HomeMy WebLinkAboutMiscSTANDARD STREAM STUDY NARRATIVE
AND HABITAT DATA REPORT
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
Prepared for:
The Boeing Company
Renton, Washington
Prepared by:
Amee Foster Wheeler
Environment & Infrastructure, Inc.
3500 188th Street SW, Suite 601
Lynnwood, Washington 98037
(425) 921-4000
January 2015
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TABLE OF CONTENTS
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Page
1.0 INTRODUCTION ........................................................................................................... 1
2.0 STANDARD STREAM STUDY NARRATIVE ................................................................. 7
2.1 STREAM CLASSIFICATION ...................................................................................... 7
2.2 VEGETATIVE COVER ............................................................................................. 7
2.3 ECOLOGICAL FUNCTION ........................................................................................ 8
2.4 FISH AND WILDLIFE ............................................................................................... 9
2.4.1 Mammals ................................................................................................ 9
2.4.2 Birds ........................................................................................................ 9
2.4.3 Amphibians and Reptiles ........................................................................ 9
2.4.4 Fish ....................................................................................................... 10
2.5 MEASURES TO PROTECT TREES AND VEGETATION .............................................. 12
2.6 No NET Loss OF ECOLOGICAL FUNCTION .......................................................... 12
3.0 HABITAT DATA REPORT ............................................................................................ 13
3.1 HABITATDIVERSITY ............................................................................................ 13
3.2 MIGRATION CORRIDORS ..................................................................................... 14
3.3 SPECIES AND COVER TYPES ............................................................................... 14
3.4 IDENTIFICATION OF DISTURBED AREAS ................................................................ 15
3.5 EXISTING HABITAT VALUES AND FUNCTIONS ........................................................ 15
3.5.1 Temperature ......................................................................................... 16
3.5.2 Water Quality ........................................................................................ 16
3.5.3 Reach Sinuosity .................................................................................... 16
3.5.4 Vegetative Conditions ........................................................................... 16
3.5.5 Floodplain Condition ............................................................................. 17
3.5.6 Habitat Values and Functions at the Project Site .................................. 17
3.5. 7 Habitat Alterations and Impacts and Proposed Habitat
Management Program .......................................................................... 17
4.0 REFERENCES ............................................................................................................. 19
Table 1
Table 2
Table 3
Table 4
TABLES
Small Mammals Reported to Occur Along the Lower Cedar River
Birds Reported to Occur Along the Lower Cedar River
Non-Native Fish Species Introduced into the Lake Washington/Lake Union
System
Different Aquatic Life Uses and Their Associated Numeric Temperature Criteria
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Figure 1
Figure 2
Figure 3
Figure 4
Figure 5
Figure 6
Figure 7
TABLE OF CONTENTS
(Continued)
FIGURES
Vicinity Map
Aerial Photograph of Boeing South Aircraft Bridge
Plan View of Boeing South Aircraft Bridge and Proposed Lighting
Plan View of Proposed Boeing South Aircraft Bridge Lighting and Solar Panel
Placement
Cross-Sectional Views of Proposed Lighting
Side Views of Solar Panel Support Box and Mounting Bracket
Back View of Solar Panel Support Box
APPENDIX
Appendix A Photographic Log
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STANDARD STREAM STUDY NARRATIVE
AND HABITAT DATA REPORT
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
1.0 INTRODUCTION
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The Boeing Company (Boeing) proposes to conduct maintenance activities on its South Aircraft
Bridge (the Bridge) located in Renton, Washington, on the lower Cedar River (LCR) south of Boeing's
North Aircraft Bridge (Figures 1, 2, and 3). The project site extends across the length of the Bridge
(approximately 200 feet) between the east and west banks of the LCR (Figures 3 and 4). The
proposed project consists of the following elements:
• Place light-emitting diode (LED) lamps along footpath on the Bridge (Figures 3, 4, and 5);
and;
• Install two 3-foot by 5-foot solar panels on the Bridge (Figures 3, 4, 6 and 7).
The City of Renton expressed concerns regarding potential light impingement on the adjacent LCR
resulting from installation of new light fixtures on the Bridge. The focus of this study is to assess
potential habitat alteration to the LCR and its associated riparian habitat due to the proposed
installation of LED lighting along the footpath of the Bridge. Boeing's proposed lighting installation is
being conducted to improve safety at the facility for Boeing employees and contractors who must work
at night. The proposed plan will install a 200-foot-long, 24-volt, 250-watt LED amber-hued rope
lighting across the entire length of the Bridge along the footpath on the south side of the Bridge
(Figures 3 and 4). The proposed lights (587 nanometer wavelength) will have a luminous flux of 14.9
lumens per foot and the 200 linear feet of lighting will only add a total of 2,980 lumens to the Bridge
walkway (equivalent to one 4-foot fluorescent tube, but amber instead of white). The lights will be
mounted on the bridge curb only 9 inches off the ground with lighting directed horizontally across the
walkway (Figure 5). The use of LED amber-hued lighting and its placement at near deck level will
prevent errant light from illuminating the underlying LCR. The bridge deck is constructed of solid
concrete rather than grating, so that there are no gaps in the bridge deck through which light can
reach the underlying river.
Lights will be powered by a stand-alone system of two 3-foot x 5-foot solar panels and battery storage
units. The solar panels will be mounted on the south side of the bridge structure, one on the east end
and one on the west end, landward of the ordinary high water mark (OHWM) (Figures 3, 4, 6, and 7).
No construction activities will occur and no structures will be placed below the OHWM. The proposed
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use of LED lighting is also expected to be more environmentally sustainable, substantially decreasing
energy consumption when compared to other types of lighting such as incandescent, halogen, and
mercury vapor.
