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Wetland Mitigation Concepts Report, Houser Way Relocation Project- DRAFT
WETLAND MITIGATION CONCEPTS REPORT
HOUSER WAY RELOCATION PROJECT
RENTON, WASHINGTON
prepared for:
The City of Renton
Public Works Department
Renton, Washington
prepared by:
Adolfson Associates, Inc.
5309 Shilshole Avenue NW
Seattle, Washington
April 1994
Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT •
TABLE OF CONTENTS
TABLE OF CONTENTS ......................................................................
i
EXECUTIVESUMMARY .................................................................. .
INTRODUCTION ..............................................................................
1
PROJECTDESCRIPTION ....................................................................1
SENSITIVEAREAS ...........................................................................3
Wetland Functions and Values .......................................................
Wetland Classification .................................................................
Wildlife/Habitat.........................................................................6
REGULATORY REQUIREMENTS .........................................................6
FederalRegulations ....................................................................6
StateRegulations .......................................................................7
LocalRegulations ......................................................................7
IMPACTS ........................................................................................9
MITIGATION CONCEPTS ...................................................................9
Mitigation Requirements ..............................................................9
Goals and Objectives...................................................................9
Conceptual Site Plan ...................................................................11
Clearing and Erosion Control.........................................................11
PlantPalette.............................................................................12
MAINTENANCE...............................................................................12
MONITORING AND REPORTING.........................................................13
SUCCESS CRITERIA..........................................................................13
CONTINGENCY PLAN.......................................................................14
FINAL MITIGATION PLAN.................................................................14
REFERENCES ..................................................................................15
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
EXECUTIVE SUMMARY
At the request of ENTRANCO, consultants to the City of Renton (City), ADOLFSON
ASSOCIATES, INC. (AAI) prepared a Wetland Mitigation Concepts report for the
Houser Way site, located in Renton, Washington. The report addresses mitigation
goals, maintenance and monitoring of the mitigation elements, success criteria, and a
contingency plan.
The project site is located at the toe of the steeply sloping, wooded western
embankment of Interstate 405 (I-405). It extends from North 8th Street south to Sunset
Boulevard and lies between the toe of the I-405 embankment and the Burlington
Northern Railroad (BNR) line.
Within the project area, a vegetated drainage channel and adjacent wetland is located at
the bottom of the steep slope of the western embankment of I-405. The wetland is a
mixed palustrine forested/scrub-shrub/emergent wetland characterized by a forest
canopy layer dominated by red alder, black cottonwood, and western red cedar. The
scrub-shrub and ground cover strata are dominated by red alder saplings, salmonberry,
spiraea, and common horsetail. Upland vegetation in the general area consists of
Douglas-fir, silver fir, and western hemlock. Scrub-shrub and ground cover strata
include blackberry, sword fern, and Scot's broom.
Impacts to the wetland will be primarily due to construction activities. These will
include: roadway excavation, development of embankments and drainage systems,
paving, construction of a wetpond for surface water management, and development of a
wetland mitigation area. The open drainage channel will be filled, and the wetland
adjacent to the drainage channel will be excavated during construction activities. The
wetland soils within the drainage channel will be stockpiled for use in the mitigation
wetland, as applicable.
The goal of the mitigation plan will be to maintain or improve the functions and values
which are presently provided by the wetland in this area, primarily storm water control
and wildlife habitat.
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT "
INTRODUCTION
At the request of ENTRANCO, consultants to the City of Renton (City), ADOLFSON
ASSOCIATES, INC. (AAI) has prepared this technical report for the Houser Way site,
located in Renton, Washington. The report is being completed as part of the Houser
Way Relocation Project: the proposed construction of an extension of Houser Way
from North 8th Street south to a connection with Sunset Boulevard. The boundaries of
the study area were established on an aerial photograph supplied by Entranco and
located in the field according to the aerial photograph.
The first phase of the Scope of Work for this project included a wetlands
determination, delineation, rating, a qualitative functional value assessment, and a brief
discussion of regulatory implications and permitting considerations. These elements
have been summarized in the report Houser Way Wetlands Study (Adolfson Associates,
Inc. 1993). Phase two of the Scope of Work includes an analysis of potential wetlands
impacts and the development of a mitigation plan. These elements are presented in this
report.
