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Prepared by:
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FAPWT-09-175
3�93
Hydraulic Report
Strander Boulevard Extension Project
Cities of Renton and Tukwila, Washington
20 July 2011
Submitted by
BergerABAM
33301 Ninth Avenue South,Suite 300
Federal Way,Washington 98003-2600
Job No. FAPWT-09-175
TABLE OF CONTENTS
EnecutiveSummary...............................................................................................................................i
ExistingConditions...............................................................................................................................3
ExistingDevelopment...........................................................................................................................3
Topography............................................................................................................................................4
Soi Is........................................................................................................................................................4
GeologicalHazards................................................................................................................................4
Floodplain..............................................................................................................................................4
Wetlands................................................................................................................................................4
ExistingUtilities........................................................................................................................5
ExistingDrainage Areas........................................................................................................................6
ProposedConditions.............................................................................................................................7
Phase1.......................................................................................................................................7
Phase11......................................................................................................................................7 ,
Phase111.....................................................................................................................................9 '
Requirements......................................................................................................................... 10 '
FlowControl........................................................................................................................................ 12 I
WaterQuality......................................................................................................................................12
ConveyanceSystem ...........................................................................................................................12
Pond....................................................................................................................................................13
ErosionControl................................................................................................................................... 14
LIST OF TABLES
Table 1: Summary of Applicable Treated Surfaces - Phase II........................................................il
Table 2: Summary of Applicable Treated Surfaces - Phase III.......................................................11
LIST OF FIGURES
Figure1: Vicinity Map......................................................................................................................... 1
Figure2: Phase II ................................................................................................................................ 8
Figure3: Phase III ............................................................................................................................... 9 '
LIST OF APPENDICES I'
Appendix A Background Information I�I
Appendix B Plans and Details '�,
Appendix C Drainage Calculations '
Appendix D Renton's Standard Plans �,
Appendix E Pump Station Memorandum ��I
Appendix F Geotechnical Report ,
H��draulic Kepnrt F.�.PIVT-09-175,Berger,aB.A'�1
Strander Boulevard Extension Project 20 July 2011
Cities c�f Renton and Tukr�-ila,61�'ashington Page ii
EXECUTIVE SUMMARY
The primary goal of the Strander Boulevard extension project is to provide a commuter and
freight connection behveen West Valley High�vay (State Route 181 [SR 181]) and Oakesdale
Avenue SW. The existing Strander Boulevard dead-ends at approximately 190 feet eastward
from the intersection with West Valley high�vay. 'The project is located in both the cities of
Renton and Tukw�ila, Washington. The City of Renton is the lead agency. See Figure 1,
Vicinitv Map.
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Figure 1: Vicinity Map II
The Strander Boulevard extension project will ultimately extend Strander Boulevard to the west !
from the intersection with SR 181 to connect to SW 27th Street at the intersection with Naches
Avenue SW. The roadway extension is approximately 1,450 feet long. The project area is
relatively flat. Within the project limits,Union Pacific Railroad (UPRR) and BNSF Railway both
have railroad tracks perpendicular to the Strander Boulevard roadway extension. The tracks '
are separated by approximately 430 feet. In order to extend Strander Boulevard, railroad
bridges will be constructed for each of the railway lines at their existing elevations. The
roadway v��ill slope down just east of SR 181 to go under the bridges and then rise to the east to
Hydrau(ic Report FAPWT-09-175,BergerABAA4
Strander Boulevard Extension Project 20 July 2011
Cities nf Rent��n and Tuk�+�ila,11�ashin;;ton Pas�e 7�if 14
connect ti�ith SW 27th Street. The low point of the roadway will be approximately 25 feet lower
than the surrounding land.
This project involves three phases. The first phase, which is alread}� constructed, made
improvements between Oakesdale Avenue and Naches Avenue. The second phase (current
project) �vill construct the bridge for the BNSF railroad and two travel lanes between Naches
Avenue and the Sound Transit Station. Detention and �vater quality facilities will be
constructed as part of Phase II. The third phase (future project) will expand the roadti�ay to two
lanes in each direction separated by a median or left-turn lane. A joint-use trail for pedestrians
and bicyclists ti�ill be provided on the north side of the roadway. A bridge�vill be constructed
to carry UPRR over Strander Boulevard.
Sound Transit will be constructing a commuter rail station just to the north of the project,
between the t��o railroad lines. BNSF v��ill be constructing a third rail on the east side of their
existing tracks. A loop road built as part of Phase III �vill connect the lowered Strander
Boulevard to the rail station.
The Strander Boulevard extension project will collect stormwater runoff in a closed conveyance
s}�stem. Storm�ti�ater will be routed to a wet ti�ell (pump station). The pump station�vill raise
the storm�vater to the elevation of the surrounding area. The stormwater will be discharged
from the pump into a storm�.vater �-��ater qualit��/detention pond. The pond ���ill outfall to an
existi►�g �vetland.
In Phase II, the project �-vill encompass approximately 5.25 acres. The project site consists of
approximately 0.35 acre(6.7 percent) of existing impervious area and 4.90 acres (93.3 percent) of
existing pervious area. After construction, the Phase II project site will consist of 3.0 acres
(57.1 percent) of impervious area and 2.25 acres(42.9 percent) of pervious area.
For the final build-out condition (Phase III), the project will encompass approximately
6.05 acres. The project site consists of approximately 1.06 acres (17.5 percent) of existing
impervious area and 4.99 acres (82.5 percent) of existing pervious area. Based on the
preliminary design, after construction, the project site will consist of 4.58 acres (75.6 percent) of
impervious area and L48 acres (24.4 percent) of pervious area.
Hydraulic Repurt FAPLI�T-09-1i5,BergerABA��9
Strander Boulevard Extension Project 20 July 2O l]
Cities of Kenton and Tuk�ti•ila,1Vashin�trnl Pa�e 2��f I-1
EXISTING CONDITIONS
T'here are t�vo rail facilities�vithin the project area. UPRR and BNSF Railway are located on
western and eastern sides of the project, respectively. Both of these rail lines reside on
embankments that are approximately 10 to 15 feet higher than the surrounding land. The top of
rail elevation is+33.5 and�34.5 for BNSF and UPRR, respectively. The east property line of
BNSF right-of-way is the boundary line between the cities of Tuk���ila and Renton.
Strander Boulevard is the missing roadway�link for a continuous thoroughfare betcveen
Southcenter Boulevard to the far west and East Valley Road to the far east. Currentl}�, vehicles
must travel approximately three-quarters of a mile to the north to travel east/west on Grady
Way or travel almost 1 mile south to travel east/west on South 180th Street.
In the project vicinit��, between SR 181 and the Strander Boulevard dead-end, there is one lane
in each direction�a�ith a two-way, left-turn lane (TWLTL). The TWLTL becomes a left-turn lane
at the intersection of SR 181. The existing asphalt concrete pavement is in poor condition.
There is curb and gutter on both the north and south sides of this segment.
The Interurban Trail running north/south,just west of UPRR, crosses on the western side of the '
project site. The trail is located just east of where Strander Boulevard dead-ends. A 6-foot ',
side�valk on the north side of Strander Boulevard allows a connection point for pedestrians and I
bicyclists from SR 181 to the Interurban Trail. The City of Tukwila uses an area just east of j
UPRR, and south of Strander Boulevard, for stockpiling material. I,
Between the two rails, there are no developments ar buildings. This area is mostly grass with
some small shrubs. The 700-foot-wide area between BNSF and Naches Avenue has similar
characteristics. There are intermittent paved road�vays on both of these properties. These
roadways�vere part of the facilities for the Longacres Racetrack that previously resided
approximately 2,000 feet to the north. When the racetrack was demolished, the roads�vere left
in place.
EXISTING DEVELOPMENT
There are t�vo fast food restaurants on the northeast and south�vest corners of SR 181 and
Strander Boulevard. Taco Bell and Jack-in-the-Box reside on the north and south sides,
respecHvely. Per City of Tukwila's Zoning Map (December 1995), this area, as well as the area
west of the city limits, is zoned as a Tukwila Urban Center(TUC).
On the east side of the project area, within the city of Renton, the majority of the area is zoned as
Commercial Office by the City of Renton (City of Renton Zoning Map, February 2010). A
federal reserve bank resides on the southwest corner of Oakesdale Avenue and SW 27th Street.
Another banking facility resides at the end of Naches Avenue, approximately 1,500 feet south of
the intersection with SW 27th Street. There is a small area south of the Bank of America site that
is zoned as a Resource Conservation Area. See Appendix A for a copy of the zoning maps for
the t�vo cities.
Hy-draulic Report FAP4tiT-09-1i5,BergerABAA4
Strander Boulevard Extension Project 20 July 20]]
' Cities of Renton and Tukwila,Washington Page�of]4
L
TOPOGRAPHY
The project area is relatively flat �vith an approximate change in grade over the site of 10 feet. In
the project��icinity, the elevation varies from+30 to+20. There are three small 5-foot-high dirt
mounds (top elevation being+30) on the north side of the Tukwila property. Wetland Q/R also
resides on the Tukw�ila property. Wetland Q/R is described belo�v in the section on Wetlands.
The majority of Wetland Q/R is at Elevation+25 but has some small depressions that reach
doti�n to+20. The majority of the project area is at Elevation+25.
Both the UPRR and BNSF rail lines are situated on top of an embankment approximately 12 feet
above the surrounding area. Top of embankment elevations are approximately+34 and +33 for
the UPRR and BNSF railways, respectively.
S01 LS
According to the U.S. Deparhnent of Agriculture's King County Soil Survey Sheet No. 11, the
dominant soil betvveen the railroads is Puget Silty Clay Loam (Pu). To the east of BNSF, the
soils vary bet�n�een Woodinville Silt Loam(Wo) and Puyallup Fine Sandy Loam (Py). All three
soil types have slow runoff potential and have a high water holding capacity. Soils Wo and Pu
have a slow permeabilit��rate�vhile Py has a moderately rapid permeability rate. See
Appendix A for a copy of the King County Soil Survey and descriptions of the soil properties.
GEOLOGICAL HAZARDS
According to King County's geographic information systems (GIS) data, there are no geological
hazards�vithin the project vicinity. See Appendix A for a copy of the GIS data.
FLOODPLAIN
Federal Emergency Management Agency (FEMA} is currently in the process of revising the
flood insurance rate map (FIRM), Pane10978K, for the area surrounding the project. T'he Cities
have adopted FEMA's proposed revisions to the FIRM. Based on the proposed revisions, the
project site is considered to be in "Zone X," which are areas determined to be outside the
0.20 percent annua] chance floodplain. See Appendix A for a cop�� of the proposed FEI�-1A
floodplain.
WETLANDS
There are numerous �vetlands in the project vicinity. See the ��etland figure in Appendix A for
the location of all ti�etlands. David Evans and Associates prepared a Wetland Technical
Memorandum (WTM) for the City of Renton in November 2007. This document describes the
wetlands in the project area. This document also discusses impacts to the wetlands, which were
based on a previous roadway configuration. The impacts that are discussed in the WTM do not
apply to the current Strander Boulevard extension project. The main body of the above-
mentioned memo is located in Appendix A.
H��draulic Keport FA['41T-09-]7�, Ber�;erAB:a1�1
Strander Boulevard Extension Project 20 July 201 I
Cities of Renton and Tukwila.�V'ashington Page���f 14
One of the largest ti�etlands in the project vicinity is Wetland Q/R, located south of the extended
Strander Boulevard on the Tukwila property bet�veen the two rail lines. This wetland
encompasses approximately 25 acres and is considered Category II Wetland per Department of
Ecology rating system. There is a 36-inch culvert at the north end of Wetland Q/R. This culvert
conveys water from Wetland Q/R to the east under BNSF.
Wetlands A, C, D, and E are located between the UPRR tracks and the Interurban Trail.
According the WTM, these�vetlands are classified as Category III. These wetlands are�vet in
the��et season and dry in the summer season. Wetlands A, D, and E are hydrologically
isolated, meaning that any stormwater that reaches them is trapped. Wetland B is also a
Category III wetland. Wetland C is hydrologically connected to Wetland B in the wet season.
The project�vill not impact Wetlands A, B, C, or D. Wetland B is connected to Wetland Q/R by
a 36-inch culvert that runs west to east under the UPRR embankment.
�-tietland S is located at the toe of slope of BNSF's �vest embankment,just north of the extended
Strander Boulevard. Per the WTM, Wetland S is a non-jurisdictional wetland. This wetland is
hydrologically� isolated.
Springbrook Creek�h'etland and Habitat Mitigation Bank is located on the elst side of B�1SF
and south of Bank of America. The 130-acre mitigation bank was created to provide
compensation for unavoidable wetland impacts caused by future WSDOT projects. See Figure 1
vicinity map for location of Springbrook Creek Mitigation Bank.
Existing Utilities
T'here are numerous utilities in the project area: power (both underground and aerial), storm,
�n�ater, fuel, sanitary se�ver, and fiber optic (see in Appendix B for Composite Utility Drawing).
All of these utilities will need to be protected and/or relocated during construction.
In the vicinity of the proposed BNSF bridge, two parallel overhead power lines run from
Oakesdale Avenue to the east BNSF right-of-�vay line. At this point, the northern aerial
transmission(115kV) line crosses over BNSF tracks/right-of-tiTay to the�vest to eventually
terminate at Puget Sound Energy's (PSE) substation located on the southwest corner of Sound
Transit's property. At BNSF's east right-of-way line, the southern aerial distribution line
changes direction to run south, where the line goes underground to the�vest.
Located underground between the above-mentioned, east/w�est transmission lines are two
petroleum pipe lines (12-and 14-inch steel pipes). These fuel lines run east/west from
Oakesdale Avenue under BNSF and UPRR to SR 181. Approximately, 9 feet separates the two
pipes and cover varies from 6 to ll feet.
A 36-inch reinforced concrete sanitary sewer pipe runs west/east under BNSF on the south side �I
of the above-mentioned transmission lines. There is approximately 15 feet of cover over the ''
Hedraulic Report FAPtiti'T-09-175,Berger.4BAI��I ���,
Strander Boulevard Extension Project 20 Jul��20ll I
Cities of Renton and Tukwila,�ti'ashington Page�of 14 ��
sanitary sewer line. All of the above-mentioned underground pipes ���ere constructed at least 40
years ago. The condition of these pipes is unknown.
A 60-inch pressurized water pipe is located approximately 550 feet to the north and parallel to
Strander Boulevard. The water line resides in its own 30-foot right-of-way outside of the BNSF
and UPRR rights-of-way. All of the above-mentioned underground pipes were constructed at
least 40 years ago. The condition of these pipes is unknown.
An overhead power line transmission line (ll5kV) runs east/���est on the north side of the
60-inch water pipe.
A 4-inch PVC fiber optic conduit (AT&T line) and a 2-inch steel conduit (BNSF line) run
north/south on the��est side of BNSF right-of-w�ay at approximately 32.5 feet west of the
centerline of BNSF's west tracks (main track 1 [MTl]). Per BNSF's record drawings, five 2-inch
HDPE fiber optic conduits (BNSF lines) run north/south on the east side of BNSF right-of-�va��
at approximately 42.5 feet east of the centerline of BNSF's west tracks (MT7).