Under the Renton Municipal Code (RMC) 4-8-120C (Submittal Requirements -Specific to Application
Type: Land Use Applications), the City requires the following environmental reports to be included
with Boeing's permit application submittal for the proposed project:
Stream or Lake Study, Standard: A report shall be prepared by a qualified biologist, unless
otherwise determined by the Administrator, and include the following information:
a. Site Map: Site map(s) indicating, at a scale no smaller than one inch equals twenty feet
(1" = 20') (unless otherwise approved by the Administrator of the Department of Community
and Economic Development or designee):
i. The entire parcel of land owned by the applicant, including one hundred feet (100') of the
abutting parcels through which the water body(ies) flow(s);
ii. The OHWM determined in the field by a qualified biologist pursuant to RMC 4-3-050L 1 b
(the OHWM must also be flagged in the field);
iii. Stream or lake classification, as recorded in the City of Renton Water Class Map in RMC
4-3-050Q4 or RMC 4-3-090 (if unclassified, see "Supplemental Stream or Lake Study"
below);
iv. Topography of the site and abutting lands in relation to the stream(s) and its/their
buffer(s) at contour intervals of two feet (2') where slopes are less than ten percent (10%),
and of five feet (5') where slopes are ten percent (10%) or greater;
v. One hundred (100) year floodplain and floodway boundaries, including one hundred feet
(100') of the abutting parcels through which the water body(ies) flow(s);
vi. Site drainage patterns, using arrows to indicate the direction of major drainage flow;
vii. Top view and typical cross-section views of the stream or lake bed, banks, and buffers
to scale;
viii. The vegetative cover of the entire site, including the stream or lake, banks, riparian
area, and/or abutting wetland areas, extending one hundred feet (100') upstream and
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downstream from the property line. Include position, species, and size of all trees at least
ten inches (10") average diameter that are within one hundred feet (100') of the OHWM;
ix. The location, width, depth, and length of all existing and proposed structures, roads,
stormwater management facilities, wastewater treatment and installations in relation to the
stream/lake and its/their buffer(s); and
x. Location of site access, ingress and egress.
b. Grading Plan: A grading plan prepared in accordance with RMC 4-8-120D7, and showing
contour intervals of two feet (2') where slopes are less than ten percent (10%), and of five feet
(5') where slopes are ten percent (10%) or greater.
c. Stream or Lake Assessment Narrative: A narrative report on eight and one-half inch (8.5")
by eleven inch (11") paper shall be prepared to accompany the site plan and describes:
i. The stream or lake classification as recorded in the City of Renton Water Class Map in
RMC 4-3-05004 or RMC 4-3-090;
ii. The vegetative cover of the site, including the stream or lake, banks, riparian area,
wetland areas, and flood hazard areas extending one hundred feet (100') upstream and
downstream from the property line, including the impacts of the proposal on the identified
vegetation;
iii. The ecological functions currently provided by the stream/lake and existing riparian area
and the impacts of the proposal on the identified ecological functions;
iv. Observed or reported fish and wildlife that make use of the area including, but not limited
to, salmonids, mammals, and bird nesting, breeding, and feeding/foraging areas, inciuding
the impacts of the proposal on the identified fish and wildlife;
v. Measures to protect trees, as defined per RMC 4-11-200, and vegetation; and
vi. For shorelines regulated under RMC 4-3-090, Shoreline Master Program, the study shall
demonstrate if the proposal meets the criteria of no net loss of ecological functions as
described in RMC 4-3-090D2. If the proposal requires mitigation for substantial impacts to
the existing vegetation buffer in order to demonstrate no net loss of ecological functions, a
supplemental stream or lake study may be required by the Administrator of the Department
of Community and Economic Development or designee. (Ord. 5137, 4-25-2005; Ord. 5633,
10-24-2011).
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Habitat Data Report: Habitat data reports include:
a. Site Plan: The site plan shall indicate:
i. The vegetative cover types reflecting the general boundaries of the different plant
communities on the site;
ii. The exact locations and specifications for all activities associated with site development
including the type, extent and method of operations;
iii. Top view and typical cross-section views of critical habitat/wildlife habitat to scale;
iv. The results of searches of the Washington Department of Fish and Wildlife's Natural
Heritage and Non-Game Data System databases;
v. The results of searches of the Washington Department of Fish and Wildlife Priority
Habitat and Species database.
b. Narrative Report: A narrative report shall be prepared to accompany the site plan which
describes:
i. The layers, diversity and variety of habitat found on the site;
ii. The location of any migration or movement corridors;
iii. The species typically associated with the cover types, including an identification of any
critical wildlife species that might be expected to be found;
iv. Identification of any areas that have been previously disturbed or degraded by human
activity or natural processes;
v. A summary of existing habitat functions and values, utilizing a habitat evaluation
procedure or methodology approved by the City;
vi. A summary of proposed habitat alterations and impacts and proposed habitat
management program. Potential impacts may include but are not limited to clearing of
vegetation, fragmentation of wildlife habitat, expected decrease in species diversity or
quantity, changes in water quality, increases in human intrusion, and impacts on wetlands
or water resources. (Ord. 4835, 3-27-2000)
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This report provides a description of the environmental and habitat attributes of the project site where
the Bridge Lighting project is to occur, as defined by RMC 4-8-120C. Sections 2.0 and 3.0 present the
requisite information for the Standard Stream Narrative and Habitat Data Report, respectively.
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2.0 STANDARD STREAM STUDY NARRATIVE
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This section presents the standard stream study narrative, providing information about existing habitat
conditions and functions of the LCR adjacent to the proposed project site.
2.1 STREAM CLASSIFICATION
According to RMC 4-3-05004 (City of Renton Water Class Map), the LCR in the vicinity of the project
site is Class 1 water.