PROJECT DESCRIPTION
The Houser Way Relocation Project site is located at the toe of the steeply sloping,
wooded western embankment of Interstate 405 (I-405) in the City of Renton, in King
County, Washington (Section 8, Township 23 North, Range 5 East). It extends from
North 8th Street south to Sunset Boulevard and lies between the toe of the I-405
embankment and the Burlington Northern Railroad (BNR) line (Figure 1).
The project is designed to alleviate the traffic congestion on North Renton
neighborhood streets and arterials, mainly on North 3rd Street, North 4th Street, and
Park Avenue North. The new roadway will provide a more convenient access for
Boeing and PACCAR employees to neighboring highways such as I-405, SR 900, SR
169, and SR 167.
The new Houser Way will be a frontage road to I-405 lying between and paralleling I-
405 and the Burlington Northern Railroad (BNR) railroad tracks. The roadway will
extend from North 8th Street south to Sunset Boulevard just north of North 3rd Street.
At its southern end, the new roadway will connect to Sunset Boulevard through an
interchange and will require an undercrossing structure under the I-405 southbound off-
ramp and Sunset Boulevard. At its northern end, the roadway will connect to the
existing Houser Way and North 8th Street through a tee intersection.
The total length of the project is approximately 2,600 feet. The roadway will be a two-
way, two-lane street with a 14-foot-wide lane in each direction. A six-foot sidewalk on
the west side will diverge from the roadway just before the undercrossing. The
sidewalk will then become grade-separated and run along the west side of the
undercrossing and Sunset Boulevard, finally merging with the existing sidewalk on
04/13/94 1
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT,
Sunset Boulevard north of North 3rd Street. A three-foot curb on the east side of the
roadway will begin just south of North 8th Street and terminate just north of the
undercrossing.
The steepness of the I-405 embankment and the drainage conditions in the project area
will require construction of a retaining wall just south of North 8th Street. Work will
include: paving, curbs, gutters, sidewalks, structural walls, an undercrossing structure,
storm drainage, water quality treatment, channelization, signalization, and
environmental assessment. This report summarizes the conceptual approach to the
compensatory wetland mitigation which will be required for this project.
SENSITIVE AREAS
Within the project area, a vegetated drainage channel is located at the bottom of the
steep slope of the western embankment of I-405. The channel conveys surface and
storm water flows north approximately 1,600 feet north along the toe of the
embankment to a 42-inch concrete storm drain along North 8th Street. The flows then
travel 900 feet west in this system to a 72-inch concrete storm drain along Garden
Avenue North to Park Avenue North. At the south side of Park Avenue North, the
flows join other storm flows and are conveyed through Gene Coulon Park in a low
gradient, open channel locally known as Johns Creek. The flows then discharge to
Lake Washington.
One wetland, comprising 0.98 acres, was identified on the project site within and
adjacent to the drainage channel (Figure 2). The wetland is a mixed palustrine
forested/scrub-shrub/emergent wetland characterized by a forest canopy layer
dominated by red alder, black cottonwood, and western red cedar. The scrub-shrub
and ground cover strata are dominated by red alder saplings, salmonberry, spiraea, and
common horsetail. Upland vegetation in the general area consists of Douglas-fir, silver
fir, and western hemlock. Scrub-shrub and ground cover strata include blackberry,
sword fern, and Scot's broom.
Wetland Functions and Values
The wetland was evaluated according to the methodology developed by the Army
Corps of Engineers (Corps) (Reppert et al., 1979). It was given a MODERATE rating
for water quality improvement, as the hydrophytic vegetation within and adjacent to the
channel provides runoff retention and water purification functions. The wetland
received a LOW-to-MODERATE rating for storm and flood water control and
hydrologic support due to its small size and the low degree of woody cover. Although
the wetland rated LOW for biological support due to its small size and lack of unique
species, its moderate plant diversity and ability to support water dependent species,
such as waterfowl, earned it a MODERATE rating. These ratings are provided in
Table 1.
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WETLANO A
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ADOLFSON
ASSOCIATES, INC.