EXISTING DRAINAGE AREAS
The existing Taco Bell restaurant resides on 0.81 acre. The storm��-ater for this site is treated for
both water quality and detention on site. After treatment, the storm�ti�ater is discharged to a
closed conveyance system on the southeast corner of the property. From the surve��, it appears
that this system conveys stormwater on the east side of the Interurban Trail to eventually feed
the wetland located on the west side of UPRR.
The existing Jack-in-the-Box restaurant resides on 0.56 acre. It is not known at this time if
treatment is provided on site. No record draw�ings for this site were able to be located in
Tukwila's archives. From site meetings with Tukwila's maintenance department, it is believed
that this system outfalls to infiltration trenches located wTest of the UPRR tracks. It has not been
determined if these infiltration trenches��ill be able to be recreated in Phase III. If this is the
case, the area from the Jack-in-the-Box site will need to be routed through the pond in Phase III.
The area between the two rail embankments, south of the extended Strander Boulevard is flat.
This area does not appear to produce any significant runoff due to being contained within the
t�a�o embankments. Rainfall is mostly infiltrated with a small amount feeding Wetland Q/IZ.
Wetland Q/R is mostly fed bv Wetland B. Wetland Q/R flows to the east in another 36-inch
culvert that goes under the BNSF embankment to outfall on the east side.
The area between the two rail embankments, north of the extended Strander Boulevard is flat.
The ground in this area slopes slightly(0.5 percent) to the nartheast towards the BNSF
embankment. Wetland S is located approximately 100 feet north of the proposed Strander
Boulevard extension. This �vetland sits at the toe of the���estern BNSF embankment and is
approximately 330 feet long.
H}'draulic Repurt FAYlb'T-09-1��,BcrKcrABAI��I
Strander Boule��ard Extension Project 20 July 201 I
Cities��f Renton and Tuk�cila,tib'ashington Pa�;c 6��f 1�
The embankment for UPRR is approximatel�� 12 feet above the existing ground. The slopes of
the embankment feed numerous wetlands located at the toe of slope. According to the WTM,
these wetlands are hydrologically isolated.
The embankment for BNSF is also approximately 12 feet above the existing ground. Runoff
from both sides of the embankment flows to the surrounding area. There are no formalized
ditches at the toe of slope to convey the starm��ater. The change in grade from Longacres Way
to the extended Strander Boulevard is approximately 020 percent(2-foot drop over 1,000 feet).
PROPOSED CONDITIONS
The proposed Strander Boulevard extension project�vill be grade-separated from UPRR and
BNSF Railway and will pass under these railroad tracks. Current plans are to construct this
extension in three phases. Descriptions of each of these phases are as follows.
Phase 1
Phase I extends the corridor at-grade from Oakesdale Avenue SW to Naches Avenue SW. This
roadway segment is two lanes in each direction with a median dividing the lanes. Tum-lane
pockets are provided in the median at cross street locations. The roadway has 5-foot planter
strips behind each curb, with a 6-foot-wide sidewalk on the north and a 12-foot-wide sidewalk
on the south side. Construction of this phase has been completed.
Phase II
Phase II will connect the�vestern end of Phase I to the southwest corner of the Sound Transit's
property (see Figure 2 on the following page)by providing a driveway up to this location. The
Sound Transit project, to the north, will construct a road that ties into the driveway. The
driveway will be a two-lane roadway with 2-foot shoulders and curb and gutter on both sides.
The lane widths��ill vary from 16 to 19.5 feet to accommodate the turning movements of
articulated buses. A 6-foot-wide pedestrian path will be provided on the north side of the
roadwav. This sidewalk extends from the intersection with Naches Avenue SW to the end of
the driveway into Sound Transit.
Because the roadH�ay��ill be directed under BNSF, the roadway�vill be approximately 25 feet
lower than the existing grade. To accomplish the lo�ver elevation, 3H:1 V cut slopes�vill be
used. The typical roadway geometry will consist of two 11-foot lanes, 2-foot shy distance from
edge of travelled way to face of curb, curb and gutter, and a 5-foot strip behind the curb. Tl�►e
ground will be excavated 2.5 feet belo�v the proposed roadway. A 2.5-foot roadway section�Till
house an underdrain system that will capture any seepage from the surrounding soils. The
underdrains will be surrounded by gravel backfill for drains. Quarry spalls, placed 1 foot thick,
will protect the cut slopes and area behind the curb. See Typical Road Sections in Appendix B.
A railroad bridge will be constructed to carry BNSF rail traffic over this roadway connection.
The roadway section under the bridge v��ill be 2.5 feet in depth. This railroad bridge will be
constructed to accommodate the full Phase III build-out of Strander Boule��ard. The bridge and
H��draulic Report FAP4b'T-09-]i�,BergerABAb4
Strander Boulevard Extension Project 20 Julv 2011
� Cities of Renton and Tukwila,�ti`ashington Page 7 of 14
�
foundation c��ill be designed to accommodate a third rail on the bridge structure. A shoofly to
both the west and east will be required to construct this bridge.
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Figure 2: Phase II
This shoofly consists of widening the existing rail�vay embankment by placing material on both
the east and west sides. This will allow the BNSF tracks to be relocated to the�vest while the
east side of the BNSF bridge is built and then to the east�vhile the west side of the BNSF bridge
is built. The height of the embankment varies from 10 to 12 feet. The�vest and east
embankments for the shoofly will remain in place after completion of Phase II to be used by
neighboring projects.
Sound Transit will be constructing a ne�v commuter rail station to the north of the project. The
Sound Transit project is currently in the design phase. BNSF will be constructing a third rail on
the east side of their existing tracks. The BNSF project is in the preliminary design phase.
The Sound Transit project will regrade the west embankment to be incorporated into the
commuter station. The east embankment will be used by the BNSF's third rail project and by
the Sound Transit Station project. If in the future it is determined that neither of these projects
w�ill use the embankments, this project will remove the embankment and restore the area and its
drainage pattems to the existing condition.
HVdraulic Report FAP�vT-09-175,BergerABA1�1
Strander Boulevard Extension Project 20 July 20ll
Cities of Renton and Tukti�ila,VVashington Page 8 of]4
Phase II shall begin construction in the summer of 2011.
Phase III
Phase III (future project) will complete the Strander Boulevard extension (see Figure 3 below).
The Phase III roadway will be widened to four through lanes separated by a median or left-turn
lane. The median will be used to support railroad and roadway bridge supports.
A railroad bridge will be constructed to carry UPRR traffic over Strander Boulevard. A shoofly
���ill be required to construct this bridge.
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Figure 3: Phase 111
Connection to the Sound Transit Tukwila Station will be through a loop ramp constructed to tl�e
south of the Strander corridor. A roadway bridge will be constructed over Strander Boulevard
to connect to the south side of Sound Transit's property.
A joint-use trail will be provided along the narth side of Strander Boule��ard. This trail will
provide a pedestrian/bicycle connection between Oakesdale Avenue and the Interurban Trail.
Pedestrian and bicycle connections �vill be provided to the Interurban Trail and to the Sound
Transit Sounder propertv from this joint-use trail. A pedestrian bridge �vill carry the Interurban
H�•draulic Report FAP11'T-09-17�,Bergcr.AB.a��1
Strander Boulevard Extension Project 20 Jui�-201 I
Cities of Renton and Tuk�vila,11-ashington Page 9��f]�
Trail over Strander Boulevard. Traffic signals will be installed at the Naches Avenue SW/
Strander Boulevard intersection and at the Tukwila Station loop ramp/Strander Boulevard
intersection. Strander Boulevard will be lighted.
Right-in/right-out drive�vay connections will also be provided for Taco Bell,Jack-in-the-Box,
and PSE located on the east side of the intersection of SR 181 and the Strander Boulevard
extension.
A high ti�ater table at the project site will require that the roadway be constructed in a boat
section �a�here the road�aray elevation is below the design groundwater elevation. This boat
section will be constructed by driving sheet piles outside of the walls that will form the
permanent sides of the boat section. These sheet piles will be temporarily tied back to sheet pile
deadman and will provide temporary sides for the boat section.
Because the project is to be built in two phases, the stormwater system �n�ill also be built in t�vo
phases. The conveyance system for Phase II�vill accommodate the runoff from the two lanes
and the cut slopes on both sides of the roadway. A conveyance pipe needed far Phase III will
be constructed in Phase II to allo�v this pipe to be embedded in the foundation slab.
Further discussion on conveyance design and standards can be found in the Conveyance
Svstem section.
For the current project flo�v control and ���ater quality facilities ��-ill be designed for Phase II
only. Flow control and water quality facilities for Phase III were sized to verify that they would
fit within the Phase III project footprint. These Phase III calculations are provided for
informational purposes.
Further discussion on the requirements, standards used, and design of these facilities can be �
found in the sections on Flow Control and Water Quality on the following pages.
Requirements �
The proposed starm drain system analysis and design �vill comply with the following minimum
requirements set forth by the Washington State Department of Ecology's Storm�vater
Management Manual for Western Washington(SMMWW) (2005). The minimum requirements
are listed below. '
■ I�-linimum Requirement No. 1: Preparation of Stormwater Site Plans �
■ Minimum Requirement No. 2: Construction Stormwater Pollution Prevention(SWPP) ,
■ Minimum Requirement No. 3: Source Control of Pollution
■ Minimum Requirement No. 4: Preservation of Natural Drainage Systems and Outfalls
■ Minimum Requirement No.5: On-site Starmwater Management ,
■ Minimum Requirement No. 6: Runoff Treatment
■ Minimum Requirement I�o. 7: Flo�v Control
H}'draulic Repurt FAPl1%T-09-1;'�,BergerABAh7
Strander Boulevard Extension Project 20 July 201 I
Cities of Renton and Tuk��ila,lVashington Page 10 of l4
■ Minimum Requirement No. 8: Wetlands Protection
■ Minimum Requirement No.9: Basin/Watershed Planning
■ Minimum Requirement No. 10: Operation and Maintenance
Not all of the minimum requirements apply to all projects. Which requirements shall apply to a
project is determined by whether a project is considered a "redevelopment" or "new
development" project. This is determined by the amount of existing impervious surface on a
project site. If a site contains 35 percent or more of existing impervious surfaces, then the
project is considered a "redevelopment" project. If a site contains less than 35 percent of
existing impervious surfaces, then the project is considered a "new development" project. The
Strander Boulevard final project has 17.5 percent of existing impervious surfaces; therefore, it is
considered a "new development" project. Per the SMMWW, Minimum Requirement Nos. 1
to 5 shall apply to the"new" and "replaced" impervious surfaces and land disturbed.
Minimum Requirement Nos. 6 to 10 shall apply to the "new" impervious areas and "converted"
pervious areas. Converted pervious areas are areas that are converted from native vegetation to
lawn ar landscaped areas. See Appendix C for SMMWW's Flo�v Chart and requirements.
When the existing impervious area is much less than the proposed impervious areas, many
local governments require that the "replaced" impervious surfaces be brought up to current
stormv��ater standards in �vhat is termed as "retrofitting." In these situations, the "replaced"
impervious surfaces shall follow the same requirements as the "new" impervious surfaces. For
the sizing of the��ater quality and detention facilities, the "replaced" impervious surface areas
were included in the analysis for the Strander Boulevard extension project. See Appendix C for
a summary of the "new" and "replaced" areas. See Table 1 and Table 2 for the summary of
applicable treated surfaces for Phase II and Phase III, respectively.
Table 1: Summary of Applicable Treated Surfaces - Phase II
Project Area Impervious Surface Converted Pervious
Surfaces
2.71 acres(new)
5.25 acres 2.25 acres
0.29 acre(replaced)
Table 2: Summary of Applicable Treated Surfaces - Phase III
Project Area Impervious Surface Converted Pervious
Surfaces
3.67 acres (new)
6.05 acres 1.48 acres
0.90 acre (replaced)
H��draulic IZe��rt FAI'1ti'T-09-17�,BergerAB.a�1
Strander Boule��ard Extension Project 20 July 201 I
Cities of Rent�m and Tukwila,1Nashington Pa�;r]1 af I-1
FLOW CONTROL
Per the requirements in Volume 3 of the SMMVVW, a calibrated continuous simulation
hydrologic model based on the Environmental Protection Agency's Hydraulic Simulation
Program, Fortran (HSPF) must be used when designing for flow control. The hydraulic analysis
for the Strander Boulevard extension project was performed using MGSFIood, Version 3.13,
which meets this requirement. The performance standard for flow control is to match
developed discharge durations to predeveloped durations far the range of the predeveloped
discharge rates from 50 percent of the 2-year peak flo��up to the fu1150-year peak flow. The
predeveloped condition shall be considered forested, per the criteria set farth in the SMMWW.
See Appendix C far MGSFIood detention calculations for both Phase II and Phase III.
WATER QUALITY
Storm�vater treatment facilities for the project �vere analyzed and designed to meet the
minimum standards identified in Volume 5 of the 2005 SMMWW. Water quality design
volumes w�ere determined using the above-mentioned continuous runoff model in accardance
��ith the guidelines listed in Volume 5, Chapter 4 of the SMMWW for the 6-month, 24-hour
storm. Water quality facilities were sized to treat the ne�v impervious, replaced impervious,
and converted pervious surfaces in the project area.
The minimum ���ater qualit�� volume rec�uired is 13,048 cubic feet and 22,301 cubic feet for
Phase II and Phase III, respectively. The�vater quality volume calculations are given on
page 12 and page ll of the respective MGSFIood reports found in Appendix C.
Enhanced treatment is required in urban growth management area on roads �ti�ith an average
annual daily traffic of 7,500 or greater per SMMWW Volume 5, Chapter 3. At this time, it is not
kno��n what the projected traffic counts ��ill be. Traffic counts will be determined during the
final design of Phase III. At that time, it will be determined if enhanced treatment will be
required. By the definition of a high-use site by the SMMWW(Volume 5, Section 2.1), the
project�vill not use oil control facilities. This phase (II) of the project will not provide enhanced
treatment or oil control facilities.
CONVEYANCE SYSTEM
The proposed conveyance system �vas analyzed and designed uz accordance with the current
guidelines set forth in Chapter 4 of the 2009 King County Storm�ti�ater Design Manual
(KCSWDM). StarmSHED3G was used to compute the 25-year, 24-hour storm peak discharge
for all pipelines. StormSHED3G analyzes the conveyance system using the intensitti� duration
curves far Seattle(see Appendix C for StormSHED3G calculations).
Gutter flow and inlet spacing ���ere determuled b��using the Gutter Analysis method described
in the current edition of Washington State Department of Transportation (�-vSDOT) Hydraulics
Manual (see Appendix C for gutter analysis calculations).
In an earlier version of this report(dated 18 Februarv 2011) the finished profile road�va�� grade
line �vas different for Phase II and Phase IIL The profile grade for this phase (II) of the project
Hydraulic Keport FAPWT-ll9-175,BcrgcrABAhI
Strander Boulevard Extension Project 20 Jul��201 f
Citieti uf Rent�m and Tuktia-ila,1�Vashington PaKe]2 uf l�
��ill now use the Phase III roadway profile. The low point of the roadway will be located on the '
��est end of the project at approximately station "S" 16+00. All of the stormwater will be
conveyed to a Type 2 catch basin at this location. The catch basin will be fitted with an open
throat combination inlet similar to WSDOT's Standard Plan B-25.20-00. From this location, the
stormwater will be routed to the pump station located to the south. The pump station will
house two pumps and will also have a backup generator. The pump station�vill pump the
water to the stormwater pond located further to the south. (See Appendix B for the pump
station plans and Appendix E for the Pump Station Memorandum.)