2.2 VEGETATIVE COVER
An Amee Foster Wheeler biologist, Bob Stuart, conducted site surveys on May 14, 2014 from 1200 to
1300 and on November 24, 2014 from 1400 to 1500, in order to assess habitat conditions and
vegetative cover along the LCR shoreline adjacent to and within 100 feet of the project site. The
project site is defined as the South Aircraft Bridge where it crosses the LCR approximately 3,950 feet
south of its mouth, where it discharges to Lake Washington. The South Aircraft Bridge is used by
Boeing to transport aircraft (i.e., 737s) from Boeing's production facility located on the east side of the
LCR to the Renton Municipal Airport where the planes are launched and landed. The Boeing facility
and the Renton Municipal Airport consist primarily of concrete and asphalt surfaces.
A vegetation survey was conducted along the east and west banks of the LCR adjacent to and
extending 100 feet upstream and downstream of the South Aircraft Bridge (Figure 2). Appendix A
provides a photo log depicting habitat conditions and vegetation along the riparian zone of the east
and west banks of the LCR adjacent to the project site.
The riparian zone along the west bank of the LCR south of and within 100 feet of the Bridge is narrow
(6 to 12 feet wide), abutting an 8-foot-high concrete flood-control wall (Appendix A, Photos 1, 2, 4,
and 9). Riparian vegetation at the time of the visit was very sparse and was limited primarily to
patches of reed canarygrass (Phalaris arundinacea), Japanese knotweed (Polygonum cuspidatum),
horsetail (Equisetum f/uviatile), Himalayan blackberry (Rubus armeniacus), and alder (A/nus rubra)
(Appendix A, Photos 5 through 9). Reed canarygrass, Japanese knotweed, and Himalayan blackberry
are listed as noxious weeds by King County. The width of the riparian area is limited by the concrete
flood-control wall (Appendix A, Photos 1 and 2). No trees with trunks greater than or equal to
10 inches in diameter at breast-height (DBH) are located within 100 feet of south of the Bridge on the
west bank.
The west bank of the LCR within 100 feet north of the Bridge is more heavily vegetated than that
south of the Bridge (Figure 2 and Appendix A, Photos 10 through 12). Vegetation on the west bank of
the LCR within 100 feet north of the Bridge consists of alder, unidentified species of willow ( Salix
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spp.), reed canarygrass, Japanese knotweed, and Himalayan blackberry, as well as an unidentified
species of evergreen tree. No trees with trunks greater than or equal to 10 inches DBH are located
within 100 feet north of the Bridge on the west bank.
The east bank of the LCR within 100 feet south of the Bridge is more heavily vegetated than the west
bank south of the Bridge (Figure 2 and Appendix A, Photo 13). Riparian vegetation on the east bank
south of the Bridge is similar to that located on the west bank north of the bridge, with the exception
that the riparian corridor is not confined by a fiood-control wall. The Cedar River Trail Park,
maintained by the City of Renton. is located along the east bank of the LCR and consists of
manicured lawns, ornamental shrubs and native vegetation (Appendix A, Photo 15). An 8-foot-wide
asphalt pedestrian path is located in the Cedar River Trail Park, within 60 feet of the LCR. The Boeing
plant is located within 75 feet of the LCR (Figures 1 and 2). No trees with trunks greater than or equal
to 10 inches DBH are located within 100 feet south of the Bridge on the east bank.
The vegetation on the east bank of the LCR within 100 feet north of the Bridge is similar to that south
of the bridge (Appendix A, Photos 14 through 18). The Cedar River Trail Park extends north to the
Boeing property at the mouth of the LCR and consists of manicured lawns, ornamental shrubs and
native vegetation, and an asphalt pedestrian path (Figure 2 and Appendix A, Photo 15). No trees with
trunks greater than or equal to 10 inches DBH are located within 100 feet north of the Bridge on the
east bank.
2.3 ECOLOGICAL FUNCTION
Riparian habitats have important ecological functions other than providing habitat for birds and other
wildlife. Healthy riparian vegetation protects banks from erosion, infiuences in-channel aquatic
habitats, maintains favorable water temperature for fish through shading, filters runoff, and provides
nutrients. Riparian vegetation creates meanders, increases habitat complexity, and can protect
against scour during severe storm events. Riparian habitats link upland and aquatic habitats. Upland
habitats have a critical role in watershed function and affect riparian and aquatic habitats, particularly
in drier, low-elevation sites.
The riparian zone along the east and west banks of the LCR within 100 feet of the project site is
sparsely vegetated and includes a number of invasive species, as discussed in Section 2.2, above.
The primary ecological functions provided by riparian vegetation along the east and west banks of the
LCR within 100 feet of the project site include:
• Nesting and foraging habitat for birds and small mammals,
• Input of terrestrial insects from overhanging vegetation.
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• Input of allochthonous organic matter (via leaf fall),
• Limited erosion control, and
• Limited habitat complexity.
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The LCR is a man made channel created in 1912 when the river was diverted as a tributary to the
former Black River directly to Lake Washington. The LCR is channelized and substantially altered, so
that there is very limited riparian area to provide all of the potential ecological functions of an
unaltered habitat. Riparian vegetation provides very little, if any, shading to the LCR because of the
dominance of small shrubs and the lack of large trees. Both banks of the river in the project area are
contained within levees and/or flood-control walls, so there is no potential for the creation of meanders
or off-channel habitat. Because of extensive development along both banks of the river in the project
area (Boeing to the east and west and the Renton Municipal Airport to the west), there is little, if any,
transition between riparian and upland habitats.
2.4 FISH AND WILDLIFE
This section addresses fish and wildlife species that may use the LCR in the vicinity of the project site.
2.4.1 Mammals
No mammals or signs of mammal use were observed during the site visits. Given the level of
development in the project area, it is likely that only small mammals such as squirrels, mice, rats,
voles, moles, raccoons, opossums, muskrats, and river otters use the riparian areas along the LCR
shoreline within 100 feet of the project area. Richter and Azous (1997), conducting small-mammal
surveys in a wetland along the LCR, reported 13 species of mammals (Table 1). These, as well as
other small mammals common to the Puget lowlands, may occur along the LCR adjacent to the
project site.