Table 1. Functional Value Assessment for Hauser Way - Wetland A
CRITERIA
FUNCTIONAL
VALUES Low Rating Moderate Rating High Ratio
Water Quality 1) intermittently 1) associated with 1) associated with
Improvement flooded wetland lake estuary or perennial
2) < 50% 2) 50-80% stream or river
herbaceous cover herbaceous cover 2) > 80%
3) size < 10 acres 3) size 10-100 acres herbaceous cover
4) no proximity to 4)downstream from 3) size > 100 acres
pollutants/ not nonpoint pollutants 4) downstream from
downstream from 5) retains 25-50% municipal point
industrial point overland runoff discharges
discharges 5) retains > 50%
5) retains < 25% overland runoff
overland runoff
Storm and Flood 1) size < 5 acres 1) size 5-10 acres 1) size > 10 acres
Water Control 2) directly upstream 2) directly upstream 2) directly upstream
from remote areas from rural areas from urban &
3) < 10% woody 3) 10-30% woody developable areas
cover cover 3) > 30% woody
4) isolated/ no cover
cumulative effects
Hydrologic 1) size < 5 acres 1) size 5-10 acres 1) size > 10 acres
Support 2) hydrologically 2) seasonally 2) permanent
(Streamflow isolated flooded/ associated inundation/
Maintenance) 3) temporarily with riverine or associated with
saturated or lacustrine systems estuary
inundated; low 3) moderate flooding 3) high flooding
flooding frequency frequency frequency
4) located adjacent to 4) located adjacent to
an adjacent wetland open water
Biological Support 1) vegetation lacking 1) shrub/forested 1) marsh
[except mudflats] swamp 2) intertidal marsh/
2) isolated systems/ 2) upper tidal marsh/ associated with
wetland associated associated with permanent stream or
with ephemeral intermittent streams river
streams 3) two habitat types 3) three or more
3) one habitat type 4) moderate plant habitat types
4) low plant diversity diversity 4) high plant
5) no or few habitat 5) several habitat diversity
features features 5) many habitat
6) no unique species 6) unique species features
7) no water- potential 6) unique species
dependent species 7) water-dependent present
8) small size species potential 7) water-dependent
8) medium size species present
8) large size
Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
Following implementation of the wetland mitigation concepts discussed in this report, it
is anticipated that there will be a small net increase of wetland functions and values in
the project area.
Wetland Classification
The City of Renton classifies wetlands in its Wetlands Management Ordinance (No.
4346) based upon area, the presence of salmonids, the number of vegetation classes,
the presence of permanent open water, and the presence of endangered or threatened
species and/or habitat(s).
The wetland does not contain permanent open water and is subject to continued
disturbance for maintenance as a drainage channel. According to the Ordinance, the
wetland merits a Category 3 - Lower Quality Wetland rating due to the degree of
disturbance it receives, its low-to-moderate wetland functions ratings, and its low usage
by wildlife.
Wildlife/Habitat
A female mallard was the only wildlife identified within the project area during field
observations. A few unidentified songbirds were heard and seen, and coyote sign was
observed near the streambed. No other wildlife presence was detected. A small
forested component at the toe of the slope from I-405 adjacent to the wetland provides
some habitat for wildlife; however, its habitat function is not intrinsic to the wetland.
This area is the same forested community found along the toe of the I-405 embankment
where no wetlands exist. This area is not expected to receive much use by wildlife
due to its position between a major highway on one side and railroad tracks and an
industrial area on the other.
No endangered, threatened, or sensitive species of plant or animal were observed at the
site during the field observations. This observation has been subsequently confirmed
by a search of the Priority Habitats and Species data base of the Washington
Department of Wildlife and the Natural Heritage Program data base of the Washington
Department of Natural Resources (WDNR, 1993).
REGULATORY REQUHUAEENTS
Federal Regulations
All federal actions or projects receiving federal funding are subject to the 1969
National Environmental Policy Act (NEPA). Section 401 of the Clean Water Act
(CWA) mandates that federally permitted activities in wetlands comply with the CWA
and state water quality standards. The principal applicable federal law regulating
activities in or near wetlands is Section 404 of the CWA. Under Section 404 of the
CWA, the U.S. Army Corps of Engineers (Corps) has been given the responsibility
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Wedand Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
and authority to regulate the discharge of dredged or fill materials into waters and
adjacent wetlands of the United States (Federal Register, 1986).