In Phase III, a roadway sag v��ill be located at approximately Station "S" 14+40. This is just east
of UPRR's eastern property line. In Phase III, all of the stormwater will be routed to the
aforementioned catch basin residing at Station "S" 16+00. This catch basin has been sized to
accommodate the Phase III conveyance system that will be going against the grade of the
road��ay to collect Station "S" 16+00.
The underdrain system is expected to collect 10 to 30 gpm during high ground�vater periods.
(See page 12 of the Strander Boulevard Underpass Phase II Revised Dewatering Evaluation in
Appendix F). This underdrain system connects to the storm system to be pumped to the pond.
The existing 36-inch culvert that extends from Wetland Q/R to east of BNSF will have a
temporary extension on the west side to accommodate the shoofl}�. The size of the culvert w�ill
not be altered.
POND
The project�vill use a hvo-celled, combined �vater quality detention and starmwater pond for
treatment and detention. Water quality�treatment is contained in the bottom of the pond�vith
additional storage above for detention.
The first celYs primary role is sedimentation. Approximately 33 percent of the water quality
volume will be contained in the first cell. The first cell shall contain 4feet of water quality
storage and 1 foot of sediment storage. A berm separating the t��o cells shall be submerged
1 foot. The second cell shall have 3.1 feet of�n�ater quality starage. (See Appendix B far Pond
Geometry.)
A control structure will be placed in the second cell of a pond. This control structure shall
contain a riser pipe with orifices that are sized for the allowable discharges rates as discussed in
the flow control section above. Also in the second cell, an emergency overflow� spillway, sized
to pass the 100-year flow will be located on the south end of the pond.
The groundwater(maximum seasonal high flow of 30 gpm) will generate approximately 43,200
gallons per day (5,776 cubic feet per day). In order to accommodate the ground�vater, 0.3 feet of
storage will be provided over an area of 21, 000 square feet between the top of the water quality
storage(�n�ater surface elevation+23.7) and the bottom of the detention storage (+24.0) for an
overall approximate volume of 6,300 cubic feet.
Hydraulic Report FAPti�VT-09-17�,BergerABAn4
Strander Boulevard Extension Project 20 July 2011
Cities of Renton and Tuk�vila,Washington Page 13 of 14
The seasonal high groundwater table in the project area is approximately 4 to 5 feet belo�� the
existing ground (Elevation+19). (See Appendix F for the geotechnical report for the project.)
According to the 2009 KCSWDM, the "dead storage of�vet ponds may be provided belo�� the
groundwater level," (page 6-69). The bottom of the first cell elevation is approximately+19.7.
This is 0.7 foot above the seasonalh�high groundwater table. The bottom of detention starage is
4 feet above this at Elevation+23.7. Discharge from the pond will be routed to Wetland Q/R to
the south.
The preliminary design of the Phase III pond uses a stormwater tivetland pond. In the next
phase the footprint of the pond will almost double in size, become shallower, and will need to
be vegetated. This ti�ork will need to be completed in the dry season. Baker tanks or other such
mechanisms may need to also be employed during construction of the pond.
DOWNSTREAM ANALYSIS
Per Section 2.6.2 of the SWWMM, development projects that discharge storm�vater off site shall
complete a qualitative do�vnstream analysis. Per section 2.6.2 of the SWWMM, this analysis
"shall extend dowrnstream for the entire flow path from the project site to the receiving water or
up to 1 mile, whichever is less. If a receiving water is within one-quarter mile, the analysis shall
extend within the receiving�vater to one-quarter mile from the project site." The stormwater
pond shall discharge to the 25-acre wetland Q/IZ (considered a water of the state) that is
approximately 0.8 miles in length. A hydroperiod analysis determined there would be no affect
to the wetland. This analysis is provided in Appendix C.
EROSION CONTROL
A Temporary Erosion and Sediment Control (TESC) Plan ti�ill be prepared prior to construction.
This plan will establish the when, where, and how specific erosion control techniques will be
implemented. This plan will be constantly changing as site conditions and construction
activities change. The TESC Plan will be the responsibility of the Certified Erosion and
Sediment Control Lead. At minimum,filter fabric fences will be installed do�Tnslope of all
construction areas, and sediment traps will be used to protect ne�v and existing catch basins.
Further measures ti�ill be considered when construction methods and schedules are set. A
Stormvvater Pollution Prevention Plan will be submitted b�� the contractar and shall be
approved by the engineer of record.
H��draulic Report FAPE�ti'T-09-1�:5,BergerABA�9
Strander Boulevard Extension Project 20 July 2011
Cities of Renton and Tukta•ila,�Vashington Page 14 of 14
Hydraulic Report
Strander Boulevard Extension Project
Cities of Renton and Tukwila, Washington
Appendix A - Background Information
Zoning Maps
King County Soils Survey
Soil Descriptions
King County GIS
Flood Plain Map
Wetland Locations
David Evans and Associates Wetlands Technical Memo
Letter to Tukwila
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KINf.CnIINN ARFt.,WASHIN(.ION Nll.I1
SIiEET NO.11
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SOIL SERIES DESCRIPTION
Puget silty clay loam
Mapping Symbols: Pu
The Puget series consists of poorly drained soils that formed in alluvium in small
depressions of the river valleys under sedges and crasses at elevations ranging fr��m 10 �.�
650 feet. Slopes are 0 to 1%.The annual precipitatior i� ;� to �� inches. 7�he fro:t-�T�e
�:'3�0"] 1S ;3�)i)l1t IQ(� C!31`�
T��pical Profile:
Depth from Surfac�
0 to 60 Inches:dominantly mottled dark grayish-bro«n ,�t-:�'
grayish-brown silty clay loam
Permeahili
Slo�
Rooting Depth:
If drained,roots penetrate with difficulty to 60 inches
Depth to Seasonal High Water Table:
0 to 1 foot
Available Water Holding Capacity:
High
Runoff Potential:
Slow to pondetl
Erosion and Slippage Hazard:
Slight
Flooding Potential:
Severe
Puget Series
Page 2
Use and Management:
This soil is used for pasture and row crops.
Pasture forage yields aze 2.5 tans/acre/year if undrained and 5.0 tons/acre/yeaz if drained
with good management.
Douglas-fu, Western Hemlock, Westem Red Cedar, Red Alder, Willow, and Sitka
Spruce are important tree species. This soil has severe limitations for seedling mortality,
` plant competition, equipment limitations, and windthrow limitations because of its poor
drainage and flooding potential.
The Puget soil has severe recreational and engineering limita.tions due to its flooding
potential,high seasonal water table,and shrink-swell potential.
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SOIL SERIES DESCRIPTION
«'oodin�-ille silt loam
�Vlapping Symbol: Wo
The Woodinville series consists of neariy level and gently undulating poorly drained soils
that formed in alluvium under grasses and sedges in stream valleys. Slopes aze 0 to 2%,
annual precipitation is 35 to 55 inches,and the frost-free season is about 190 days.
Elevation ranges from sea 1eve1 to 85 feet.
Typical Profile:
� Depth from Surface:
0 to 38 Inches:Gray siliy clay loam
38 to 60 Inches: Greenish-gray silt loam
Permeability:
i
, Moderatel�� �l���r�
Rooting Depth�
{ 60 i
Depth to S���_---- '--�-- ----- - -----
. 0 to 1 foot
Available Water Holding Capacity:
High
�
Runoff Potential:
Slow
Erosion and Slippage Hazard:
Slight
Stream Overflow Hazard:
Severe
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� � Woodinville Series
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Use and Management:
Primary uses are for hay,pastore,and mw crops.
Pasture forage yields are 2.0 tons/acre/year if undrained and 5.0 tons/acre/year if drained.
Douglas-fir, Western Red Cedar, Western Hemlock, Red Alder, Willow, and Sitka
Spruce aze important tree species. These soils have severe limitations on equipment use
for site preparation and timber harvest, seedling mortality, plant competition, and
windthrow hazard for forestry use.
These soils have severe limitations on recreational and engineering uses due to their
seasonal high water table and flood hazard.
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SOII,SERIES DESCRIPTION
Puysllup fine sandy Ioam
Mapping Symbols: Py
The Puyaltup series consists of well drained soils that formed in alluvium under conifers,
hardwoods,and grasses at elevations from 20 feet to 500 fee� Slopes are 0 to 2%. The
annual precipitation is 35 to 60 inches.The frost-free season ranges from 160 to 200 days
and the mean annual au temperature is about 50 degrees F.
T�ypical Profile:
Depth from Surface:
0 to 34 Inches:Very dark grayish brown and dark grayish brown fine
sandy loam
, 34 to 60 Inches: Very dark grayish brown, dark grayish brawn, and
i dark-brown sand, loamy sand,and medium sand.
; Permeability:
' Moderately ragid
Raoting Depth:
b0 inches �
Depth to Seasonal High «-ater Table:
4 to 5 fec-
i Available Water Holding Capacit� �
Moderately high
Runoff Potential:
Slow
� Erosion and Slippage Hazard:
Slight
', Flooding Potentiat:
� Slight to severe
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� Pnyallup Series
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� Use and Management:
j Primary uses of this soil are for row crops and pasture.
IPasture forage yields are 3.5 tons/acre/year with good management.
�
Douglas-fir, Westem Hemlock, Red Alder, Willow, and Sitka Spruce aze important tree
species. This soil is rated as having severe limitations for forestry because of seedling
mortality, plant competition, and windthrow hazards, with equipment limitations also
being rated as severe.
The Puyallup soil has moderate recreational and severe engineering limitations due to its
flooding potential.
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The information included or tnis map hes been::�inp;leC by 4��c C�u�ty sta`f`-om a v�rsty o�`eaurces e�d �sutjec:'o chan�e•nithout 2oC��e �no
Counry makes no represe^.ahons or A�ara�it.es.exp e o- mF�ietl.a�to a �.er;,���n�.ete ie�s. me.r �s or r gh:s:o t�e,.�e of sxt ir r.,al or
This documen�is not intentlee for use as a survey product.rC:n�Co�ry sFal nct�e��.;aole for zny generzl. oecial.i�e�rect ircde�ta o cor c�ertal s �
damages mclutling,but nol limited to,iost revenues or tost prof:ts resulOng from the use or misuse of tne mfo�T�ation wntained on th�s map.F�n;sale cf Kmg County
ihis map or informanon on this map is prohibited except by written pertnission of Kmg County.
Da[e:11;'1012010 Source:King County iA4AP-Sensitive Areas(hltp:!lxvnv.metmkc.gov(GISfiM11AP}
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The information irGuded on this map has been compiled by Kinc County s�aflfrom a vanety o`sources and is subjecl lo change without notice.Kfng
County makes no representations or warrar.tles,exp�ess or implied,as to accuracy,completeness,timel+ness,or rights to the use of such information.
This document is not intended for use as a survey producl King Coan?y shall not be liable for any genera�.special.indirect,�nciCeeta�,or consequential a �
damages inGuding,but no[�imited to.lost revenues or lost profts resulimg from the use or misuse of ihe in�°orriafion containec o�c7is map.Any sale of Kmg County
this map or information on th-s map is prohioiled excep:by wri;ten pertnission of King County.
Date:�1%14I2010 Source�.King Coon:y 1MAP-Sensitive Areas(http;7www.metrokc.gov,'GIS,hMAPI
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tv1AT'CHLINE 430-I-��J (
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City of Renton Strander Boulevard Extension
and Union Pacific Railroad Realignment
Phase 1, Segments 2A and 2B
WETLAND TECHNICAL MEMOR:ANDUM
;
PERT0000-0006
Prepared for:
CITY OF RENTON
Prepared by:
DAVID EVANS AND ASSOCIATES,INC.
415 118th Ave. SE
Bellevue,WA 98005
,
November 2007
i
City of Renton Strander Boulevard Egtension
and Union Pacific Railroad Realignment
Phase 1, Segments 2A and 2B
WETLA,ND TECHNICAL MEMORA1vDUM
��e�0000-000a
Prepared for: ,
, CITY OF RENTON '
i
( Prepared by: Ii
I �,
Ji.m Shannon
Senior Fish and Wildlife Biologist
DAVID EVANS AND ASSOCIATES,INC.
415 118th Ave. SE
Bellevue,WA 98005
November 2007
TABLE OF CONTENTS
9.0 INTRODUCTION..........................................................................................................................1
2.0 PROJECT DESCRIPTION..........................................................................................................1
3.0 REVISED WETLAND IMPACTS...............................................................................................2
4.0 WETLAND RA1'INGS..................................................................................................................2
4.1 Wetlands H,M,P,and S...........................................................................................................4
42 Wetlands A,C,D,and E...........................................................................................................4
4.3 Wetland QR...............................................................................................................................5
4.4 Wetland T......................................................................................... ................6
.........................
4.5 Mitigation Banlcing............................
........................................................................................
5.0 SUM1ViARY.................................».................................................................................................7
6.0 REFERENCES............................�.................................................................................................7
Tables �
Table l.Permanent and Temporary Wetland and Buffer lmpacts................................................................2
Table 2.Project Wetland Classification and Jurisdiction.............................................................................3
Appendices
Appendilc 1.Vicinity Map
Appendix 2.Wetland Impacts
Appendix 3.Wetland Rating Forms
Appendix 4.Wetland Photographs
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Strander Boulevard E�Rension and Union Pacific Railroad RealignmeM Phase 1,Segments 2A and 2B
Abbreviations and Acronyms
BNSF Burlington Northern Santa Fe Railway
City City of Renton
Corps U.S.Army Corps of Engineers
DEA David Evans andAssociates, Inc.
Ecology Washington Deparnnent of Ecology .
HGM hydrogeomorphic
JARPA Joint Aquatic Resources Permit Application �'I
NEPA National Environmental Protection Act II
Project Strander Boulevard Extension and Union Pacific Railroad Realignment Project— I�'�
Phase 1, Stage 2A and 2B ',
UPRR Union Pacific Railroad j
II
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� Strander BoWevard Extension and Union Pecific Railroad Realignment Phase 1,Segments 2A and 2B
I
1.0 Introduction
At the request of the City of Renton(City),David Evans and Associates,Inc. (DEA)prepared.
this Wetland Technical Memorandum for support of the Joint Aquatic Resources Pernut
Application(JARPA)for the Strander Boulevard Extension and Union Pacific Raikoad
RealignnZent Project—Phase l, Stage 2A and 2B (Project).The project is located in the cities of
T�kwila and Renton,Washington(Appendiz 1).The Project includes parts of three elements of
a larger project(Altemative 1)that received a National Environmental Protection Act(NEPA)
Categorical Exclusion and a State Environmental Protection Act Determination of Nan
significance on July 19, 2005.