2.4.2 Birds
Several bird species were observed during the site visits, inciuding American crow ( Corvus
brachyrhynchos), American robin (Turdus migratorius), Canada goose (Branta canadensis) and
European starling (Sturnus vulgaris). Richter and Azous (1997) conducted bird surveys in a wetland of
the LCR between late May and mid-June in 1988, 1989, 1991 1992, and 1995 to determine
distribution and relative abundance. They reported 58 species of birds (Table 2). It is likely that these,
as well as other species of birds common to the Puget lowlands, nest or forage in the project vicinity.
2.4.3 Amphibians and Reptiles
No amphibians or reptiles were observed during the site visits; however, it is likely that amphibian
(e.g., Anurans) and reptile species (e.g., turtles) found in the Lake Washington basin may use the
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areas within the site vicinity. Richter and Azous (1997) reported the occurrence of six amphibian
species in the LCR:
• Ensatina (salamander) (Ensatina eschscholtzii),
• Long-toed salamander (Ambystoma macrodactylus),
• Northwestern salamander (A. gracile),
• Pacific tree frog (Pseudoacris regil/a),
• Red-legged frog (Rana aurora), and
• Western red-backed salamander (Plethodon vehiculum).
No information was located listing reptile species occurring along the LCR in the project vicinity;
however, reptiles listed for King County (King County, 2008) that could occur in the project vicinity
include:
• Common garter snake (Thamnophis sirtalis),
• Northern alligator lizard (Elgaria coerulea),
• Northwestern garter snake (T. ordinoides),
• Painted turtle ( Chrysemys picta),
• Rubber boa ( Charina bottae ),
• Slider (Trachemys scrip/a),
• Western fence lizard ( Sceloporus occidentalis), and
• Western terrestrial garter snake ( T. elegans).
2.4.4 Fish
Small fish were observed jumping in the LCR adjacent to the project site during the site visits.
Although they could not be identified, they appeared to be small salmonids. The Lake Washington
system, including the LCR adjacent to the project site, hosts many fish species, including five
salmonid species: Chinook salmon (Oncorhynchus tshawytscha), coho salmon (0. kisutch),
sockeye/kokanee salmon (0. nerka), coastal cutthroat trout (0. clarki clark1), and steelhead/rainbow
trout ( 0. mykiss). Anadromous forms of each of these species use the Cedar River system as
migratory, forage, nursery, and spawning habitat, so individuals are present in the river both as adults
during migrations to spawning grounds and as juveniles (Kerwin, 2001 ). All of these species occur
seasonally in the LCR adjacent to the project site. Additionally, there have been isolated reports of
coastal/Puget Sound bull trout ( Sa/velinus confluentus) occurring in the Lake Washington system;
however, it is believed that few bull trout occur in the Lake Washington system, if they occur at all.
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Puget Sound Chinook salmon, Puget Sound steelhead trout, and bull trout are federally-listed species
under the Endangered Species Act.
Nonanadromous forms of winter steelhead (rainbow trout), sockeye (kokanee), and cutthroat trout
may also occur in the LCR. Resident rainbow trout spend their entire life in the Lake Washington
system. The resident rainbow trout population was sustained with hatchery plants because they rarely
successfully reproduce in Water Resource Inventory Area (WRIA) 8; however, releases of hatchery
rainbow trout have been all but eliminated. Nonanadromous coastal cutthroat trout also occur in the
Lake Washington system and are much more abundant than the anadromous form. Kokanee salmon
is the freshwater, resident form of 0. nerka. Some progeny from the parents of anadromous sockeye
may also remain in Lake Washington for all or a portion of their lives (resident/anadromous sockeye)
(Kerwin, 2001 ).
The largest single population of adfluvial bull trout in western Washington is found above Cedar Falls
in the upper Cedar River watershed. It is believed that a small number of bull trout pass through the
reservoir and downstream hydroelectric facilities to the river reaches below Cedar Falls. However, it is
apparently not sufficient to support the establishment of bull trout populations under the current
ecological conditions (Corps, 2002).
Native char, presumably bull trout, have been observed in the fish ladder viewing pool at the Hiram M.
Chittenden Locks as recently as 1997, while isolated reports of native char being caught in or around
Lake Washington occur every few years. A large juvenile char, again, presumably a bull trout
(-250 millimeter [mm], 3 year old), was caught in the LCR in July 1998. An adult char was also caught
in the LCR in April of 1993 (Corps, 2002).
Based on this information, occurrence of bull trout in the LCR adjacent to the project site is expected
to be extremely limited, if they occur at all.
Species endemic to the Lake Washington system include the northern pike minnow (Ptychocheilus
oregonensis), peamouth (Mylocheilus caurinus), sculpins (Coitus spp.), and longfin smelt (Spirinchus
thaleichthys) (Weitkamp et al., 2000; Wydoski and Whitney, 2003). Twenty-four non-native fish
species (Table 3) have been identified in the Lake Washington/Lake Union system. A number of these
species are now believed to be no longer present in the system. Some of these species are known to
prey on juvenile salmon (e.g., smallmouth bass) while others are potential competitors with juvenile
salmonids for food (Kerwin, 2001 ).
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2.5 MEASURES TO PROTECT TREES AND VEGETATION
The proposed project will not occur in areas with existing trees or riparian vegetation. No direct or
indirect impacts to riparian vegetation or trees will occur as a result of the proposed project; therefore,
no measures to protect vegetation or trees have been incorporated into the work plan.
2.6 No NET Loss OF ECOLOGICAL FUNCTION
The project will result in no net loss of ecological function in the riparian zone of the LCR adjacent to
and 100 feet upstream and downstream of the Bridge. As described above, the LCR adjacent to the
project site provides limited ecological function due to low habitat diversity and complexity.