Section 404 permitting is most commonly applied to freshwater wetlands. Two kinds
of permits are issued by the Corps: General and Individual. General Permits (also
known as Nationwide Permits, or NWPs) cover proposals that would have minimal
adverse impacts on the environment. The NWP for wetland alterations applicable to
the Houser Way Project is NWP 26. This NWP specifically addresses wetlands which
are (1) above the headwaters of a river or stream (that point in the watercourse at which
the mean annual discharge is less than five cubic feet per second) or (2) hydrologically
isolated. Such permits apply to fills and other impacts of less than one acre. Proposed
impacts from 0.99 acre to two acres also require a Water Quality Certification under
Section 401 of the CWA from the Department of Ecology (see below).
State Regulations
The Washington State Department of Ecology (Ecology) becomes involved through a
requirement for Coastal Zone Management Consistency under the authority of the U.S.
Coastal Zone Management Act (16 U.S.C. 1451 et. seq.) and its regulations (15 CFR
Parts 923-930). In this process, Ecology reviews projects for consistency with state
requirements, including Shorelines Permits. If a project is consistent, Ecology issues
certification. Note that the local jurisdiction typically administers Shoreline
Management Plans.
In addition to Coastal Zone consistency, Ecology issues Water Quality Certification
(Federal Clean Water Act Sec. 401; Chapter 173-225 WAC) for activities which may
result in discharges into surface waters.
All actions which may impact the natural or built environment are subject to the State
Environmental Policy Act (SEPA) of 1971 (with new implementation rules adopted in
1984, Chapter 197-11 WAC) and, in Western Washington, to the Puget Sound Water
Quality Act (Chapter 90.70 RCW). The State Hydraulic Code requires Hydraulic
Project Approval for projects below the ordinary high water mark, and the Floodplain
Management Program has jurisdiction over construction in floodways and floodplains
that may affect flood elevations and/or flood protection.
Local Regulations
Permits from the cities with jurisdiction over the project area must be granted before
the commencement of construction in any wetland or wetland buffer. Most cities
require a wetland delineation and preparation of a wetland mitigation plan for all
wetlands affected by the project. The final approval of both the wetland delineation
and the mitigation plan is granted by the city in question.
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
The City of Renton regulates wetlands under its Wetlands Management Ordinance
(Title IV, Chapter 32, ##4346). Under the Ordinance, wetlands may be assigned one of
three ratings, as follows:
"1. Very HiPh Quality Wetlands-
Category I wetlands are wetlands greater than 2,200 sq. ft. which meet one or more of the following
criteria:
a. The presence of species listed by federal or state government as endangered or threatened, or the
presence of essential habitat for those species;
b. Wetlands having 40% to 60% permanent open water(in dispersed patches or otherwise) with
two or more vegetation classes;
c. Wetlands equal to or greater than ten acres in size and having three or more vegetation classes,
one of which is open water;
d. The presence of plant associations of infrequent occurrence; or at the geographic limits of their
occurrence; or
e. Wetlands assigned the Unique/Outstanding#1 rating in the current King County Wetlands
inventory 1991 or as thereafter amended.
2. High Quality Wetlands-
Category 2 wetlands are wetlands greater than 2,200 sq. ft. which meet one or more of the following
criteria:
a. Wetlands greater than 2,200 sq. ft. that are not Category 1 or 3 wetlands;
b. Wetlands that have heron rookeries or raptor nesting trees, but are not Category 1 wetlands;
c. Wetlands of any size located at the headwaters of a watercourse, but are not Category 1
wetlands;
d. Wetlands assigned the Significant#2 rating in the current King County Wetlands Inventory 1991
or as thereafter amended;
e. Wetlands having minimum existing evidence of human related physical alteration such as diking,
ditching, channelization.
3. _Lower Quality Wetlands -
Category 3 wetlands are wetlands greater than 45,000 sq. ft. which meet one or more of the
following criteria:
a. Wetlands that are severely disturbed. Severely disturbed wetlands are wetlands which meet the
following criteria:
(1) Are characterized by hydrologic isolation, human-related hydrologic alterations such as
diking, ditching, channelization, and/or outlet modification; and
(2) Have soils alterations such as the presence of fill, soil removal, and/or compaction of soils;
and
(3) May have altered vegetation.
b. Wetlands that are newly emerging. Newly emerging wetlands are:
(1) Wetlands occurring on top of fill materials; and
(2) Characterized by emergent vegetation, low plant species richness and used minimally by
wildlife. These wetlands are generally found in the areas such as the Green River Valley
and Black River Drainage Basin.
c. All other wetlands not classified as Category 1 or 2 such as smaller, high quality wetlands."