This technical memorandum complements the Wetlands Technical Discipline Report, Strander
Boulevazd Extension,dated May 2004,and includes a current project description,wetland
impacts, and wetland ratings using the VJashington Department.of Ecology(Ecology)rating
system (Hruby 2004).
2.0 Project Description
Three action alternatives were proposed in the discipline reports prepared for the NEPA.
Alternative 1 was chosen as the preferred.alternative.The current project includes portions of
' three elements from Altemative 1.These elements include:
1. Relocation of the Union Pacific Railroad(UPRR)tracks.
2. New road.way construction from West Valley Highway to Oaksdale Avenue SR7
(overpass only).
3. Modifications to Longacres Way(bridge conveying UPRR over South Longacres Way
only).
We propose to relocate the UPRR approximateIy 300 feet to the east to parallel the existing two
sets of Burlington Northem Santa Fe Railway(BNSF)tracks.The relocation will begin
approximately 1,000 feet south of Southwest 27th Street and end 5,500 feet north under
Interstate 405.We estunate approximately 125,OOU cubic yards of fill for the relocated track.
New roadway construction will include an overpass over the relocated frack that ties to West
Valley Freeway to the west and approximately 1,000 feet to the eas� It is esti.mated 250,000
cubic yazds of fill will be used for the overpass approaches.A stormwater detention and
enhanced treatment facility will be built near the overpass.
Modifications to Longacres Way wili include the construction of the UPRR bridge over
Longacres Way only. Standard railroad bridge designs will be used for this bridge.
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� Strander Boulevard Extension and Un(on Padflc Railroad Realignment Pttiase 1,Segments 2A and 2B
3.0 Revised Wettand Irnpacts
The proposed alignment of the UPRR relocation(Alternative 1 in DEA 2004)has changed from
its original design due to a change in the design of the new roadway overpass. The original
overpass was a bridge built on piers. Currently the design is an overcrossing with approaches
made of fill. This design change reduced total impacts to wetlands on-site but also changed
which wetlands will be impacted{Table 1;Appendiz 2}.
Table 1.Permanent and Temporary Wefland and Buf#'er Impacts.
Wetland Permanent PermaneM Temporary Temporary
Impacted Wetland fmpact Suffer Impact Wet�and Impact Buffer Impact
(acres) (acres} (acres) (acres)
A 0.009 4.101 0.004 0.013
C 0.191 0.042 0.138 0.012
D 0.036 4.024 0.034 0.023
E 0.022 0.026 0.019 0.019
H 0 0.026 0 0.023
M 0 0.038 U 0.036
P 0.009 0 0.005 0
QR(Cat.I} 0 0 0 4
QR(Cat.ilj 0.875 0.568 0.242 0.175
S 0 0.300 0 0.098
T 0.286 1.580 O.137 0.127
Total 1.434 2.846 0.599 0.52fi
4.0 Wetland Ratings
The study area contains nine wetlands impacted by the current design. Using scores from the
Washington State Wetland Rating System(Hruby 2004)the project will impact eight Category
III wetlands and one Category UII wetland(Table 2).Wetland rating forms with aerial photos
used for detennining ratings and wetland photos can be found in Appendices 3 and 4
respectively.
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Strander BoulevarcJ Extension and Union Pacfic Railroad Realignment Phase 1,Segments ZA and 2B I
Table 2.Project Wetland Classification and Jurlsdiction.
Ecology Classification
Water Size
Cowardin �� Quality Hydrologic Habihat Totel Ecology Buffer (approx.
Wetland Ciassffication 7ype Score Score Score Score Category Jurisdiction (ft) sq ftj ,
A PEM D 20 24 5 49 I!I 7ukwila 50 2,467
C PSS D 14 20 13 47 I!I Tukwila 80 67,870
D PSS D 16 24 8 48 III Tukwila 50 3,546
E PSS Q 20 20 9 49 !II Tukwila 50 1,500
H PEM D 20 20 4 44 !II Tukwila 50 499
, .,.
M PEM D 24 20 6 50 Ill Tukwila 50 5,i10
._._._.._. .._..._.R . PFO D 16 20 7 43 --:--- III - -Tukwila 50 622
45,000/
QR PSS/PFO D 22 20 16 58 I/il Tukwila i00 1,044,000
S PEM D 20 20 6 46 III Tukwila 50 6,428
T PEM D 18 16 11 45 IIl Tukwila 50 21,831
The hydrogeomorphic(HGl1�classification of all wetlands impacted by the Project azea is
considered to be depressional,which means that the unit is in a topographic depression in which
water ponds or is saturated to the surface at some time during the yeaz, and any outlet,if present,
is higher than the interior of the wetland{Hruby 2004).
Project wetlands have potential to improve water quality and reduce flooding and stream
degradation. The opportunity to improve water quality is provided by the presence of pollutant
sources in the close proximity or upslope of these wetlands. Pollutant sources include ra.ikoad
tracks and recrea.tional paved trails (i.e. Interurban Trail). Water quality is improved when
wetlands trap pollutants and is a function of outlet type,vegetation density, and azea of seasonal
inundation within the wetland. Hydrologic functions aze provided when these wetlands store
excessive or erosive flows that may damage roadways or properties downstream. The potential
to perform hydrologic functions is provided by the chazacteristics of the outlets,wetland size,
and the amount of live flood storage provided. Field observations indicate that much of the
study area below the toe of fill for the railroad tracks is seasonaliy inundated. Additionally,
frequent flooding of the Green River and Springbrook Creek provi.de greater opportunity for
wetlands in the study area to provide functions that may mitigate the peak flows and reduce the
severity of flood events.
In general,the wetlands impacted by the project demonstrate a low level of habitat function.
Using the Washington State Wetland Rating System,no wetlands scored above 16 for habitat.
These wetlands generally have a moderate vegetation structure(five to nineteen species of
plants),but disturbed buffers limit vegetated connections to other wetlands in the azea. Overall,
these characteristics allow for a moderate number of habitat niches, low access to the wetland,
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Wetiand Technical Memorandum Page 3
Strander Boulevard Extension and Union Pacific Railroad Realignment Phase 1,5egments ZA and 2B
and low opportunities for connections to other wetlands within the greater wetland system.
However,the presence of large downed woody debris and persistent thin-stemmed vegetarion in
areas subject to inundation are indications of adequate habitat for amplu�bians.
4.1 Wetlands H, M, P, and S
These isolated wetlands do not appeaz to fall under the jurisdiction of the U.S.Army Corps of
Engineers (Corps)through Section 404 of the Clean Water Act. However,the Corps has the
ultimate authority in making Section 404 jurisdictional determinations. No other wetlands
within the proposed Project alignment were determ.i.ned to be isolated.
� These cvetlands were rated as Category III following Ecology's rating s3�stein(Hruby, 2004}.Tl�e
,_.. . ..
_ .
--- -�- -fim fi�nction-of these wetlands is water i un rovement and h ci�olo a�stora �
� �3',. ��tY � P Y S� �= .. ._
Railroad and automobile activities upslope make available pollutants that provide the
opportunitq for water quality improvement. All of these wetlands are densely vegetated and
have the ability to filter sediments, enhancing their ability to trap pollutants.
These wetlands are also hydrologically isolated.Any stormwater flowing into them is trapped
and does not contxibute to downstream floodi.ng.
4.2 Wetlands A, C, D, and E
Wetlands A, C,D, and E aze located between the UPRR tracks and the Interurban Trail. These
wetlands were rated as Category III following Ecology's rating system(Hruby 2004}.Wetlands
A, C,D, and E are scrub/shrub with predominant species including Pacific willow and red-osier
dogwood.
These wetlands have a close prolcimity to the Green River. Soils and hydrology indicate that a
hydrologic connection was once present tlarough a sur£ace waxer connection to the river despite
the presence of a constructed berm,roadway,and trail between the two resources (DEA 2004).
The primary function of these wetlands is water quality improvement and hydrologic starage.
Railroad and recreational activities upslope make available pollutants that provide the
opporn�nity for water quality i.mprovement. Wetlands A, C,D, and E are moderately vegetated
and have the ability to trap sediments.
Field observations indicate that Wetlands A,D, and E are inundated during the wet season and
dry during the summer months. Wetland C is inundated year round but has a significant area of
seasonal inundation.This characteristic facilitates the process of denitrification, which removes
nitrogen fram the system by releasing it as Nitrogen gas. Wetlands A, C,D, and E have the
opportunity and potential to reduce concentrations of sediment,phosphorus, and nitrogen within
the waters that it receives.
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Strander Boulevard Extension and Union Pacific Railroad Realignment Phase 1,Segments 2A and 2B
These wetlands have no surface water connection to the Cneen River and are hydrologically
isolated.Any stormwater flowing into them is trapped and does not contribute to downstream
floodi.ng.
Wetland C provides wildlife habitat functions related to the complex vegetation structure,which
contains scrub/shrub and emergent vegetation. This type of vertical structure is a characteristic
that increases habitat comple�ty and niches (Hruby 2004). Additionally,Wetland C is in close
proximity to Wetland QR These characteristics can provide appropriate habitat for wetland-
dependant and wetland-associated species a.nd indicates greater opporiunity for species dispersal
and foraging(Hruby 2404).
4.3 Wetland QR .. .
Wetland QR is located beiween the BNSF and UPRR tracks. This almost 25-acre wettand spans
the distance between the UPRR and BNSF tracks for approximately 0.80 mile.This wetland is
characterized by a mature forested component dominated by cottonwQod and a scrub/shiub
component dominated by willow species and red osier dogwood. The forested component
contains approximately 45,000 square feet of mature cottonwood stands along the east edge of
the UPRR track. Standing water and reed canarygrass along the railroad tracks comgrise the
edges of Wetland QR
Using the Ecology wetland rating system(Hruby 2004),Wetland QR scored as a Category II(i.e.
58 points). However,the mature forested component is a special characteristic of Wetland QR
that automatically makes that component a Category I wetland(�iniby 2004). The mature
forested portion is mostly black cottonwood(Populus trichocarpa)measuring 2Q to 60 inches
diameter at breast height
The scrub/shrub portion of Wetland QR is Category II.Therefore, following Ecology's wetland
guidelines system(Hruby 2004),Wetland QR is a Category UII wetland.
Wetland QR is connected to Wetland B by a 36-inch culvert under the UPRR tracks.Wetland B
is hydrologically connected to Wetland C.Wetland B is not impacted by this Project.A 36-inch
culvert at the north end of Wetland QR undez the BNSF track connects Wetland R to the
�' _ _ _ _ _ _ _ Q _ _
Springbmok Creek basin on the east.
This wetland provides water quality improvement,hydrologic storage, and wildlife habitat.
Railroad and recreational activities upslope make available pollutants that provide the
opportunity for water quality improvement. Wetland QR is a densely vegetated wetland that has
the ability to filter sediments, enhancing the ability to trap pollutants.
Wetland QR is inundated.year round and has a significant area of seasonal inundation. This
characteristic facilitates the process of denitrification,which removes nitrogen from the system
�
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Wetland Technical Memorandum Page 5
� Strander Boulevard Extension and Union Pacfic Railroad Realignment Phase 1,Segmertts 2A and 2B
(
�
by releasing it as nitrogen gas. Wetland QR has the opportunity and potential ta reduce
concentrations of sediment,phosphorus, and nitrogen within the waters that it receives.
Wetland QR provides wildlife habitat functions related to the complex vegetatian structure,
which contains farested, scrub/shrub,and emergent vegetation. This type of vertical structure is
a characteristic that increases habitat complexity and niches{Hruby 2004). Additionally,
Wetland QR has a mature forested component. These characteristics can provide appropriate
habitat for wetland-dependant and wetland-associated species and indicates greater opportunity
for species dispersal and foraging(Hruby 2004).
4.4 Wetland T
Wetiand T is a linear ditch feature located along the west edge of the BNSF track. Tlae shape; -
location, and concrete outlet struchzre indicate that the we�land was likely developed as part of a
storrnwater management facility. Standing water was present throughout the wetland, as well as
a diverse number of emergent obligate wetland plants.The concrete outlet structure is
approximately 12 inches and is located under the BNSF track at the northem end of the project.
T'he primary function of this wetland is water quality improvement. Railroad,residentiai roads,
and reereational activities upslope make available pollutants t11at provide the opport�znity for
water quality improvement. Wetland T is a densely vegetated wetland that has the ability to filter
sediments;enhancing the ability to trap pollutants.
i Wetland T is inundated seasonally. This characteristic facilitates the pracess of denitrification,
which removes nitrogen from the system by releasing it as nitrogen gas. Wetland T has the
opportunity and potential to reduce concentrations of sediment,phospborus, and nitrogen within
the waters that it receives.
Wetland T provides minimal wildlife habitat functions related to the emergent vegetation. This
characteristic can provide appropriate habitat for wetland-dependant and wetland-associated
species.
_ _ 4.5 Mitigation. Banking .
It is anticipated that the direct wetland impacts of the Project will be mitigated for in the
Springbrook Creek Wetland and Habitat Mitigation Bank(Springbrook Bank), which is operated
and maintained by WSDOT and t11e City of Renton. The Springbrook Bank was established to
provide advanced compensatory mitigation for highway projects within the Lower Green and
Cedar River Basins(WRIA 8 an 9). The bank is located just east of the study area. See the
Mitigation Plan for more details (DEA 2007).
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Strandar Boulavard Extension and Union Paafic Railroad Realignment Phase 1,Segments 2A and 2B
5.0 Sumrnary
In sumuiary,this technical memorandum complements the Wetlands Technical Discipline
Report, Strander Boulevard Extension(DEA 2004).The current proj ect description includes the
UPRR relocation,an overpass of the UPRR and related stormwater facilities, aud a bridge over
South Longacres Way.
The Project will impact nine wetlands for a total of 1.56 acres. The Project will also permanently
impact 3.09 acres of wetland buffer.
' Using the Ecology rating system(Hruby 2004), all of the wetlands are Category III wetlands,
with the exceprion of Wetiand QR which has a Category UII rating.The Category I portion is a
� one-acre stand of mature black cottonwood.The rest of the wetland, approximately 24 acres,is.a
Category II.
We propose to mitigate for direct impacts to wetlands by using the Springbrook Bank.The
Springbrook Bank was es#ablished to provide advanced compensatory mitigation for highway
projects within the Lower Green and Cedaar River Basins.
j , 6.0 References
�
David Evans and Associates,Inc.(DEA).2004.
. 2007.
Hruby. 2�4.
I . _ _
� �
�
�
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Strender Boulevard Extansion and Union Pacific Railroad Realignment Phase 1,Segments 2A and 2B
Widener & Associates Transportatiun �F En� ir�,ninrntal Plannin_
i(IIOS :�„a;���1�. �'uirr D_ f:�rrcrt.�� 1 9.�_'tl.: iiI (;.�i:.i� ;i,.c; F;j� {-!�^� . . �
September 8, 2010
Moira Carr Bradshaw
Senior Planner, Department of Community Development
City of Tukwila
6300 Southcenter Boule�-ard Suite 100
Tukwila, WA 98188
Strander Boulevard/Sound Transit Site
City of Tuk�vila, VVashington
Dear Ms. Bradshaw:
I am writing in response to your letter dated June 30, 2010 requesting further information for the
Strander Boulevard and Sound Transit Commuter Station application. Included below are the
items requested followed by our responses. In addition, since the application was submitted.
there have been alterations to the Strander Boulevard project which have altered the wetland
impact locations and quantity. See Table 1 for revised impacts. The attached Strander Boulevard
site plan, Figure W-1, shows all wetland impacts created by the Strander Boulevard project as
well as the Sound Transit Commuter Station. The Sound Transit Commuter Station layout is
included as a separate plan sheet in order to show adequate detail.