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3.0 HABITAT DATA REPORT
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The habitat data report, as required by the City of Renton and described in RMC 4-8-120C, will
provide pertinent habitat and ecological function information for the immediate project site where the
Bridge project is to occur. Subsequent sections of the report will discuss following:
• The layers, diversity and variety of habitat found on the site;
• The location of any migration or movement corridors;
• The species typically associated with the cover types, including an identification of any
critical wildlife species that might be expected to be found;
• Identification of any areas that have been previously disturbed or degraded by human
activity or natural processes;
• A summary of existing habitat functions and values; and
• A summary of proposed habitat alterations and impacts and proposed habitat
management program.
3.1 HABITAT DIVERSITY
The LCR downstream of 1-405 (approximately 1.6 miles) is an artificial channel created early in the
20'h century and is completely constrained between levees and revetments. This reach was regularly
dredged to prevent flooding from the time of its completion in 1912 until the mid-1970s. Portions of the
reach were again dredged in 1999 for the first time since the mid-1970s. Flood-control dredging is
proposed during the summer of 2015. In-stream habitat in the reach is almost entirely glide, with little
habitat complexity. Land uses prevent floodplain connectivity and have eliminated the potential for re-
connection with a natural floodplain or the establishment of a riparian corridor. Channelization and
existing land uses also prevent significant large woody debris (LWD) from accumulating in the
channel. The reach is also very low-gradient and depositional, and the substrates have high levels of
fine sediments (Corps, 2004; Parametrix and Adolfson, 2010).
The shoreline along the LCR adjacent to the project site consists of developed property belonging to
Boeing and the City of Renton.
With realignment of the Cedar River into Lake Washington in 1912, the zone of sediment deposition
was localized through the City of Renton (Perkins, 1994 ). The vast majority, if not all, of the non-
suspendable sediment load is now deposited along this reach because Lake Washington lies at the
river's mouth. With the path of the river fixed by armored banks, progressive infilling of the channel
resulted. Sediment is continually deposited in the downstream 2 miles of the river and in an enlarging
delta in Lake Washington.
Amee Foster Wheeler
Project No. LY14160300 13
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Aquatic habitat within the LCR adjacent to the project site consists of a low relief benthic habitat
composed of small cobbles with some gravel and no boulders. LWD in the stretch of the LCR
adjacent to the project site is extremely limited (Appendix A, Photo 1 ). River discharge at the time of
the site visits in May and November 2014 was approximately 1,000 cubic feet per second (USGS,
2014). Channelization of the LCR has eliminated meanders within the lower river, such that the lower
1.6 miles of river consists of a uniform glide habitat with a nearly complete absence of riffles and
pools. Habitat diversity along the LCR adjacent to the project site is extremely limited.
3.2 MIGRATION CORRIDORS
A query of the Washington Department of Fish and Wildlife's Priority Habitat and Species (PHS)
database (http://wdfw.wa.gov/mapping/phs/) identified five salmonid species that use the LCR as a
migration corridor:
• Chinook salmon;
• Coho salmon;
• Sockeye salmon;
• Steelhead and rainbow trout; and
• Coastal cutthroat trout.
Two of the above species, Puget Sound Chinook salmon and Puget Sound steelhead trout. are listed
as threatened under the Endangered Species Act.
Bull trout, a member of the char family, may also be found in the LCR and is also listed as threatened
under the Endangered Species Act. Population status information and extent of use of this area is
currently unknown. Adult and subadult size individuals have been observed infrequently in the LCR
(below Cedar Falls), Lake Washington, and at the Locks. No spawning activity or juvenile rearing has
been observed and no distinct spawning populations are known to exist in Lake Washington outside
of the upper Cedar River above Lake Chester Morse (not accessible to bull trout within Lake
Washington) (NOAA-Fisheries and USFWS, 2008). It is unlikely that bull trout use the Cedar River as
a migratory corridor.
3.3 SPECIES AND COVER TYPES
The almost complete absence of riparian vegetation along the west bank of the LCR and the limited
riparian vegetation along the east bank adjacent to the project site and the highly developed
shorelines along both banks of the LCR severely limit habitat availability and use by multiple plant and
animal species. The concrete flood-control wall on the west bank of the LCR adjacent to the project
Amee Foster Wheeler
14 Project No. LY14160300
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site severely limits the width of the riparian zone and eliminates the transition zone from riparian to
terrestrial habitats.
Typical plant and animal assemblages and associations that would be expected along the riparian
corridor of the LCR are, for the most part, absent along the stretch adjacent to the project site.
A query of the Washington Department of Natural Resources' Natural Heritage Program online
data base (http://www.d n r. wa .gov /Resea rchScie nee/How To/Conservation Restoration/Pages/
amp_nh_data_order.aspx) did not identify any plant or terrestrial animal species of special concern in
the vicinity of the project site.
Critical wildlife species occurring at the project site include those salmonids identified in Section 2.4.4
above.
3.4 IDENTIFICATION OF DISTURBED AREAS
The entire project area is highly developed and disturbed. As stated in Section 3.1 above, the lower
1.6 miles of the LCR is an artificially-created channel with extensive development along both banks.
3.5 EXISTING HABITAT VALUES AND FUNCTIONS
The LCR adjacent to the project site has very limited habitat value and is low functioning. A
combination of two habitat assessment methods was used to provide a qualitative assessment of the
existing habitat values and functions. These habitat assessment methods were the U.S.
