' on center
Ferns, grasses, and ground-covers —4' on center
The plan calls for installing single trees, or clusters of three shrubs, on 10ft centers
and single shrubs on 5ft centers. Areas between will be filled in with ferns,
grasses, or ground-covers on 4ft centers. Exact placement of installed materials
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Project: 2021-HMP-002 August 2021 AERIAL
will be up to the landscape installer, following the basic 10-foot spacing pattern
described above and using the planting map as a guide. Successful
implementation of the planting plan will achieve a structurally and biologically
diverse plant community that mimics undisturbed riparian stream buffers.
Volunteer native vegetation can be counted towards the target densities of
restoration area at the time of monitoring audits.
Native plant species appropriate for this area include, but are not limited to the
following:
Trees:
Pacific madrone (Arbutus menziesii)
Western red cedar (Thuja plicata)
Douglas fir (Pseudotsuga menziesii)
Garry oak (Quercus garryana)
Western hemlock (Tsuga heterophylla)
Grand fir (Abies grandis)
Cascara (Rhamnus purshiana)
Cottonwood (Populus balsamifera)
Shore pine (Pinus contorta v. contorta)
Pacific crabapple (Malus fusca)
Serviceberry (Almenlanchier alnifolia)
Shrubs:
Ocean spray (Holodiscus discolor)
Wax myrtle (Myrica californica)
Thimbleberry (Rubus parviflorus)
Hookers willow (Salix h000keriana)
Tall Oregon grape (Mahonia aquifolium)
Nootka rose (Rosa nutkana)
Salmonberry (Rubus spectabilis)
Salal (Gaultheria shallon)
Evergreen huckleberry (Vaccinium ovatum)
Snowberry (Symphorocarpus albus)
Elderberry (Sambucus racemosa)
Red osier dogwood (Cornus stolonifera)
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Ferns, grasses, and ground-covers:
Sword fern (Polystichum munitum)
Bracken fern (Pteridium aquilinum)
Tufted hairgrass (Deschampsia cespitosa)
Coastal strawberry (Fragaria chiloensis)
Seashore saltgrass (Distichlis spicata)
Coastal lupine (Lupinus littoralis)
Silverweed (Potentilla pacifica)
Twinberry (Lonicera involucrate)
Henderson's checker-mallow (Sidalcea herdersonii)
All planting should occur during winter dormancy. The optimum time for planting
is from February to March.
Installation
Installation of the prescribed vegetation will be performed by qualified
landscapers familiar with planting of native vegetation in natural settings.
Installation will be performed only after construction on the property is
completed to avoid damage to the plantings.
Fertilizing
Artificial fertilizer may be applied to each planting hole in the form of "slow-
release" tablets or some other similar material. However, general broadcast
fertilization MAY Not be used within the landscape planting area.
Maintenance
Maintenance of the installations will be the responsibility of the landscape
installer. Maintenance is to include any weeding or watering necessary to ensure
plant survival for up to three years after the date of installation.
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Monitoring
Following the implementation of the mitigation measures, an annual report will
be submitted to the county for 3 years post construction. The report will detail
the presence of new, or the reoccurrence of any invasive species. Invasive species
found on site will again be removed mechanically, using hand tools only to reduce
disturbance to the stream buffer and mitigation area plantings. The annual report
will also document the planting success of native plantings. If plant survival in the
mitigation area falls below 90% at any time in the 3-year monitoring period, the
mitigation area will be selectively re-planted to achieve target densities.
If any failures of mitigation measures are identified during the annual inspection,
corrective actions will be recommended in the report and will be taken to restore
them to working order as soon as possible.
Summary
This report Identifies potential impacts of the construction of a proposed
driveway, ±600ft2, within the regulated buffer of a Type-Ns stream. The proposed
route is currently dominated by invasive species and provides little benefit to the
stream and its buffer. Mitigation measures have been proposed to avoid,
minimize, and mitigate for those impacts on the stream buffer's ecological
functions and fish and wildlife habitat. Successful implementation of the
proposed mitigation measures will result in a net benefit to the stream and its
buffer's ecological functions, structural diversity, and species richness. Mitigation
measures include re-establishing approximately 600ft' of vegetated stream buffer
currently covered with invasive species, for a mitigation ratio of 1:1.
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Project:2021-HMP-002 August2021 X ARCTOS AERIAL
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Structure Setback _75'Type Environmental Consulting(Drone Imagery
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PO Box 2466
' Shelton,WA 98584
60 Type-Ns Stream (425}344-9315
Mitigation Areas arctosaerial@gmail.com
(600ft2 total) www.arctosaerial.com
62' Proposed SFR
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Project:2021-HMP-002 August 2021 A RCTOS
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Project: 2021-HMP-002 August 2021 ARMSAERIAL
References
Environmental Laboratory. (1987). "Corps of Engineers Wetlands Delineation Manual,"Technical Report
Y-87-1, U.S. Army Engineer Waterways Experiment Station,Vicksburg, Miss.
Guard,J. (1995). Wetland Plants of Oregon &Washington. Lone Pine Publishing. 240 pp. Edmonton,
Alberta, Canada.
Hruby,T. (2014). Washington State Wetland Rating System for Western Washington: 2014 Update.
(Publication #14-06-029). Olympia,WA: Washington Department of Ecology.
Munsell Color(Firm). (2009). Munsell soil color charts :with genuine Munsell color chips. Grand Rapids,
MI
Pojar,J. and A. MacKinnon. 1994. Plants of the Pacific Northwest Coast (Revised Edition 2014). Lone Pine
Publishing. 528 pp.Vancouver, British Columbia,Canada.
United States Department of Agriculture, Natural Resources Conservation Service. 2010. Field Indicators
of Hydric Soils in the United States,Version 7.0. L.M.Vasilas, G.W. Hurt, and C.V. Noble (eds.).
USDA, NRCS, in cooperation with the National Technical Committee for Hydric Soils.
U.S.Army Corps of Engineers 2018. National Wetland Plant List,version 3.4, http://wetland-
plants.usace.army.mil/U.S.Army Corps of Engineers, Engineer Research and Development
Center Cold Regions Research and Engineering Laboratory, Hanover, NH
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.
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