Table 1. Summan-of wetland cate ories,size,im acts, mitiQation ratios,and ro osed miti�ation acrea e.
Wetland Ecology �'�'etland Area Permanent Im acts Springbrook Miti ation
Name Cate orv (acres (acres Ratio acres)
O III O.a3 0.03 0.85 0.026
Q/R II 25 1.156 1 1.156
Total 25.03 1.186 1.182
Wetlands O and Q!R will have a total of 1.186 acres of permanent impacts which will be
mitigated for at the Springbrook Creek Habitat and Wetlands Mitigation Bank. One credit at the
Springbrook Bank compensates for the replacement of one acre of Category II wetland, as
dictated by the Mitigation Bank Instrument. The 1.182 credits necessary for the wetland
mitigation ratios shown above have been approved from the Springbrook Mitigation Banl:.
Due to the shoofly locations for the Union Pacific Railroad and Burlington Northern-Santa Fe
tracks, impacts have increased to wetland Q/R and impacts will now occur to all of wetland O.
not only the wetland O buffer. As it was previously proposed to mitigate for all of wetland O,
the mitigation credits of 0.026 have not been altered. Wetland Q/R mitigation credits have
increased to 1.156 acres. The entire area of wetlands N, P, and S will be impacted: ho��ever
these have been pre�iously deteiznined to be non-jurisdictional by the City of T'uk���ila.
Wetland Q/R will also have 1.697 acres of peimanent buffer impacts. Buffer impacts to Wetland
O will be 0.45 acres. When mitigation credit is purchased, any associated buffer impacts are
automatically mitigated for because the Springbrook site contains 12.55 acres of non-credit
generating wetland buffer. The purchase of wetland impact mitigation credit also includes the
purchase of surrounding buffer.
Requested lntoi7iiation
1. If the application is intended to mitigate for the Strander Boulevard Extension project,
then please explain the impacts to Wetland A and clarify whether tax parce12523049023
is included in this application.
Response: Wetland A will not be impacted by project activities. All
buffer areas north of wetland A which w�ill be impacted by proposed road
construction are within the maintained gravel access road as well as the fill
slope for this road and the railroad tracks. As these areas have been
previously disturbed and provide no beneficial buffer function to wetland
A, no mitigation has been proposed. Tax parcel 2523049023 is included in
this application for the construction of the Strander Boulevard Extension.
2. Are there wetlands C, D, E, F, G, and M?
Response: These wetlands occur in the vicinity of the project area;
however Wetlands C, D, E, F, G, and M will have no impacts.
3. Requests for wetland alterations must meet each of the criteria that follow. The criteria
are in italics. Please provide responses.
a. The alteration will not adversely affect��atef-quality:
Response: Wetland mitigation provided at the Springbrook Mitigation
Bank will provide water quality functions within the same subbasin,
replacing the function lost by the wetland impact, resulting in no adverse
impact to water quality.
b. TI�e alteration tivill not adversely affect fish, tivildlife, or their habitat:
Response: All wetland impacts occur in portions of the wetland adjacent
to the railroad embankment, which because of this disturbance as well as
the wetland's overall position between the two railroads are limited in ��I
their value for wildlife habitat. Wetland O is a very narrow depressional '�I
wetland and provides very little habitat function. Mitigation at the
Springbrook Mitigation Bank provides habitat that is connected to the
wildlife corridar provided by Springbrook Creek and is adjacent to the
project area.
c. The alter-ation til�ill not Izave ar1 adver-se affect on dr-airiage artd oy-storm tit�uter•
detention capabilities:
Response: Storm water detention facilities will be constructed to
accommodate all water from the proposed project. Wetland alteration is
located where it will not impact drainage from the remaining wetland.
d. Tlze alter-ation ti1•ill�rot lead to arnstable earth conditioi�s or create an ef-osion
hn�ar�d or contribttte to scour-i�1g actiorts:
Response: The proposed wetland alterations will fill will not create any
unstable earth conditions. Standard BMPs will be used to minimize
erosion during construction and stabilize all disturbed areas after
completion.
e. Thr ulteration tivill not be rnaterially detrifnental to uitv otlter pr-opertl�and
Response: The wetland impacts will not be detrimental to any other
property as storm water from the site will be treated in the proposed storm
���ater pond and all wetland functions will be provided at the Springbrook
bank which is adjacent to the project area.
f The alter�ation til�ill�7ot have adverse effects or� anv otl�er sensitive areas.
Response: No other sensitive areas have been identified within the project
limits or will be impacted by proposed wetland alterations.
4. On site mitigation shall be provided except where the applicant can demonstrate that one
of the following is met. Please identify which of the following is applicable to the
proposed two (or three) wetland impacts and respond accordingly.
• On site mitigation is not scientifically feasible due to problems with hydrology,
soils, waves or other factors; or
• Mitigation is not practical due to potentially adverse impact from surrounding
land uses; or
• Existing functional value created at the site of the proposed restoration are
significantly greater than lost wetland functional values; or
• Establish regional goals for flood storage flood conveyance habitat or other
wetland functions have been established and strongly justify location of
mitigation at another site. '
Response: On site mitigation was considered and deemed unfeasible for ',
the impacts to wetland O and Q/R for three of these criteria. Onsite ,
mitigation was not scientifically feasible due to the soil compaction '
created by the railroad. Soils in the area have been compacted to a depth
of 10 feet in some areas and would not provide suitable hydrologic
condirions for wetland mitigation. The surrounding land use including the
railroad embankments and proposed Sounder Transit Station would create
adverse impact to on site mitigation because the high fragmentation of the
c�orridor would provide marginal habitat value. �
Use of the Springbrook bank is environmentally preferable to on-site I!,
mitigation because it will advance mitigation at the watershed level '�i
resulting in greater net gain in ���etland function. Due to the Sprinabrook
bank's position in the landscape, it contains hydrologically connected
riverine habitat, larger patch size, and habitat connectivity to the
Springbrook Creek riparian conidor. The Springbrook bank is located
adjacent to the project area and is within the same subbasin, making it an
ideal choice.
5. A Notice of Application is required to be posted and mailed to agencies with jurisdiction
and parties of record. Please provide us with the names and addresses of any parties of
record to the Strander Boulevard DNS and a site plan that shows the Strander Boulevard
extension and the Sounder Station improvements. You may include two separate site
plans since this includes tv��o separate projects and a large area. Because the action
involves multiple properties and property owners, please ensure that the property lines,
wetlands and project improvements are clearly identified.
Response: Please see the attached site plans and contact information for Parties of I'
Record below. Figure W-1 shows the wetland impacts for Strander Boulevard as I
well as the impacts to wetlands P, S, and N, non-jurisdictional wetlands which
will be impacted for the creation of the Sound Transit Station. �',
Mike Kirkland Gust M. Erikson
MK Property Services, LLC Puget Western, Inc.
PO Box 1188 19515 N Creek Parkway ste: #310
Kent, WA 98035-1188 Bothell, WA 98011
(425)888-2993 (425)487-6567
6. Two postings of the site will be needed—One on Longacres VVay and one at Strander
Boulevard. Please follow the following link to directions far posting the site.
http://www.ci.tukwila.wa.us/dcd/apps/Si�pecHandout-12-06.pdf
As detailed in the linked directions, we would prefer for the City to coordinate the
notice sign process and will contact FastSigns when a file number for the project
is received.
Should you have any further questions, please contact me at (425) 503-3629 or at
rwidener��prodi� .y net.
Sincerely,
✓��� -�� !�' �,�
(l ,�``'=-
Ross VVidener
Widener&Associates
Enclosure: Comrnuter Station and Strander Blvd Site Plans
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Hydraulic Report
Strander Boulevard Extension Project
Cities of Renton and Tukwila, Washington
Appendix B - Plans and Details
Composite Utility Drawing
Typical Roadway Section
Typical BNSF Phase II
Pond Plan
Pond Section
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SCALE: 1=4 H !=4 Y SCALE: i=4 H i =4 V /�0 p�q�g,
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FOR ROADWAY SECTIONS G, H, &f ��,ror�o,r,T
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H iYPICAL SECTION-SW 27TH ST
SCAlE: t=4 N '. =4 V
STA'S' 21+�6 TO 23+84
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' �� 1RENCH PER M500T PA7H � � SITY; LANE UNE i SITY j
1
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CONSTRUCTION NOTES:
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1 1 W�
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� - SCAIE t -3 H i�3 Y
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' � ' 18.00' LT ' - I .tf� . 18.00�RT ( �lAAl10NS
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� cr � � � � i------------------------------------------------�--------- -i 0 z au ur�xoR� stRuc�ur�s+►a�eE u�n a�is
;, � 1-w w-�-�-�-w' w w � N.�_�; w w � ��„ W/SOUD UOS PER DETAIL 3 ON DO-6. SEE ROADWAY
$ W i� j ° f w w w w x w w w-�-w w � BApcFtlL fOR UNDEi�RAIM PIPE ZONE BEDOpJG AND
�� j I : � I � a s�Pa�w a�.ua.Porrn sEcnans ru��t,vNac�
0
� I 4I ; I o �w OETAk DRAWpIGS FOR POND OETAILS.
Ll! � 72 Lf �o lOQ LF . � � ONS'TRUCTfON �'S'L1NE o �� 9. SEE STORAI PUYP STATION ORAMNGS FOR STORhf
oL7� PEl�ORATfD I 5 PERFORATED ! OR2-�4 PUMP STAIlaN.
_ _Pvc wr�_ _ 1 � Pvc a�r� �� 1 tos� �_� I ��
�� �22-UCfl2 � PERf�tA1ED OR2-UD07
OR2-SD5 ! o'� qt2-U044 � O�Q
�� I o 18+00 4 _ ( PVC PIPE 20+90 21+00 o E 10. SEE WATER UNE EXTENSION PLAN AN6 PROFlIE
.,..z�. . :: n,,,�,.���-��ow»�.�w�.. �;«- ` � '} ORAN@IGS FOR WA1FR LINE
�.-�,�._-�..e:.....�" .. .....�....�.�.�- �
� 31 tF _ � x , v„. '
(n 12•HDPE� ( 30 lF , 0 30 LF � ]9+OD ^ � � 11. fOR flBER OPS1C$EQEIENC0�1G SEE COtISiRUCTION
_ ! � �oR�rtn �ao� oLL ��,��o ' �-sos a� � ��o�w►�n SW2TTHST � �� � ,� �� sr,�c�c�opnc Ka..oc�noH�Ers_Faa�
¢ DR2-SCi i� : PVC PIPE PERF4RA'ED i 1 154 lf �TSC PLAN AND DETAitS SEE UT DRAVYiNGS.
�"- ( 4 LF �C° � PVC PfPE j � PVC P�'E 4 lF 12�HOPE 12� H9#�E P+�C P�'E DR2-SD3 m 12't10PE F�
� PVC� I � OR2-UD03 � J = PVC PIPE ' �
,�:.>.:.,�,u.�R ,.�.,,���„�..n ,�.�..��-.- -,�.�::.s�a,,,,k_�,....,.- : - - - �-��..�
' z+,..�.,,.�,..yF.�,. ,�� �. .,�....Q...,.,�., �.m,. , . �. -�. Z _
I� ROW 105 Lf
-'� I CR2-U001 � � 150 L� � 30 lF DR2-UDO6 75 lf n J
= tY FiDPE � � �/ PERFORASED PERFORAIED DR2-iA08 PERfORA7FD DR2-UD10 i 2 �DEN01ES STORM DRAIN
V � tso� � I t - i I Pvc�Pe Pvc�a� Pvc� �c..� s�ucnx�ruu�
Q � 12'HDPE ��_:r Eo o�e ��e ..� o�a c�5 c�e--o�e o�e ose a.�a--� �Q DQt0iE5 D51G Nld�iBER
�� � j \� UP1DEftDRAfN NOTES UNDERORAIN NOTES ��
! � 69 LF 20' S1EEL CASNG �
�1 SEE DETAIL 1.DD-4 I �\ S1RUC1Utt� STA/OFF P�ES IN PiPES OUT STRUCNRE STA/QiF PfPES�1 PIPE'S Ot37 �DENOIES UNDER DRAIN
E �1 1 � I � STFtl1C1UI�NUY�R
� ro i tJ �2-�U1 STA'S' 17+50.00 8'MV IN =7.85 8'!'�iY OUT=7.85 q22-U006 STA'S' 19+00.00 8'UN IN=4.55 8� INV WT=9.53 � OENOIES OWG NlB1BER
�� 32.�5 RT 8'(NY flliT m7.85 3275'RT 8'M!V OUY=9.3,T
.� � �� - �� 1 OR2-U002 STA'S' 17+70.Q0 8'�IV IN =8.29 g INV WT e&29 ��7 SFA'S' 19+75.87 8' INV IN=1275 8' WV dUT�1275 �
� o'� �& 3.D0'RT 8'i�iY OUT=8.29 1.25 RS 1 � DENOjES PUYP SYSiEY
� � � 57RUCT1�7E PYJY�R
' � ��� ', � , r �-� STA'S" 17+70.b0 8'INY IM=7.�'i B•R�V WT�7.9fi pR2-tJD08 ��` '� 19+75,OQ B' IIY tK.1279 8'� WV�JT�1219 pQ�p�,S 6yyg��
�' - i r !_._ . 32J5 R? 8'INV kl =7.96 32.75'RT
( (� _ , � �2_� STA'S' 1&+70.00 8�MIV IN =879 8"iNV WT=879 �2_� STA 'S`20+84.Q0 8° MIV OUT=17.90 �
� �� : r � 3.D0'RT 8'MtV OUT=&79 t.25 RT i
�m
� �' I __ srn•s� �e+�aoo s• wv a� =e.as sr�'s'xo+eo.ao � ? ' � � ;1 ��.,__�
� o�-wos s'wv our=a+s oa:-w�o a'wv our=».aa =: ;
� �� ` � • )2 7 5'i t T 8'�!V I N �8.4 6 �a 3 2 7 5'R T I ` ;�f
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�;
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�
� 20 ° _� KEY PLAN
ti scale feet
� FEDAID:STPUL-1276(004) ,'� � n.w� .e..� � �w ,�,
� q� ,{ � CTTY O_. STRANDER BOULEVARD EXTENSiON �/�4/�+
� HPr-�2��(aos) �, ����-����LL�L'11V1 ""' RENT�l1 PtiASE 1,SEGMENT2A
� CALL 48 HOURS �✓ �`3 � �',,,x v�wk„wrxs o��o,,m,�t "'
BEFORE YOU DIG 3"°1�''"'"�x'�5°`w',5"ee 3°° � 'A'� �` � -'�a. °ATtJL �v.°"°° F°'°°"'°"'et�'^ DRAINtAGE PI.AN
. � DR-2
ai a SNEET 2
Federat Wa�t,'Neshatatm s800(3-2600 �yAt R``� ...os .e,i�m..v BS z2r
A 1-800-424-5555 {206)431'2300 F�c(206}�31-225D �. �5� � d`� '�R ,;56 QoGert �1. Hanson P.E. Oate
� i
NE 1/4, SEC 25, T 23 N, R 4 E, W.M.