Environmental Protection Agency's (EPA's) Rapid Bioassessment Protocols for Use in Wadeable
Streams and Rivers (Barbour et al., 1999) and the U.S. Forest Service's Stream Inventory Handbook:
Levels I and II (USFS, 2010). Both methods incorporate the use of physicochemical and biological
parameters to assess habitat value and functionality. The EPA's Rapid Bioassessment Protocols
incorporates both benthic invertebrate and fish assemblages' data in evaluating habitat value and
function. For the purposes of this project, neither benthic invertebrate nor fish assemblage data were
collected as part of the evaluation process due to the necessity of applying for and receiving the
necessary permits to gather such data. The habitat assessment is based on physicochemical
conditions observed at the project site:
• Temperature;
• Water quality;
• Reach sinuosity;
• Vegetative conditions of the stream banks and the riparian zone; and
• Condition of the floodplain (e.g., accessibility from the bank, overflow, and size).
Amee Foster Wheeler
Project No. LY14160300 15
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Each of the above parameters is discussed below.
3.5.1 Temperature
Mean monthly water temperatures (°C) in the LCR at Renton for the period of 1992 through 2013
(USGS, 2014) are as follows:
• January -6.0; • July-15.5;
• February -6.4; • August -15.8;
• March -7.6; • September-13.7;
• April -9.4; • October -10.9;
• May-11.5; • November -8.1 ; and
• June -13.2; • December -6.3 .
The warmest water temperatures occur during the months of June, July, August, and September;
however, even the highest mean monthly temperatures are compliant with Washington State aquatic
life temperature criteria (Table 4 ), with the exception of the char spawning and rearing beneficial use.
Char (e.g., bull trout) do not spawn in the LCR and it is highly unlikely that they use the LCR as
rearing habitat.
3.5,2 Water Quality
No site-specific water quality data were found for the project site; however, water quality monitoring
has been conducted in south Lake Washington by the Washington State Department of Ecology
(Ecology). Washington State's Water Quality Assessment [303(d) & 305(b) Report] (Ecology, 2008)
identified exceedances of water quality standards for temperature, pH, dissolved oxygen, and fecal
coliforms in the LCR. No chemical exceedances of state water quality criteria were identified for the
LCR adjacent to the project site.
3.5.3 Reach Sinuosity
As discussed above, the lower 1.6 miles of the LCR are channelized and much of the shoreline on
both banks is restrained by bulkheads. There is no sinuosity within the entire 1.6 miles of the LCR.
Stream sinuosity can provide increased habitat complexity through the creation of pools, riffles, and
glides, as well as the creation of off-channel habitat.
3.5.4 Vegetative Conditions
As described previously, riparian vegetation is sparse along the both banks of the LCR within 100 feet
of the project site. As such, habitat diversity and functionality along this reach of the LCR is severely
limited.
Amee Foster Wheeler
16 Project No. LY14160300
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3.5.5 Floodplain Condition
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The LCR is an artificially-created channel confined by levees and bulkheads on each bank. Except in
extreme discharge conditions, the LCR has very little connectivity with its floodplain and virtually no
potential for formation of off-channel habitat within the floodplain. Because of the low gradient of the
LCR, it functions as a sediment depositional zone. The City of Renton and the U.S. Army Corps of
Engineers periodically dredge the LCR for flood-control purposes. The City of Renton is proposing
flood-control dredging for the summer of 2015.
3.5.6 Habitat Values and Functions at the Project Site
A qualitative assessment of the LCR adjacent to the project site indicates that it provides very low
habitat value and function due primarily to the sparse riparian vegetation and habitat complexity.
3.5.7 Habitat Alterations and Impacts and Proposed Habitat Management Program
The project will not involve any in-water components, nor will any portion of the project occur in the
riparian zone of the LCR. The one component of the project that could potentially affect aquatic biota
in the LCR is light impingement from the additional lighting proposed for the Bridge.
The proposed lights will be amber (587 nanometer wavelength) with a luminous flux of 14.9 lumens
per foot. The 200 linear feet of lighting will only add a total of 2,980 lumens to the Bridge walkway
(equivalent to one 4-foot fluorescent tube, but amber instead of white). Because the lights will be
mounted only 9 inches above the bridge deck and directed horizontally across the walkway, there will
be no direct light impingement on the surface water of the LCR. Additionally, the proposed solar
panels and battery storage units mounted on each end of the south side of the bridge will be located
landward of the OHWM, so there will be no overwater shading attributable to these structures.
Therefore, the project will not alter existing habitat conditions along the LCR. No habitat management
or mitigation program is required for this project and none are proposed.
Amee Foster Wheeler
Project No. LY14160300 17
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Amee Foster Wheeler
18 Project No. LY 14 160300
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4.0 REFERENCES
Barbour, M.T., J. Gerritsen, B.C. Snyder, and J.B. Stribling. 1999. Rapid Bioassessment Protocols for
Use in Streams and Wadeable Rivers. U.S. Environmental Protection Agency, Office of Water,
EPA 841-B-99-002, Washington, D.C.
Corps (U.S. Army Corps of Engineers). 2002. Montlake Cut Slope Stabilization Project Environmental
Assessment Biological Evaluation -Lake Washington Ship Canal, Seattle, Washington.
Corps, Seattle District, Seattle, Washington.
Corps (U.S. Army Corps of Engineers). 2004. Cedar River at Renton Flood Damage Reduction
Operation and Maintenance Manual -Cedar River Section 205 (Renton, Washington). U.S.
Army Corps of Engineers, Seattle District, Seattle, Washington.
Ecology (Washington State Department of Ecology). 2008. Washington State's 2008 Water Quality
Assessment [303(d) & 305(b) Report]. Ecology, Olympia,
http://www.ecy.wa.gov/programs/wq/303d/2008/index.htm1 (accessed April 15, 2012).
Kerwin, J. 2001. Salmon and Steelhead Habitat Limiting Factors Report for the Cedar-Sammamish
Basin (Water Resource Inventory Area 8). Washington Conservation Commission, Olympia.