The Ordinance also establishes minimum buffers of 100, 50, and 25 feet for Category
1, 2, and 3 wetlands, respectively. Alterations to wetlands or their required buffers are
allowed by the City only under specified conditions.
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
The City recognizes that application of the Ordinance may deny all reasonable use of a
given property. If such circumstances are demonstrated, development may be allowed
which is consistent with the general purposes of the Ordinance and the public interest.
Environmental impacts, including impacts to wetlands, are reviewed by the
Environmental Review Committee of the City's Development Services Division. A
wetland development permit is required prior to any development or alteration of a
property which contains wetlands.
Ili TACTS
Construction activities will include: roadway excavation, development of embankments
and drainage systems, paving, construction of a wetpond for surface water
management, and development of a wetland mitigation area. The open drainage
channel will be filled, and the wetland adjacent to the drainage channel will be
excavated during construction activities. The wetland soils within the drainage channel
will be stockpiled for use in the mitigation wetland, as applicable.
NMGATION CONCEPTS
Mitigation Requirements
According to the City of Renton's Wetlands Management Ordinance, mitigation for
impacts to wetlands must be considered in the following order: (1) avoid disturbance to
wetlands and/or buffers; (2) minimize impacts to wetlands and/or buffers; (3)
compensate for any wetland or buffer impacts; (4) restore any wetlands or buffers
impacted; and (5) create new wetlands and buffers to replace those which were lost.
The City maintains a policy of balancing community desires for economic
development, public health, safety, and welfare with support for the concept of no net
loss of wetland acreage, functions, and values. The City encourages protection of high
value wetlands, restoration of disturbed or low quality wetlands, and creation of new
wetlands to offset unavoidable impacts or losses.
For this project, the design team considered all practical efforts to avoid and minimize
potential impacts to the wetland, including modification of the preferred alignment,
restricting specific construction activities during certain times of the year, and limiting
clearing and grubbing only to those areas necessary to construct the project. Avoidance
of wetlands, however, will not be possible in this case due to the location of the
wetland in the only practicable alignment path of the new roadway. Accordingly,
mitigation measures for this project have relied heavily on wetland creation as
compensation for impacts to wetlands.
Goals and Objectives
The goal of the mitigation plan will be to maintain or improve the functions and values
which are presently provided by the wetland in this area, which include:
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
• Flood storage/desynchronization
• Water quality improvement
• Wildlife habitat
Mitigation will be accomplished in several ways. The project is situated at a point
where hillside drainage reaches the valley floor. The project site, as well as other areas
downstream of the project, have flooded in the past during large storm events. The
functions of flood storage/desynchronization and water quality improvement will be
provided through construction of a grass-lined swale/ditch approximately 1,600 feet
long on the west side of the roadway to convey both on-site flows and the regional
flows entering the south end of the site. These flows will be conveyed to a wetpond
constructed on the east side of the North 8th Street/Houser Way intersection.
Additional flood storage will be provided in a created wetland adjacent to the wetpond
on the north side which will be able to receive overflows from the wetpond during
severe storm.events. Under normal circumstances, however, the wetland will not
receive flows from the wetpond. The wetpond will discharge at Houser Way and
North 8th Street to the existing storm drain system.
Wetland and wildlife habitat will be provided by creating approximately 11,340 square
feet of palustrine wetland in an existing upland area at the intersection of North 8th
Street and Houser Way. Additional habitat will also be provided for approximately
5,400 square feet of the wetpond area. The created wetland will contain a mosaic of
several habitat types, including emergent vegetation, shrubs, and trees. Shrubs and
trees will be planted on the margins of the wetpond. Shrubs and trees will provide
shade for both the wetland and the wetpond and help to moderate water temperature.
One of the objectives of this plan is to create wetland and wildlife habitat on-site. Not
only will this avoid habitat fragmentation, but this strategy will also render maintenance
and monitoring programs more efficient and cost effective.