0
�
o� NOTES:
T ( �. sg s��s c,� a c7 Faa�c� ��nars
r - _ ... _ allo c�¢xu Nor�s.
� , _ _ ._.. _ _.__ ,.
_ :. ___ _,. _ _ ;
� .. , - ,� % `-.,.._ _. ,_ . _... ___ __..._ .. .... _ _ ,.__.. _.__�. � PER W�OT S1D� 8�10-� LOCKNG�E
. _. : _. ._
�.
� ;:. _.... _--. .._ . . . ._.._ __....._ _...._ � ..___ ....._.. _._... �. �- .- .w _ .___. --. . . _
. ...._ .. :.
.:: ..
__
_ _..__. .
__ ... .___ ,
_.....,
,. , COMPOSI
� _.. _ :-. ._ ...._..._. _ , ,. U�1t.1TSE5.
- ; .,_
..__....
I .__..... � - ; .... _. .. .. ..-._..�_ ---.,.._
g � .. ... __. __ . �-- . .. .
_ ._ .,_.
L _a' ,..._ ,__. . ,.. .-- - 4. I�UZATION Pl.ANS FOR CH/VfP1E1.fZAT10N k
--:_._._
� :' `-, --._..,.. _.. . .. ... _. . ..._ ._ . ,. _,_ _._. 51(�ING.
;: _
. ... _.... -- _
-_ .
� - _. �._ ' -
_ .... ._
. . _ .__._.__
� ..._ :,: _ _
"__ .. ..._ ', S. SEE DRAINACE PROFlLE StiiEE1S FOR PoAt @..EVATIONS.
�i � ,_: _ _.
.. �.__ .__..�....
; ____.... PIPE(NVERTS, SiRUCTURE TYPE. P�E NATERiAL AND
_. .-. . - . , ::w --
_... . _._..
� 1 - _ -_ _: STAil01JING.
_._.
. _. ... ,, ...
�° ._ __ - YANED GRAtES
. .__ _ _ .
_..__.
` _ _ 6. ALL CATCH BASWS SHALL HAVE
. ,..
� N _ _ . . _ . UN3FSS Oh1FRWlSE SPEpFiED.
� Q I-----------------------------ROW ------------------------ --`-''�---�— 7. ALL UNOERORMN STRUCiURES N1LL BE AREA IMEiS
� ( ___` W/SOLID L.�S PER DETAI�.3 ON DD-&. SEE ROADWAY
w SECAONS�OR UNDERORAN PPE ZONE BEDOING AND
� _: ` �-
_ ,_____ BACKFlLL
W : ` ..
. _ ___..._. . .:_ ..
� - - & SEE POND PLAN. POND SECTIONS ANU DRAfNAGE
� DETAfL DRANINGS fOR P�ID DET+tILS.
W � w w w w w w w w w
� ONSTRl7CT10N rt•s•ur�E S�27Ty gT 9. SEE SFORiJ PUMP STAIS�N ORAN�iG,S FOR STORA{
�� 25+00
�.. PUI� STAIWN.
p 26+00
�� 22+00 23+OQ 24+00 10. SEE V�ATER IJNE EXTEN9�1 PIAN ANO PROFlLE
�.. DRAMANGS FOR WATER UNE
N
= _..._
= DR3-SD3 _
fn
Q SW ZTTH ST , 12' HOPE - . _ ; _ ,: __
� f DR3-SD1
� �-. .,.:..,._
? �x sa ac:� � � � s�.�:� �:� � sn � s.� � ry � �:� �:ra �:�a:s�:a�:s3 ss �:se.�_,�:� �:�a ,,' " . ,.- -
� ------------s---------------- ROW ---------^-- a� `
----- ----�------ --------
= SEE DEMOLITiIXV PLANS +3R3-502 �� -. � _ DENOlES STORN ORAIN
1—i \� y1 : ~ --=a�� DENO S D11�NUNBER
� �� y '���r
� \� � i�//
� Q
I �l � �/
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i_ Z �
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t !3
1 ( Ja
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s. �
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� ' �i� .�.__--'��—�.—
� ; i,�,;4_—.
� 2o a zc +a KEY FLAN
ct,�
Kma r�c
`9.C%«, CITY C'F STRANDER BOULEVARD EXTENSION �/t+/+�
� f'EOWD:SfPUL—t Y76(004) ,C� ��d �� `t� � �Ye
H�r-iz�e(°as) �� '���.�fj���Q.T�A M "�s RENTON PHASE 1,SEGMENT 2A ,,,�
a CALL 48 HOURS �.� '-� � ►t�C� �
� BEFORE YOU DIG �01�n'"'�'xso�,n'.swee3°° '�`�'��.� �c .�-E DA7U� "���r°`co°�0"`o-`�'��°" QFWNAGEPl1W DR-3
„ rmc�wer,w�,:,qron��zsao •e•••a
; 1�00-424-5555 tz��a3�.�o �x;zo��a3�-uw "L� ra. � ar on� �aPa � a.,�.., RobM A4, Hanson p,E, ' Cota SHEET 3 e� zz,
o NOTES:
d
p t. 57�tM ORAA�t �t�t1�£FtTs ARE uEASURED FROAi C£NiER �'
�i STRUCTURE
T 18 , .. .. 40 2 +�LL FRpYES ANO UDS 9�A1�BE OF IOCKMG TYPE PQ2
� . .. ;.. : : . i wS00T STD PWi 8-30.10-00.
_ , � :
1
; 3. C8 TYPE 1 PER M5DOT STD PLAN B-520-OQ.
, : � _ '
< El4STiNG(�tADE ,
-fi : � : ,f-- -.---- �-.: : ; _:
, .
.
, ,
. ....
30 _,. .. _ . . , . . . . 4. CB T1PE 2 PER k5U0T STD PIAN 8-10.20-00.
.._.. . , ,. ... . . ... . s�.. . r .
i �
{Ntl-SDI, CB iYPE 1 �_ t _ .:�. _'..___-} �; : ,
--- + ---- ----
w �tlVE GRATE 1- . �: -� ��_ � Y � - .. ` . . { 5. N.L cAT(}� BAS�JS SHALL HA4E vANED 6RATES UNIESs
: :
.-'
�, A 'S' r5+91.T0(24.9' Rn :::..+ .:_ �:... ''.' : � :. . . : . --- -- -= -- - - �� _- on�ws�sa�a�n.
� -�� �-- . . � - .
� 20 RI►t' 8.88 �POSED CRADE STA 'S' 17+96.00(29.5'Rl'j .. .. . i .. " :: 20 5. VANEO GRAiES PER N5607 S7D PLAN B-70.30-DO
a IE(E) = 6.10{12'HOPf} 0 Cf11TERIJNE `5'L�iF , IE =5.22 SU 'S" 18+65.00(29.1'RT} : ,.
.
� .. ,
� 11 LF 0 8.93x : ' � i � .: j IE= 5.82 7. C0118RIATfON Ni1ET PQt WSOOT S1D PLAt1 8�-25.�
:: � . i
{
� �p 12' NOi'E ' 8. IXVE BEDDING APD BACKFlLL FOR
; 1 P�'ES2PfR M1�00T SR)PLAN 8-55.20-OD.
�' � _.7 ': �:... 15U LE O 4-� D
� ' . -- : }Z 4iDPE �: 9. BEE}iIVE GRhTES SHALL BE OLY#IPIC FOlR�F7RY WC PM1 NQ
L � { .. 118 LF O 1.02X 150 lF O Q.87Z '.'. b9 lf 0 0.87x 91608H OR EQUIYAIFNT.
o, DR1-SD�. CB TYPE 2- 5{' 12'H�PE ,.... t2•HDPE : 20' SiEFl CASRiG � . . . a ::: : t . . ; _
0 ..
� W/CdYBINAl10N MQET � ; . � 10. SOUO LiDS AT CATCH 9AS�1 T1PE 1 SiRUC1UHES PFR
c.� - OR2-SOt. C8 TYPE 1 i . : . f�' WSaOT SiU PlAN 8-30.20-00.
�. . STA'S' 16+Qi.53{27.9'R1} , , :: OR2-SD2.C8 TYPE 1
� . RIM = 9.58 � STA'S' 17+50.OD(29.1' R1}
� f�l = 10.21 �' - S'A 'S� iS+0Q00(29.1'R� � � Z
iE t�) = s.so(�i�Hor�l . wM= n.sa
_..... �. ,
. .. . . ... . {..._..... . " -.. .�. .1. .. '- ,�
-�a �(N) � 3.es(�z NDPE(FUTURE PHASEa) :' : :. . IE(E) _ �.n (is'�) _
. �
IE(N)s 6.d8(12'HDPE) .:. :: - -
tE(Yl�= 250(24' HDPE{FUTURE PHASE)) :':: ::
:..
�(s) - zo� e � �tE aa���� � ._ �
� f�= 6.00(i2'►� . - ( ' ) . " ooro�s sr� oRur
. d �(� � ao� iz-� � ..:::�: � � �(s)- a�s(e•Pac� : , srnucrur� r��x
__ �(s} . �.so{za•�) � :: .: � :.. . � � , �{w}_a4� (�2'Hoa� � � - _
.. : -� OENOIES OWG rNJMBER
-2a �
PROFiLE
scxF: ,•=�o�(fwwzf, r=�a�(�xn �-o�rw�s u►ro�o�,+m
SfFtUCi11RE NUMBER
DEN01E5 DriG!AlYBER
�0 � _ _ , _. 40 w � � _. � -
j :: � , ..
... . . � .. i � ;::. ,. . . ... . , . , . .... ... .. .. _..
. ._ . . . . . .. .��..�. . ... . .. . .. ..
I i PROPOSED GRADE � OENOTES DwC NUYBER
.
- i
(
. i
1': O CENiERUNE"S"tJNE �
_ . . . .... . . _ .
� _. _ ,. � - �o �o �xisnNc c�a� �o �o . .w
_�EpSi1NG GRA� � I _
; 1 __�� --- GRADE � PRQPOSED GRAOE
, : _� -----= - _ ..: ----- -------- ----- �j. --- . �c�,�turrE•s ta�
�aszwc
. �
---------
'______r""_' i� . . ...
_.,. .. ;.. . . .. .. . ..:... . .. ........ . _� ' ' '
20 . : . , _ .. 20 � :... PROPOSED GRAEIE Zo 20 � �n
150 lf O 3.98x : -
! � -
o c��r�rve r t� . �
I. ::: . ,r►+oa� oRz vom �
oRz uoas
p �. .. : .. .. .. .. .. . . ... .. :. 3�. . .. . .-.:. . ..... .;i .... . ..... � � �: .. _ . ....
$ �fl .. .. I ... .. ..._ . ... . ... . : 10 18 � 10 10 , . .. .. �' 10
�' � .:: � :: ': oRs-so�, ce �� � �: : uNoa�a� coNr�cna� 3� �e a5cx -
, srA's' �+aaoo(2�.�'e� o o. ��_2 12.� No�aa� carwEc�
u
� . oRz-s�a.ce rvs�� .. . .: s,ir►+o� �or�2-saz ce rn�i
� = ze.s2
D - - STA�S�20+SD.DO(29.1'R� . . IE � p u � . o STA"S" 19+CQ.0�(29.1'RT}
. (y� 21 13(12 HD7E)
"'� RIY = 1&24 : S '- . DR2-SOI. CB TYPE 1 RW = 11.96
� n IE(E) y 15.16(12'HDPE} . � � : STA �S' 31+50.00(19.1'RTj �(£) = 8.30(12' F�PE}
� _ �(W}= 14.75(12'HDPE} � ( ' DR2-SDS C8 Tl'PE 1 RHi =10.21 _ � IE{N) - 7.55 12"HDP�
$ r' � -- .._..' . . .. , ... . -10 -�0 4M1H SOL10 LOCKRIG tD -�o IE{Ej= 5.11 {12' HtWE)) -�a �S(:LID LOCK97G UD _fp �(5) = 8.88{8'PVC)
�# � :.� , STA 'S� 17+50.00(2.0' L� iE N = &68(72'}IOPE STA'S' 19+00.00 (20' t� W) = 5.41 (1Y kiDPE)
- .....
2 m I ' . I : f� = 11.54 IE = 7.fl1 "PNC ib - 13.32
� . . ; �. ; :. : . �(s)=s.84(�2'�) �(�j� s.a� (iz•►�) ie(s) _ �.n (is'►+o�l
� _� .. :: : - �: . ; �
, .::: _� , . -.
3
� PROFILE
� sca�: �•a2o'�No�az), �-=io�(+��j
LL PROFlLE PROFILE
� scat�: �'=2a'(Ho�az�, t'=�o'{�r�su t�+so scu�: �•=za'(HOR+z), �•=�o�(v��sr� �s+oa
� (STA 17+50-t�lEj (STA 19+�-UNf)
R
20 D 20 40
�
� G scade feet
7
,� �°'��-t27�0°�� A p ��y �� � '� di��°� CITY C'F STRANDER BOULEVARD EXTENSION �/�+/>>
H�-iz�scoos) �� � '� �'�"1`!1.Ut�M �'
� ��' as s�m
b CALL 48 H�URS �./ v "" RENTQN PHASE 1,SEGMEtYr2A
� BEFORE YOU DIG 3301�''""�"'°��'0C � � �- .I-q,�-I �'�' �k� ��� ~DP-1
,�p�o�ee Fa Co��tn�t;a+ DWIINAC�PROFILE
� 1-80Q-424-555� c:�3��-z'���r-�aos)�i i��sa , `x,"�.� no. �a+ s. ;,�� Aara �- :•:,�:� . SHEET 1
,rsc Raber} At. Hamon P.E Gote 88 227
0
a.
� �
� NOTES:
� � r. srat:►e o�u+e���u�s�mm�roa ��x aF
, _ .... ; _ +0 40 . _ ... +o srnucnra�.
_.. , _.......,.
�R1-SD3.CB SYPE 2 - 54' :
EXISIING GRAOE i 2. ALL f�iAYES AND l�5 S}i111 BE OF COC7aNG TYPE PER
STA'S� 16+01.11 (39.9' Rn 17 LF 0 0.50x �
. Rf�l +� 1f.67 ' ' . ,_ OOSTRIG GRl10E 1YSDOT STO PLAN B-30.10-00.
tY koPE
� 30 �tM)- i.so(z+•t�) --- �_ �a �o �_°PO�D �ADE + ;: _ � 3. CB TYPE i PER Y�OT SiD PLAN 8-5.20-00.
�(E)= 6.33{B"PYC) ,
- . �(s�_ -o.�o(�s•�(To ruMa sratwri}� _
.. 4. CB TYPE 2 PER MISDOT SiD PLAM B 10.2Q-00.
� , � � ' _ _ 5. HAYE YMIED CRATES UNtESS
.. __. _ _
� i.