King County. 2008. King County Biodiversity Report 2008. King County, Seattle, Washington,
http://www.kingcounty.gov/environment/animalsAndPlants/biodiversity/king-county-
biodiversity-report.aspx (accessed September 1, 2009).
NOAA-Fisheries and USFWS (National Oceanic and Atmospheric Administration, National Marine
Fisheries Service and the U.S. Fish and Wildlife Service). 2008. Endangered Species Act-
Section 7 Consultation Biological Opinion and Magnuson-Stevens Fishery Conservation and
Management Act Essential Fish Habitat Consultation. The 1-405 Tukwila to Renton
Improvement Project (1-5 to SR 169 -Phase 2) Lower Cedar River, Cedar River Sixth Field
HUG: 171100120106, 171100120302, King County, Washington. NOAA-Fisheries and
USFWS, Lacey, Washington, https://pcts.nmfs.noaa.gov/pls/pcts-pub/sxn7.pcts_
upload.download?p_file=F13441/200704219_ 405_trip_03-03-2008.pdf (accessed May 19,
2012).
Parametrix and Adolfson (Adolfson Associates, Inc.). 2010. City of Renton Shoreline Master Program
Update Restoration Plan. Prepared for the City of Renton, Washington, http://rentonwa.gov/
uploadedFiles/ Business/EDNSP/planning/4.3%20Final%20Restoration%20Plan%20Uune-
10).pdf?n=2474 (accessed April 13, 2012).
Perkins, S.J. 1994. The shrinking Cedar River -Channel changes following flow regime regulation
and bank armoring, in Proceedings of Effects of Human-Induced Changes on Hydrologic
Systems. American Water Resources Association 1994 Annual Summer Symposium,
p. 649-658.
Richter, K.O., and Azous, A.L. 1997. Amphibian distribution, abundance, and habitat use, in Azous,
A.L., and Horner, R.R. (eds.), Wetlands and Urbanization -Implications for the Future, final
report. Puget Sound Wetlands and Stormwater Management Research Program, Washington
State Department of Ecology, Olympia, King County Water and Land Resources Division,
Amee Foster Wheeler
Project No. LY14160300 19
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Seattle, Washington, and University of Washington, Seattle, http://your.kingcounty.gov/dnrp/
library/archive-documents/wlr/wetlands-urbanization-report/wet-rept.pdf (accessed
September 1, 2009).
USFS (U.S. Forest Service). 2010. Stream Inventory Handbook: Levels I and II (Version 2.10). USFS,
Pacific Northwest Region, Region 6, Portland, Oregon.
USGS (U.S. Geological Survey). 2014. USGS Surface-Water Monthly Statistics for Washington -
USGS 12119000 Cedar River at Renton. Department of the Interior, USGS, National Water
Information System, http://nwis.waterdata.usgs.gov/wa/nwis/monthly/
?referred_module=sw&site_no=12119000&por_ 12119000_ 18=1179603,00010, 18,1992-
02,2013-09&format=html_table&date_format=YYYY-MM-
DD&rdb_compression=file&submitted_form=parameter_selection_list (accessed May 9, 2014).
Weitkamp, D.E., Ruggerone, G.T., Sacha, L., Howell, J., and Bachen, B. 2000. Factors Affecting
Chinook Populations -Background Report. City of Seattle, Seattle, Washington.
Wydoski, R.S., and Whitney, R.R. 2003. Inland Fishes of Washington. American Fisheries Society,
Bethesda, Maryland, and University of Washington Press, Seattle.
Amee Foster Wheeler
20 Project No. L Y14160300
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TABLES
TABLE 1
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SMALL MAMMALS REPORTED TO OCCUR ALONG THE LOWER CEDAR RIVER'
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
Species
Common Name and Scientific Name (Genus species)
Creeping vole Microtus oregoni
Deer mouse Peromyscus manicu/atus
Ermine Mustela ermine
Forest deer mouse Peromyscus oreas
Long-tailed vole Microtus Jongicaudus
Marsh shrew Sorex bendirei
Masked shrew Sorex cinereus
Note/s}
1. Source: Richter and Azous, 1997.
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Montane shrew
Shrew-mole
Southern red-backed vole
Townsend's chipmunk
Trowbridge's shrew
Vagrant shrew
Sorex montico/us
Neurotrichus gibbsii
C/ethryonomys gapperi
Tamias townsendii
Sorex trowbridgei
Sorex vagrans
Amee Foster Wheeler
Page 1
TABLE2
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BIRDS REPORTED TO OCCUR ALONG THE LOWER CEDAR RIVER'
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
Species
Common Name and Scientific Name Genus soecies
American crow Corvus brachvrhvnchos
American aoldfinch Cardue/is tristis
American robin Turdus miaratorius
Black-canned chickadee Parus atricanil/us
Belted kinafisher Cerv/e a/cvon
Bewick's wren Thrvomanes bewickii
Brown-headed cow bird Molothrus ater
Black-headed grosbeak Pheucticus
me/anoceohalus
Brewer's blackbird Euphagus
cvanoceoha/us
Brown creeoer Certhia Americana
Black-throated gray Dendroica nigrescens
warbler
Bushtit Psaltrioarus minimus
Chestnut-backed Parus rufescens
chickadee
Cedar waxwinn Bombvcil/a cedrorum
Cooner's hawk Acciniter coonerii
Common raven Corvus corax
Common vellow throat Geoth/vnis trichas
Dark-eved iunco Junco hvemalis
Downv woodoecker Picoides aubescens
Eurooean starlina Sturnus vu/aaris
Evening grosbeak Coccothraustes
vesoertinus
Fox snarrow Passerella iliaca
Great blue heron Ardea herodias
Golden-crowned kinolet Reau/us satraaa
Hairv woodoecker Picoides vil/osus
Hermit thrush Catharus auttatus
Marsh wren Cistothorus aalustris
MacGillivrav's warbler Geoth/vnis tolmiei
Northern flicker Co/antes auratus
Note(s)