Because the area for wetland and wetpond creation is limited, the full 25 feet of buffer
for the wetland will not be available. However, the wetland will still be effectively
buffered from intrusion and disturbance by the following elements. In addition to the
wetland plantings, native vegetation will be planted between the created wetland and
the roadway to buffer the area from human and domestic animal intrusion. The buffer
will be planted with native upland tree and shrub species such as hawthorn, currant,
and rose, which will discourage entry into the wetland. In addition, the east side of the
created wetland will be buffered by the slope of the I-405 embankment. These
elements were discussed with the City of Renton Planning Department staff member
assigned to the project during a preliminary review of the wetland mitigation concepts.
The buffer concepts were considered to provide adequate protection for the wetland and
were approved.
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
The mitigation concepts are consistent with the spirit of the City's intent for wetlands
management, in particular, "the City encourages land development projects which seek
to improve the hydrologic and wildlife habitat functions of low value wetlands (4-32-
1B. Policy and Purpose).
Conceptual Site Plan
The criteria for selecting a mitigation site included the following considerations: (1) a
preference for sites located within the same drainage basin; and (2) sites located within
the project right-of-way. Due to the nature of the steep topography and existing land
uses within the Fast Lake Washington drainage basin, the potential for suitable wetland
mitigation sites is extremely limited. Several sites were examined within Gene Coulon
Park, including areas adjacent to Johns Creek and the Trestle Marsh. However,
mitigation at these sites would primarily involve enhancement of existing wetland
areas, and the City does not recognize enhancement as compensatory mitigation. The
areas within the project site will be designed to provide the same, if not greater,
functions and values as the existing wetland/drainage system. The wetland and
wetpond site is a grassy, wooded upland area located at the north end of the project
area, between the end of North 8th Street and the toe of the I-405 embankment.
It is of primary importance that wetland hydrologic conditions be provided in the
created wetland. This will be accomplished by excavating a basin at the new wetland
site and allowing seeps and springs at the base of the I-405 embankment to provide a
water supply to the wetland.
The location of the mitigation site is also important. One of the goals of this plan to
avoid habitat fragmentation; accordingly, the created wetland will be situated so that it
forms a continuum with adjacent and nearby natural areas along the toe of the I-405
embankment.
Clearing and Erosion Control
During construction, all machinery, materials, stockpiled soils, and construction
activity will be confined to the areas allotted and approved by the City for construction
related operations. Areas used to stockpile soils will be protected and covered to
prevent drying and erosion.
An erosion control plan will be implemented at the construction site which will employ
standard erosion control practices required by the City. The mitigation wetland and
buffer boundaries will be clearly marked with highly visible markers such as bright
orange barrier fencing so that unauthorized construction activities do not occur in these
areas. Straw bales and silt fences will be placed along the construction limits during
and immediately after construction.
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
Plant Palette
Shrubs and trees will be planted in groups designed to duplicate and supplement the
plant communities in the existing wetland/drainage channel. Planting will be done by
hand or using small mechanized equipment that will not compact soils. Within the
mitigated wetland, a variety of native tree, shrub, and emergent species will be planted
at appropriate elevations (with respect to seasonal water levels). Native tree and shrub
species will also be planted on the margins of the wetpond. These species may include
the following:
Common Name Taxonomic Name
Trees: western hemlock Tsuga heterophylla
black cottonwood Populus balsamifera
Shrubs: willow Salix spp.
salmonberry Rubus spectabilis
Herbs: great bulrush Scirpus validus
small-fruited bulrush Scirpus microcarpus
spike rush Eleocharis spp.
daggerleaf rush Juncus ensifolius
sedges Carex spp.
Contractors will be required to obtain plant species commercially available from local
sources and native to western Washington.
If applicable, following excavation, the exposed surface of the created wetland will be
lined with hydric soils excavated from the drainage channel. It is expected that the
seed bank in these soils will supply additional plant species beginning in the first
growing season. These volunteer plant species include water cress, cattails, horsetail,
and red alder. They will contribute to the mosaic of habitat types planned for the new
wetland.
In addition to the wetland plantings, a strip of native vegetation will be planted between
the mitigation wetland and the roadway to buffer the area from human and domestic
animal intrusion. The buffer will be planted with native upland tree and shrub species
which will discourage entry into the wetland, such as hawthorn, currant, and rose
species. The area will also be hydroseeded with a standard erosion control mix.
