HomeMy WebLinkAboutHMP - HMP Habitat Managment Plan - 11/10/2020 ?LANNING
Habitat Management Plan
Parcel# 32232-50-94008
300 E Dalby Rd RECEIV
Union, WA 98592 ED
Mason County Nov 102020
615 VV. Alder
Street
Report prepared for:
Rick Buechel - President
Hood Canal Communications
PO Box 249
Union, WA 98592
Prepared by:
Rob Nagel
680 E Philura Ln
Shelton, WA 98584
arctosaerial@gmail.com
(425) 344-9315
(360) 229-3118
ARCTOS
... AIRIA1
Environmental Consultation I Drone Imagery
Project: 2020-H M P-204
October 2020
Project: 2020-H M P-204 October 2020 ARMS
A t R I A S
Table of Contents
Overview................................................................................................................1
PropertyDescription..............................................................................................2
Analysis of Potential Impacts.................................................................................3
Mitigation Measures..............................................................................................5
Monitoring .............................................................................................................8
Summary................................................................................................................9
References............................................................................................................12
List of Figures
Figure1: Vicinity Map ............................................................................................2
Figure 2: Map depicting stream/wetland buffers..................................................3
Figure3: Site Plan.................................................................................................10
Figure 4: Site Plan with drone imagery................................................................11
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Project: 2020-H M P-204 October 2020 A E R I A L
Habitat Management Plan
32232-50-94008
300 E Da I by Rd
Union, WA 98592
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 proposed warehouse
expansion within the buffer of Big Bend Creek, a Fish-bearing, Type-F stream, and
a tributary to the Hood Canal. The Mason County Resource Ordinance requires a
150-foot buffer with an additional 15-foot building setback for fish-bearing
streams. A category III wetland is also nearby, but the proposed expansion would
be outside the buffer and setback. (see figure 1). The warehouse expansion is
proposed 109-feet from the ordinary high-water mark (OHWM) of the stream at
its closest point, with ±1,400ft2 within the stream buffer. The proposed site is
currently maintained as a gravel lot and is devoid of vegetation. 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 warehouse
expansion 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
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in a net benefit to ecological functions and fish and wildlife habitat within
the remaining buffer.
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Figure 1:Vicinity map of project.
Property Description
The parcel is current) 1.43 acres in size and located in the SW/ of the SW/ of
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section 33, Township 22 North, Range 3 West. The main office and an existing
warehouse of Hood Canal Communications are located on the above-named
parcel. The Type-F stream flows adjacent to the parcel to the north. Existing
primary and secondary storm-water retention structures are located to the east.
The site is characterized by both young and mature western red cedar (Thuja
plicata), Douglas-fir (Pseudotsuga menziesii), big-leaf maple (Acer macrophyllum),
sword fern (Polystichum munitum), and salal (Goultheria shallon). Invasive species
that occur on the site include Himalayan blackberry.
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Project: 2020-HMP-204 October 2020 ARMS
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Figure 2:Map showing Big Bend Creek,the Category 111 wetland associated with a tributary to Big Bend Creek,and the regulated
buffers of both.The yellow polygon is the 150ft buffer for the wetland.The green polygon is the 150ft buffer for the stream.The
red polygon is the parcel in question with a proposed Boundary Line Adjustment.
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 warehouse addition within the
Type-F stream buffer.
Increased storm-water runoff and erosion
Impervious surfaces such as roofs and 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. Run-off will be directed to an
existing storm-water retention structure to trap sediment and slow down
run-off waters.
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Project: 2020-HMP-204 October 2020 AERIAL
- Stream bank stabilization
Removing of buffer vegetation and increasing storm water run-off can
speed erosion of stream banks and make them unstable. This project site is
located on an existing gravel lot already controlled for storm water. No
vegetation removal is proposed and no risk of erosion is expected.
- Loss of wildlife habitat
The development footprint of this warehouse addition within the buffer is
only ±1,400ft2 and no vegetation will be removed in the construction
process since the project site is already a gravel lot. Mitigation measures
will actually increase the amount of wildlife habitat and have a net
ecological benefit to 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 on
a commercial site 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 warehouse expansion is sited on the south side of the stream
on an existing gravel lot and no vegetation will be removed in the process
of construction. Native plantings within the mitigation area will benefit the
stream by eventually increasing shade and reducing solar input.
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Project: 2020-HM P-204 October 2020 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
minimizing the square footage of the proposed structure within the
buffer to approximately ±1,400ft2. The warehouse expansion will be
constructed in an area already devoid of vegetation.