. � r ( ALL CATp1 BASINS SHMI
zo a�zoaos�o cRaoE _ ,. _ 2o zo _. i : ::. 20 on��mwse s�c�En.
� ,
� : j i I OR3-SD2. CB TYPE 1 � � 6. YMIfD GRATES PER WS00T STD PLhV 8-30.36-00
sr,►'s'z��.00(�s.i'�r} oRs-sn�, ca iraE s - �a• ��as�c}
t0 , 10 10 � ' �.79 S7A"5'24+48.15({25 RT} ja 7. COM�IA110N �ILET PER WSDOT STD PLAN 8-25.2Q-00
� :. �(N} = 24.03(12'HOPEJ RAJ : 28,49
� I I � � �F1E.0 �At� AD,AIST 8. PPE ZONE�liG AND BAp(FILL FO(t STOR1i�WER A1PES
_ .:: PER WSUOT STU PLAN 8-55.20-00.
� '
1 � (s)= 2a.�(�2'sa{Ewsnr+c)}
p OR1-SD2.CB TYPE 2 - 54�
. 0 0 � IE (5) = 21.95(tY HOPE} 0 9. BF�}N�E GRAiES SHAi.I BE OL1'LIPIC FOUNDRY�IC PAR7 NO
� W/�iAli(��1 NLET IE (Ej 2345(i8' D.I. SD{E�STING)) �511608H OR EOUIVAIFNT.
SfA'S' ifi+0i.53(27.9'R'n ' '
R�i = 9.SQ i .::: ' .. '-: i .. - ! .� ;':: i 10. 501.10 UDS AT CATCH BA4N TYPE t STRtJCTURES PER YY500T
IE{E}=3.50(72'NOPEy 12 tf 0 0.83X ' . . _
-10' IE(N)= 5.86 (12�HDPE(FU?URE PH+15�) 2�•HCPE -70 -10 -fD STD PLAN B JG.2Q-OD.
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PROFILE PROFILE
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FR061 PUIlA STATION � ,
SfiE PU1� STATlON A1J�NS . I , i 1
� -- �---�-: ' ' PROPOSED GRAOE �' :.�::.':'' E105'FMIG GRADE 40 I.F 0�.50X
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,�� 3p . . :._ _ .. . O STORM PONC 30 30 :.: �. . 30
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1 HDPE W �E11D
_. _.
� STA 'P' 16+76.94 �- `-- * -_--
� � ' - .---- -
�. ' 29.57 RT `
.' STA 'P" 1Q+31.56
2D ., --- rt----- --- � . 50 Lf 0 4.ppX , . 20 20 !E = 23.90 . � 20
^ I:. i ' _ 24,D� � : STA 'P' 13+49.59 � �. .. 38.85'RT �
$ PS2 YH3.QISCF{ARGE NtiVHOIE- 54• �:: 19.69' LT PROPOSED GRAOE ; I .. (E = 23.8(t
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� : ;: . :::: ��S) = 24.00(18' HDPE}
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PROFILE �
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" PROFILE
R $CAI.E i'=20'(HORIZ). 1'=10"(VFAT)
� 20 0 20 �0
� � ecde feet
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m r�-�z��(oosl �1 ���,��.��,1��Q A x,{ � RENTt)N PHASE t,SEGMENT2A „�
�' CALL 48 HOURS �/ � ��nivl �
� �
33301 9fh Avenu[SaAh.Sube 30Q ��.u`r �p ""' ONTUA{ �wsd for Coostnr:tlrn
BEFORE YOU DIG �� � I-�---� w� DFUtiiNAGE PROF��E DP-2
r-eera war,we�,yo�,veaa�•zsoo . g,�o 4 � �..�.d
� 1-800-424-5555 (2(?6)�31-1''00 F�c(206j 431'225tl �� H0, RFRSION BY OpTE ApPR � ��• Robert 4. F�artean P.E � SHEET 2 89 227
NE 1/4, SEC: 25, T 23 N, R 4 E, W.M.
T . . . . . .. . - �-
� � ... . .. ........ _....... . ��
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� EXISi1NG U�DERGROUND PONER LINE
�I C - -y STORAGE TO BE RELOCAiED SEE UTILITY -- -� ` --
r _ ALIiY RELOCATION PLAN � �
STA �P" 10+33.60 �b-2 - `�-_--
66.40' LT VOLUME
CELL 2 = 35.41 S CF - ,. ``--
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j � . . � I . �.Y� . � .i� �-��YC{��T. .
d "%;� STA �P" 11+91.B2 K r��Y�,�x � '�tti"�^~M����j�~�� � -e• :
a+ PONO OVERFLOW A I `�t+-�.t, ,n.� �� .." J
z / 79.41' LT S� �. '�":_ r-.�- .r'...� . --�--
N SPILLWAY SEE DD-3 � � P _ t _ - y 5=��� � .t" r. �-
� �, ONp Mq�NTEN !X �F��_ � �: �r�--- �
q�yC ��x \,'; ,:. ; �-
� �==---___ �-
� ' � . ---__ ER� INSTALL l CK V1Nlf� COATED TYPE 3 FENCE '� ��'x �-`'� � ? ACCESS RD ��
a STA"P' 10+21.80 % / � �-__ �'ti , -�" i I /�
i -_ � f PER WSDOT STANOARD PLAN L-20.10-00, TYP �2^
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a0 i i ry . . _t-� �
/
� 10+pp k� � � �� w} � `{2 �'
7-'�- ,-t,: - STA "PA' 1+42.79 s `}'�''�'.� \\ \'•
� i / .� � ; r INSTALL BL�iCK NNYL COATED TYPE�
m � ' STA �P" 11+00 � � 79.22' LT *:r ', 1 1
' r �� ' R=28.2d 28.20' LT ' "'_�� �`�� .�t-. fENCE PER WSDOT STANDARD PLAN 1 I� 1
Q, � � � � � q� �-. \\�� �. � STA 'P" 12+45.98 L-30.10-4C, TYP 'J, ��
Q I �I � I � ��+� ��,��� � 34.50' LT STA �PA' 1+99J9 ��
� STA "P' 10+29.80 � I�� � I CELL 2 STA 'P' 11+60 \�\`\ a 79.22' LT � /
31.39� RT �� � � 1�',�, �� 28.20' U ������ STA 'P' 12+61.25 � �
� � \�, 1 STA �P' 11+00 34.50' LT X x ��' -
♦ I / j
IE(OUT)= 23.5 �� \ 28.20' RT X
R=128.20' \� � STA "P" 12+64.38
�� '' � STA 'P" 11+60 ��" z �� � � 50.40' LT � � �
i���� 28.20'RT �STA 'P" 12+40.1J ���� � � �, x ' �/� � �
\ �'� � � 28.20' LT 1 � �
, , �� , srA "P' 12+73.46 " PUMP STATlON � ' �
� ''�.,A V �� �"� _ STA 'P" 12+40.13 ' � � � 21.20' LT � `
\�\�\ � � R=71.80� 28.20' RT �,\ ', `,�'� `� SEE STORII PUAIP � �,ri ,
N
INSTALL BIACK VINYL \.� �� \\ ' -__ \ �'' ! �NSTALL BLACK VINYL � STATION PLANS /
COATED GAlE �""\\� '�-_ \ � �' � �� COATED GATE DWBLE (10') J
� --� � � � SYr1NGING SECTIONS PER � � i �
DOUBLE (10') o � R=134.50' 1A,� F � ��. �� J
SNANqNG SECTIONS � � o� � � � `�i�j>} ti W500T STANOARO PLAN � �`� r i � � � �
PER WSDOT �' STA 'P' 12+45.98\\ � ;); �/; L-30.10-00. TYP I} �
x � /
STANDARD PLAN �_ 34.50' RT � `� ��Ir �/� x � STA 'P' 12+67.99 � I i I I � �
1-30.10-00, TYP � � . . R=65.54' � ' x p_ G I I ' �
.. ^�i � \V` + �� -?�1Ad
� ��.,A o � ��� � 76.81' LT
S T A 'P� 1 0+3 8.4 6 �.,�\'�, �� ��� I I f ' � � I �
J � f � � � i 1+00 � ?+00 2+10I
46.02' Ri + ���� \1'� '' p+00 �. i I( � I �
\ � I
STA 'P' 11+60 � �`� �1'� �� � � i �� ��, � � �
70.40' RT '�� ' ` I R=77.50� ( �?' �I 1i STA "P" 12+77.29
STA"P' 10+59.68 � � 1�1 1� � � ' - CONSTRUCTION�"P�\
68.22� RT STA 'P" 12+61.25 i � � � I I�� � � 50.40� LT x � X �� � I �; I
34.50' RT I � II! I � ' I CELL 1 0o I ; ' �I I,II � I
i STA 'P" 12+72.46 � t
- ��� � I . � o � " � 40.67' LT ': , `
STA 'P' 12+95 I � ^ i I I � x %�; X I I
70.40' RT STA 'P" 12+73.46 � STA "P' 13+20.06 � z � STA PA 1+42J9 STA'PA� 1+99.79 (
RIPRAP WTLET PROTECTION, i; I I � x STA "P' 13+22.99
WELL-GRADED 4'/-24"0 22.50' RT 11.57' lT � z i 27.78' Ri � ' �
� I I � 66.40' LT 27.78' RT I
8'W x 14'L x 2' THICK � i � � % I " �
B FLOW CONTROL � I� I �I STA "P" 13+25 � 3:1 � 2.�� �
� DD-3 SIRUCTURE SEE � II� � � , �, 22.54' LT � � I j� � � B INSTAIL BLACK VINYL COATED GATE
� ��� � TA "P' 1 +95 �� �{�� � '' \ i _ I j i ��/�; ; � � � �- DD-2 DIX16LE (10') SWINGING SECiIONS PER
l S 2 � � ' R-22.50' , / x � WSppT STANDARD PLAN L-3D.iD-00, TYP I I �
� �f �_-� � �� 22.54' RT �V'�� �����\ � � ' ;��t � STA "P" 13+26J5 � � � 1 '
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22.50� RT /� � �i �SEE DRAINAGE PROFILES AND I I I I I I I
a \� �� � �/ x RIPRAP INLET PROiECTION, STORM PUMP STATION PLANS
.
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� WELL-GRADED 4'0 -24'0 I I � i I
T ��-- -------- �''----- _ x �`-- --�� %� '�-� � �8'W x 12'L z 2� THICK
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1 STORAGE VOLUME �
Q /� `--�� WATER QUALITY � � �' `- \`�', I-_ •. - -•
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o CELL 1 20,640 CF � � �� j � i��%; �f ��
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WEST SHOOFLY �Q�, R T �- < a.r•� a^"� 1 S T A 'P' 1 3+9 5.4 0 SEE UTILITY RELOCAi10!� I ' I I
° EXISTING FlBER OPTIC LINE ^ A t ;�I PLAN FOR LOCATION Of'
� � 70.40� LT FlBER OPTIC L1NES I �
�EFO EFO BFp � DR2 '.� . . . : . . .
BFn AFr BFO gFn
SEE DD-5 FOR rt- �� e� CFn �r�
� CULVERT EX7ENSION I ,n i �B'� eF0 eF� e=o BFr
-rr-- cv ONSTRUCTION �'P'L1ME � B``'--E '�I
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1`�1�l11V1
CALL 48 HOURS �/ ' � A °""`u� ,�,o, Public wo,�s Departmtnt
BEFOREYOU DIG 333019[hAvenueSaffi,Sui�300 ° `"` a� I--.--� 0.4TUM ppproved For Construction
Federal Way.Washing[on 98003-2600 ss�o,:,L�ti` �x �,�,n, POND PLAN dD-1
1-800-424-5555 (206)431-2300 Faz;(206}431-2250 ND• REYISION BY DATE APPR J5G Robert M. Honson P.E. Date 90 227
I I
I I I I LEGEND
# i I I
` I i�J I - � NEW IMPERVIOUS AREAS
�
I I
I I U REPLACED IMPERVIOUS AREAS
a
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' WETLAND "J" � I �
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Q i - � WETLAND"N" �:_, I � WETLAND
� �� WETLAND "S" -- -� – -- - WETLAND BUFFER
WETLAND "I" I •i rI=,: �
� �
� � , ,'i � I ' PROPERTY LINES
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L . .I i
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o '� WETLAND "H" � �I � �'
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� ' 0° , PROJECT AREA �
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w THE BOX �_:� ' \ .�,
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� � WETLAND"A" � ; � NEW IMPERVIOUS AREAS \
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�' WETLAND"B" ,�-:��,� ,� ,�� - I
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If•�.-�• •�•.'.'.'.'.'.'.-.•.'.•.•.'.'• -i! BO 0 80 160
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�. . . . . . . . . . . . . . . . . . . .'. - . I_'. I scole feet
FE0.41D: �, 4�'°�4 A.cy��'z� �@ CITY OF
ic.ero.:.o°�w�.i
�� Ber�erABAM s �� Z' � RENTON "�`
�
CALL 48 HOURS �� � P � �;r ` Public wo�xs o��n�„�m -
BEFORE YOU DIG 33301 9t�Avenue Sarth,SukE 300 �', 'q,`'"F:,�i.�� o� �� DATUM ppproved For Constructan
Fe7eral Way,Washington 9R003-2600 �`st��"�c.`
1-800-424-5555 -z�5,431-2379 Fa�;(206't 431-2?SO ��'L t " �'10. REVISION � BY DATE PPPR "�`�� Robert II. Hanson P.E. pate
N
O
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I
� 15' ACCESS ROAD
EL 28A
TOP OF POND
� 28,0 VADTH VARIES
� ' 1.3' FREEBOARD 10' MIN
� EXISTING �E P�N FOR DE7AIL ON POND
GROUND EXTEND RIPRAP Y-D' MIN o MAINTENACE RDAD, SEE � 15
I
m .F ' POND BERM EMBANKMENT,
� � ABOVE TOP OF PIPE N z' DETENTION STORAGE �
t � 66,259 CF "' PIPE IE = 24.0 SEE SPECIAL PROVISIONS
� ,�_�ii��'_ r DETEN110N EL 26.7 �
� � ,7 GRWN WA R STORAG 4.0 1 /�EbSTING
¢ --
¢ POND INLET� 1� -d__CRADE
` - � ` �"�� _ �� _:�� � ��. ,_. � _'-_-_ ._, _`_�._ _���_ � � II I TI-1�II�1=T1=�11 I��=��1 IL=11�=1—'�,11=�1 il���l=1 L=1 i�-_11=,- I�.-TI�1=i I� I_I�-11i I IJIi�IJ�.� II- ���II—I�II' �' � �
_ ..... .... . ... . � — . — ... - �I—il _I��c_ _
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m BEVELEDENDPER � ,_ ..1 _ i-l-l—lu�—ii-ii i-i _�_��_ ����������— _ _: __ �_ ti�II_ I— = — — — I�I� _il-i�i=ll_'il_',i��iJl-ii6_ie'n_i,�I _ _
N5�OT ST� PLAN �� ��' �'�� � KEY IN BERM FOR �ETAIL ON FLOW CONTROL
� 1' SEDIAIENT STRUCTURE, SEE DWGS DP-2 & DD-3
L 8-70.20-00 STORAGE CEIL 2 YOLUNE
4' PIPE IE = 21.7 CELL 1 VOLUME 35,4t8 CF
0 2D.640 CF POND INTERNAL
v BOTTOM OF SLOPE 3FI:1 V, TYP
SEDIAIENT STORAGE
EL 18J � SECTION - COMBINED DETENTION &WET POND
D�-1 SCALE: 1"=20'(HORIZ) 1"=1D'(VERT)
15'
DOYrN SLOPE 2.03;
QF PONO � I ' 3
r�7;`i ,'x,. —�1
..�.;�?�';fi�: '�Y„�!2�� - � —f� _
\\
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��0.50' CRUSED SURFACING
BASE COARSE
CONSOLIDATED NATIVE MATERAILS, SEE
SPECIAL PROVISIONS
� POND MAINTENANCE ROAD
S�ALE: N.T.S.