MAINTENANCE
Maintenance of the mitigation site will begin after completion of construction and
continue for three years. After acceptance of the initial planting, the construction
contractor will be responsible for plant survival for a period of one year. After this
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT '
period, maintenance will be performed by the City of Renton and would be confined to
repairing vandalism, repairing erosion damage, minor revegetation, and noxious weed
control.
MONITORING AND REPORTING
The progress of the mitigation project will be evaluated seasonally for a period of three
years by qualified technical personnel, using wetland monitoring protocols developed
for the site and approved by the City. Observations will be made during the
monitoring period of growth patterns; any apparent plant stress, pest, or parasite
infestation; the adequacy of the water supply; and any invasion or spread by noxious
weed species. Monitoring of the revegetated areas will also assess the success of the
establishment of the native species.
The results of the monitoring program will be recorded in an annual report prepared for
review by the City and other appropriate agencies. This report will be prepared in a
quality and format consistent with published scientific literature so that information
contained within the report may be used for future wetland mitigation projects.
SUCCESS CRrITY IA
The following criteria are proposed by which to evaluate the success of the mitigation
measures:
1. Ninety-five percent plant survival rate after the first year, as guaranteed by the
landscaping contractor. After the first year, a maximum of 20 percent mortality
will be allowed.
2. Areal cover development according to the following:
Emergent Species
80% cover after three years
Shrub Species
1st year -20%-30% cover
2nd year - 30%-45% cover
3rd year - 45%-75% cover
Tree Species
1 st year - 10%-20% cover
2nd year - 20%-30% cover
3rd year - >45% cover
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
CONTINGENCY PLAN
If the monitoring results indicate that success criteria are not being met, it may be
necessary to implement the contingency plan. Careful attention to construction
management is essential in ensuring that problems do not arise.
Any plant species with a 30% or greater mortality rate after two growing seasons will
be replaced with either the same or a more appropriate approved species. The
landscaping contractor will guarantee 90 percent survivorship for one year following
initial planting for losses due to defects in materials or workmanship. Dead plants will
be replaced at no charge as part of the guarantee during the first year. Replacements
made by a landscaper will be subject to the same conditions and will meet the same
standards as specified for the original planting.
FINAL MITIGATION PLAN/CONSTRUCTION DRAWINGS
A final mitigation workplan for use by the mitigation contractor, including construction
drawings and contract specifications for planting and maintenance of the mitigation
area, will be prepared following acceptance of this Wetland Mitigation Concepts
Report.
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Wetland Mitigation Concepts Report, Houser Way Relocation Project - DRAFT
REFERENCES
Adolfson Associates, Inc. 1993. Houser Way Wetlands Study. Seattle, Washington.
Entranco. 1993. Houser Way Relocation Project, Stage II Study. Bellevue,
Washington.
King County. 1990. Sensitive Areas Map Folio. Planning and Community
Development Division, King County, Washington.
King County. 1990. Wetlands Inventory, Volume 2 East. Environmental Division.
Bellevue, Washington.
City of Renton. 1986. City of Renton Comprehensive Plan Compendium. Renton,
Washington.
City of Renton. 1991. City of Renton Fish and Wildlife Habitat. Prepared by David
Evans and Associates, Inc. Renton, Washington.
City of Renton. 1992. Critical Areas Inventory, City of Renton Wetlands and Stream
Corridors. Prepared by Jones & Stokes Associates in association with R.W. Beck
and Associates. Bellevue, Washington.
City of Renton. 1992. Critical Areas Maps. Long Range Planning, Planning/Building
Public Works, Technical Services. Renton, Washington.
City of Renton. 1992. Wetlands Management. Ordinance No. 4346. Title IV,
Chapter 32, of Ordinance No. 4260 Code of General Ordinances of the City of
Renton, Washington. Renton, Washington.
Washington State Department of Natural Resources. Data base regarding endangered,
threatened, and sensitive plants and high quality native plant communities and
wetlands. Olympia, Washington.
Washington State Department of Wildlife. 1993. Priority Habitat and Species and
Nongame Systems, Mercer Island Quadrangle. Olympia, Washington.
PERSONAL COMMUNICATIONS
Fisher, Larry. Washington State Department of Fisheries, Regional Habitat Manager.
Issaquah, Washington. October 27, 1993.
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