- Mitigation area
An area in the northwest corner of the parcel totaling ±1,400ft2 will be
restored to vegetated buffer per the planting guidelines below. The
mitigation area is currently maintained as a gravel lot/parking area. This
area will be identified as a Habitat Preservation Area (HPA). Access to
this area will be restricted to a single 3-foot wide trail, and it will be
marked with signs identifying it as such.
- 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.
Equipment and materials will be parked/stored outside the stream
buffer.
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Project: 2020-HMP-204 October 2020 AERIAL
- Removal of invasive species
All occurrences of invasive species in the vicinity of the project site and
mitigation area will be mechanically removed using hand tools only.
- Landscaping with native plant species
Any landscaping within the developed area 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.
- Directing storm-water runoff to existing storm-water retention structure
Warehouse downspouts will direct runoff into an existing storm-water
retention structure located adjacent to the proposed project. Silt
fencing and strawbales will be used to insure no sediment enters the
stream or wetland.
Planting Guidelines (per Appendix C of the Mason County Resource
Ordinance)
Earthwork
Machinery earthwork will be restricted to removing existing gravel in order to
implement this restoration plan; planting holes for specified vegetation
installation will be hand dug. No additional clearing or grading should be required
for site restoration.
Native Plantings
It is recommended that native plantings be installed within 10 foot wide
restoration zones in linear strips extending across the site parallel to the edge of
the buffer to achieve the following densities:
Trees— 10' on center
Shrubs — 5' on center
Ferns— 4' on center
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The general plan calls for installing single trees, or clusters of three shrubs, on
approximate 10-foot centers. Each row will alternate between 5 trees + 3 shrub
clusters or 4 trees + 4 shrub clusters starting from the edge closest to the
identified critical area proceeding to the edge of the buffer. Specifically for stream
ravine replanting, cedar will be the first type of tree installed within the first row
at the top of the ravine, and then incrementally changing one cedar tree to a fir
through the first six rows, with all fir trees thereafter or to the edge of the buffer
whichever comes first. Exact placement of installed materials will be up to the
landscape installer, following the basic 10-foot spacing pattern prescribed. Finally,
a native ground cover planting or sword fern will be randomly installed
throughout the planting row on average four-foot centers. These densities have
been selected to provide a moderately dense, structurally diverse plant
community within the restoration area. Volunteer native vegetation can be
counted towards the target densities of restoration plants.
Typical native plant species that may be used with the restoration zone include:
Trees: Western red cedar (Thuja plicato) — 2 or 3 gallon
Douglas fir (Pseudotsuga menziesii) — 2 or 3 gallon
Western hemlock (Tsuga heterophylla) - 2 or 3 gallon
Grand fir (Abies grandis) — 2 or 3 gallon
Cascara (Rhamnus purshiana) — 2 or 3 gallon
Cottonwood (Populus balsamifera) — 2 or 3 gallon
Shrubs: nootka rose (Rosa nutkona) — 1 gallon
salmonberry (Rubus spectabilis) — 1 gallon
salal (Gaultheria shallon) — 1 gallon
evergreen huckleberry (Vaccinium ovatum) — 1 gallon
twinberry (Lonicera involucrate) — 1 gallon
snowberry (Symphorocarpus albus) — 1 gallon
elderberry (Sambucus racemosa) — 1 gallon
red osier dogwood (Cornus stolonifera) — 1 gallon
Ferns: sword fern (Polystichum munitum) — 1 gallon
All planting should occur during winter dormancy. The optimum time for planting
is from February to March.
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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 home construction on the property is
completed to avoid damage to the plantings from construction activities. All
installed vegetation shall be marked with colored flagging to facilitate monitoring
inspections. A separate "as-built" plan will be provided by the landscaper if the
planting pattern or schedule deviates from that listed within this document.
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 and weeding or watering necessary to ensure
plant survival for up to three years after the date of installation.
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. The annual report will also document the
planting success of any native species and the success of the retention structure
at controlling storm-water runoff.
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.
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Project: 2020-HMP-204 October 2020 AERIAL
Summary
This report Identifies potential impacts of the construction of a proposed
warehouse expansion, ±1,400ft', within the regulated buffer of a Type-F, fish-
bearing stream. The proposed building site, 109 feet from the stream edge at its
closest point, is currently devoid of vegetation 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 1,400ft2 of vegetated stream
buffer currently maintained as a gravel lot/parking area, for a mitigation ratio of
1:1.
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Environmental Consulting(Drone Imagery
PO Box 2466
Shelton,WA 98584
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www.arctosaerial.com
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Project: 2020-H M P-204 October 2020 ARMS
AERIAL
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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