1. Source: Richter and Azous, 1997.
p:\boeing renton~y14160300 s bridge lighting lake-
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Northern """mv owl
Oranae-crowned warbler
Pine siskin
Pacific-slone flvcatcher
Purnle finch
Red-breasted nuthatch
Red-breasted sansucker
Red crossbill
Red-eyed vireo
Rufous-sided towhee
Ruffed grouse
Rubv-crowned kinalet
Red-winged blackbird
Sora
Sona soarrow
Sham-shinned hawk
Steller's iav
Swainson's thrush
Townsend's warbler
Vaux·s swift
Violet-green swallow
Virainia rail
Warblino vireo
Western tanaaer
Willow flvcatcher
Wilson's warbler
Winter wren
Wood duck
Yellow warbler
G/aucidium anoma
Vermivora celata
Cardue/is oinus
Emnidonax difficilis
Carnodacusnurnureus
Sitta Canadensis
Snhvraoicus ruber
Loxia curvirostra
Vireo olivaceus
Pioi/o ervthroohthalmus
Bonasa umbel/us
Reau/us calendu/a
Agelaius phoeniceus
Porzana Carolina
Melosoiza melodia
Acciaiter striatus
Cvanocitta stelleri
Catharus ustulatus
Setoahaaa townsendi
Chaetura vauxi
Tachycineta tha/assina
Ral/us limico/a
Vireo ai/vus
Piranaa /udoviciana
Emoidonax trail/ii
Cardellina ousilla
Troo/odvtes hiemalis
Aix soonsa
Dendroica oetechia
Amee Foster Wheeler
Page 2
TABLE 3
NON-NATIVE FISH SPECIES INTRODUCED INTO
THE LAKE WASHINGTON/LAKE UNION SYSTEM'
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
Common Name Scientific Name Status
American shad Alosa sapidissima Uncommon strays
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Atlantic salmon Sa/mo salar Can exceed 1,000 oer vear
Black bullhead
Black crannie
Blueaill
Brook trout
Brown bullhead
Brown trout
Channel catfish
Cherrv salmon
Common carp
Fathead minnow
Goldfish
Grass caro
Lake trout
Lake whitefish
Laraemouth bass
Pumpkinseed sunfish
Smallmouth bass
Tench
Warmouth
Weather loach
White craooie
Yellow oerch
Note(s)
1. Source: Kerwin, 2001.
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lctalurus me/as
Pomoxis niaromaculatus
Leoomis macrochei/us
Salvelinus fontinalis
lctalurus nebulosus
Sa/mo trutta
lctalurus punctatus
Oncorhvnchus masou
Cvorinus carpio
Pimeohales notatus
Carassius auratus
Ctenopharenaodon idella
Salvelinus namavcush
Coreqonus clupeaformis
Microoterus salmoides
Lepomis qibbosus
Micropterus do/omieui
Tinca tinca
Lepomis qulosus
Misaurnus anaillicaudatus
Pomoxis annularis
Perea flavescens
Extinct
Common
Common
Rarelv cauoht
Rare, mav be extinct
No observed reproduction
Rarelv cauoht
Extinct
Abundant
Unknown
Intermittent
Trioloids onlv
Extinct
Extinct
Common
Abundant
Common
Abundant
No observed reproduction
No observed reproduction
Uncommon
Abundant
Amee Foster Wheeler
Page3
TABLE4
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DIFFERENT AQUATIC LIFE USES AND THEIR ASSOCIATED NUMERIC TEMPERATURE
CRITERIA'
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
Beneficial Use Temperature' (°C)
Char Soawnina and Rearina
Core Summer Salmonid Habitat
Salmonid Soawnina, Rearina, and Miaration
Salmonid Rearina and Miaration onlv
Note(s)
1. Source: Ecology, 2012.
2. Based on the 7-day average of the daily maximum temperatures.
Abbreviation(s)
°C = degrees Celsius
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12
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17.5
17.5
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Page 4
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FIGURES
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LAKE WASHINGTON
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DRIVING DIRECTIONS FROM 1-5
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Merge onto Rainier Ave. S
Tum Right onto Airport Way S.
Airport Way S. becomes Logan Ave. S. (Gate
access required onto Boeing property)
End at 737 Logan Ave. N .. Renton, WA 98057
APPROXIMATE SCALE IN FEET -------0 400 800 1600
VICINITY MAP
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
B: GSM Date: 01-12-2015 Pro·ectNo. LY11160300
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Renton, Washington
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Renton, Washington i SOLAR PANEL SUPPORT BOX {h
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Renton, Washington
By: RES Date: 01/13/15 Prot No.: LY14160300
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APPENDIX A
Photographic Log
Ph oto 1
Photo 2
APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton , Washington
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APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton , Washington
West bank of LCR immediate! south of Brid e .
Loo kin south w e st from east ba nk of LCR a t wes t ba n k.
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APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton , Washington
Ja anese knotweed on west bank of LCR south of Bri d e .
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Photo 7
Photo 8
APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton , Washington
B lackber o n west bank of LCR so uth of B rid e.
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APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
Loo kin at west bank of LCR north of Brid e .
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Photo 11
APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton , Washington
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APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton, Washington
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Photo 13 Lookin south from Brid e at east bank of the LCR note alder trees at left center .
Photo 14 Lookin north from Brid e at east bank of LCR.
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Photo 15
Photo 16
APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton , Washington
Lookin north at east bank of LCR blackber and reed cana
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APPENDIX A
PHOTOGRAPHIC LOG
Boeing South Aircraft Bridge Lighting Project
Renton , Washington
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Ph oto 17 east bank of LCR north of Brid e reed cana rass in cente r .
Ph oto 18
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