POND BERM EMBANKNENT, PONO BERM EMBANKMENT,
15' ACCESS ROAO SEE SPECIAL PROVISIONS � SEE SPECIAL PRONSIONS
El 28.0
1.3'FREEBOARD
POND BERA1 EMBANKUENT,
_ EXISTING GROUND� EXTEND RIPRAP 1'-0" NIN ^ 15 - 15' 15' SEE SPECIAL PROVISIONS � ��
� ABOVE TOP OF PIPE ACCE55�--I 1,J' FREEBOARD ;�
j EXISTING ROA� � �;
� GRADE ;
- �r=�T ` = DETENT10N EL 26.7 - DETENTION EL 26J 1 �
, �r�i� i-, ,-�=i_ , -r- 2
' PONO INTEF2NAL _ W 7 � ` _ ' ,7 �
? SLOPE 3H:1V, TYP o = DETEN110N STORACE ', - �EXISiING GRADE 1 � _ _ ,�;�,:�
� POND INLET FROM PUNP � � � - EL 24.0 GRADE � ��r�_ ����-�r: � �L�--i DETENiION STORAGE �,,�,� _TM
_ + GROUNDWATER STORACE EXISTING i i�lt ' n
., - - CROUNDWATER STORAGE -
< STAiION, SFE DWGS DP-2 & PS-5 = -=s- �'=�-'ii � ' '� i
o I'Ir� ' � EL 24.0 �1 ��
" 1' SEDIMENT 3.4' `
VARIES STORAGE `2.0' QUARRY SPALLS,
VARIES
� BEVELED END PER WSDOT STD T�
a PLAN 8-70.20-00 CONSOLIDATED NATIVE A�ATERA�S. SEE
- BOTTOM OF SPECIAL PROV1510N5
' SEOINENT STORAGE
� EL 18.7
- a SECTION - CELL 1 ; � SECTION - CELL 2 E POND RAMP
- OD-1 SCALE: 1 =20 HDRIZ 1'=1a(VERT DR-1 SCALE: 1°=20�HORIZ 1 =10 VERT E SCALE: N.T.S.
`a
_ ��715.(;( ]
'� FEDAID:STPUL-1276(004) � � i �,c ��
HPP-1276(005J /�� � ` � �AS SHOWN �°'°�-^����a� � CIT� OF STRANDER BOULEVARD EXTENSION ��/�</>>
�� �'���`�-�AI�A1V1 � _ ""5 � REI�TOv PHASE 1,SEGMENT2A
CALL 48 HOURS �/ LN � oATUM Public wo,k5 Oepartmeiit ��
3330:3th Ave�ue Sou[h,Suite 300 ':, �4M � i
- BEFORE YOU DIG � — �� Aporoved Fo� ca�5c�,�����
Feceral Way,�vashington 98003-2600 '`s;,;," �x POND SECTIONS D D—2
1-800-424-5555 (200`;431-2300 Fax:(206)431-2250 N0. REViSION BY DATE APPR ""'�"' -
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z TOP OF POND �
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� EL = +28.p o g'
� <. +, } EIAERCENCY OVERFLOW WS = +27.5 '
�. i�'.� 3 TYP � � -a.;�-.
{ I -. � 1� �-r � i
Q OVERFLOW WS ;�, �� r">.=•__ _
. EL = +27.0 0 = ' ' . •.i . .
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m � �_l'Z �t'-0' THICK QUARRY SPAL�S
� ' �-y j' ` BEGINNING A7 INSIDE
a DESIGN WS FACE OF POND SLOPE
� EL = +26J FlL�R FABRIC BELOW
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QUARRY SPALLS, TYP
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" A SECTION - POND OVERFLOW SPILLWAY
SCALE: N.T.S.
FLOW CONTROL STRUCTURE NOTES:
1. REFER TO WSDOT STD PLAN 8-10.40-DO AND ASSOCIATED PLAN NO'�E 1 FGR
VERTICA'_ PIPE SUPPORT(5).
2. REFER 10 WSDOT Si0 PLAN 8-10.40-00 AND ASSOCIATED PLAN NOTES 4, 7, 8,
AND 9 F4R SHEAR GATE.
3. RffER TO WSDOT STD PLAN B-10.40-00 AND ASSOCIATED PLAN NOTE 7 FOR
STANDARD GALV SiEEL LIFT HANDLE.
B LADDER/STEPS, SEE RIM EIEVATION = +26.7
- NOTES 8 AND 10 4. RffER 10 WSDOT STD P�AN 8-10.40-00 AND ASSOCIAiED PLAN NOTE 1, 2, 3
AND 5 FOR VERTICAL RESTRICTOR/SEPARATOR PIPE.
LIFT HANDIE, OVERFLOW STRUCTURE PER CITY OF
� SEE NOTE 3 RENTON STD PLAN 234.20 5. REFER TO ORIFlCE ELBOW DETAILS SHOWN ON WSDOT STD PLAN B-i0.4C-DO
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� 6. PIPE SIZES AND SLOPES PER PLANS.
PIPE SUPPORT, � OUTLET CAPACITY: 100 YEAR, 24 HR STORM EVENT.
SEE NOTE 1 8. METAL PARTS: CORROSION RESISTANT. GALVANIZED PARiS TO HAVE ASPHALT
4' ORIFlCE ELBOW, TREATMENT 1 PER WSDOT STD SPEC. 9-05. 4 (4)
POND DESIGN WS/ SEE NOTE 5. TYP
TOP OF RISER RESIRICTOR PLAiE 1N1H 9. METAL (�UTLET PIPE CONNECTS TO HDPE. WTLET PIPE TO HAVE SMOOTH QD
EL = +26.7 t.25' ORIFlCE CUT ROUN� EQUAL TO CONCRETE PIPE ID LESS 1/4".
AND SUOOTH ELEV= +26.0 10. LADDER;SiEPS SHALL EXTEND TO MATHIN i6" OF BOTTOM Of CATCH BASIN.
SHEAR GAiE,
Tp 0�1�ALL � i B'0 MIN, ��� 11. SEE DRAINAGE PROFILE PLANS FOR ADDITIONAL Rt�l ELEVAiION, PIPE INVERTS,
- � -� � SEE NOTE 2 ; MI 4" ORIFICE ELBOW,
i SEE NOTE 5, TYP STRUCTURE TYPE, PIPE MATERIAL AND STATIaJINC.
wncr aPe ELEV = +24.Q
SEE NOIE 9
`� IN�ET �
%, � • � � RESTRICTOR PLATE W1iH
��i . i 1.12" ORIfICE CUT ROUND
0 2�-Q" M�N INLET FRON POND �� �� AN� SMOOTH ELEV= +24.5
9 LF 18' HDPE 18"d RESTRICTOR/SEPARATOR
� CLEARANCE IE (POND) =23.9 PIPE SEE NOTE 4
IE (NW) =24.0 �'-Q" � z�
' SLOPE = 1.119: i � RESTRICTOR PIATE
� i M�N� ^' W1TH 1.125" ORIFlCE CUT
< ROUND AND SNOOhi ELEV = +22.0
y o z� �� -� � � =� -5_ c�. 60'0 TYPE 2 CATCH BASIN
_� � , `�-�, ��o� t�` r�',� � �^� MODIFlE� AS SHOWN
� - - -
BASE COURSE � �` BOTTON ELEVATION = +2a.0
� � PLAN- FLOW CONTROL STRUCTURE
- sca�E: NTs , e SECTION -FLOW CONTROL STRUCTURE FOR POND
SCALE NiS
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' CALL 48 HOURS `/ ,� - °�
` BEFORE YOU DIG '-3301 9th Ave�ue Sanh,SLi�300 �: _ �T'� �.o, a�br� wo�5 Departmeit
u, Federal Way,Washington 98003-2600 ��`-s�,,,��-, oe,�� �� ��7UM ppproved For ConstrucGon DFAINAGE DETAILS DD-3
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DR2-S02 SEE ORNNACE PLANS 11NT5 OF CA9PIG. TYPICAL
a AND DRJIMACE PR�ILES
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FOOTING. SEE OMG SIM-6 �
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SE� D1YG SW-6 FOR DETAA.S
(�NCREIE Sl.AB,
SEE BNSF�OGE PIANS
, DRAINAGE PlPE CASING DETAit(FACING SOUTH}
DD-4 SCALE: N.T.S
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5fEE1 CA�iG S1EEl CAS�iG I �
1/2'1MD'H STAINlESS � A �� �
S'IEEL BAND �
GRAVI7Y
STOR41 PIPE
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� S1iAI.L��1Tf-FUSED I
„� GRANTY
S70R11 P�E
2-2x4 WOOD SPACERS � I �
PLACm AT A MINMI;Y 5' ON �
COiTER OR AS REQUNtED TO 1/2' 911DTH STNN.ESS
ENSI�tE PIPE DOES NOT SAG S1EEL 8►NO
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� PROVIDE t/2'x t/4'NOTCN kl ?x4 W001) PROV�ANGIED CHAYFQt AT 2-2�c4 fM00D SPACFRS J / :
SYACERS FOR STANLESS S?EEL BAND FORWARD fDGE OF Dc4 N000 SPACERS �� AT A MdiIYIUM 5' ON
� CQ11ER OR AS REWIRED TO
o��oo�s Har s�c SECTION A
� No�:
d COST OF Y1000 SPACERS, STAINLESS SiEEL 8+►t�5, MA
� BUTT-FUSE6 JqN1S SHAII�WqOENTAL TO 1HE COSi
OF 1HE STEEI.CA9NG
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� � TYPICAL DRAINAGE P{PE CASING DETAlL
R DO-4 SCALE: N.T.S
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11500T STO PLAl1 B-60.40-00, T7P DOSTING 36' GIP qAVERi IE-24.31 �.a::�;�;�-;�.��.° ,� �
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APPROx 14 LF TO Z}IE U41TS CLEAN AND TRIY ENO
OF iHE MES7fRN SHOOFLY OF EXIS7ING PIPE, TYP
C� CIJLVEAT D(TENSkON DETAIL
SCA:E 1��5�N i'-5'V
CONSTRUCTtON NOTES:
t. BAI.LAST, TiES A1O RAL TO CONS1RUCiED BY OTFERS
2 REF�Jt TO HNSF 9i00FLY PLANS FOR ALIp�ENiS, PROFlLES ANp ElEVA710NS
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a CALL 48 HOURS � ��;���1��Y1 ` .,.,"'� RENTUN PFIASE 1,SEGMENT 2A ,,,�
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a 1-800-424-5555 ��,3��-i3o��i�i�.so �'"c g``"� rro. � ar on� u� ••�• ��•�'"'
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SfRUCit�2E OUIIJHE AT i}IE BACK OF CURB
� 70P OF SLOPE
BEO+NE q2ATE. 0.YYPI�FOIAJDRY INC CEAIENT(�NCREIE
� ��1 PART NO SY608H OR EQUIVALENT. CUR$ AND GUTfER
� � ` - ORAd1ACE tflTOi. F1NSH�GRADE
� � SLOPE YARES
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� t � s• r �� ` ' _ � i'-0� iFlpC QUARRY�AL1S.
Q n� 5• � � � • " +' EX1EtD TO TOP�SLOPE
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1��8� j .IOINT L1IIia� � � 12�HOPE II
� LO�k POMT �
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FOR WALL 3.5' 1�1 I SEE ORAMAGE PLANS FOR
COII�iATlON II�ET� SEE ORARIAGE S1iiUCllNif MFURMATiON. �
PLANS FOR SiRt1Cll�tE INFORMATION
, C�NCRETE GUTTER TRANSITION DETAIL-STORM DRAIN STRUCTURE N0. DR1-SD2 ��CONCRETE INLET DETAIL- STORM DRAIN STRUCTURE N0._DR1-SD1_ I
DD-6 SCALE: N.T.S DD-6 SCALE: N.T.S.
NOT=S
SOUO CAST IRON UD 1. ARFi4�ILETS TO�CONSiRUCTED FROM CON(�ETE P�PE.:N
ACCORDANCE M17H ASi11 C 14 t1�iLE55 O7FIERWISE SHONN GI
PCANS OR NOTED IN T}�STMIDARD SPEC�ICAlIONS.
2 CUTOUT HOIE 9ZE 15 EQUAL T6 THE OU�IET PIPE OUTSitJE
�IAAIETER PU15 AFtFA RiIET WALL 1HCKNESS
a cau+EcnoH ro ounEr�e-o e��T�wm�w�uwe�us+
Mihi MI�E OF THE NtEA INLET'�ALL.
PLAN VIEW 4 NON-ROCKING�FfTA1NTH ,WY�sna+.� ro�,ssurt�
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s�cnon
OUTtEi P�E M�A INLEi
� (t)PtPE WAi.I THK:KNESS qA 0 DIA i
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RDO--& SCAiE: N.T.S
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�_�Z���� , �, �"`! `�,� 5� «.�,�.�.� CITY nF STRANDEA BOUtEVARD EXT�IdS10N �/�+/+�
�j ^,,��., ' f�" � RENTON PHASE t,SEGMENT 2A „r
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a CALL 48 HOURS � v —
� BEFORE YOU DIG '�3301'"'""ewe 5°'b'•s�e 3°° '�` 'a` 3¢�' � ,�� a"'w �� �� DRAINAGE DETAILS
� Fa c«�:�«� DD-6
� 1-800-424-5555 �z��3i z3oo�os�-� �':"L�' No. r�vrs�a+ ar a� � •�- •"`�'
��� SHEET 4
� .so Rahat Al. Haneon P.E Oat� G3 227
o DESIGN DATA WET WELL BOUYANCY-STANDARD BASE
d� ADDRE55/IOCA'RON s1RAN0ER 80ulEVril2D.RF�lrON� wa ASSUAfED waTER[E1+EL ELEVAiiON- 27.06 calU►A
� � LATi13UDE�LOPi��l1DE 47'2723`N 122'14�29�N' N£T WfJ.I 6EPlli= 32.0 FEE� S�rar�der Boc�levard Ex#ension
� Fvncna+ sur�ace sroa�wA�x a+o cRourar�Ahrt wEr wFu M�c�au�r¢x= io.a�T
�w��wc�;Wa s�na+ wer�u wat�n�acr+as- n.o�r�s Stormwater Pt��np Stateon
auua sTana� �rnE oua�.ex suautRs� ►�t+�tt wau aa= �f.s��ez
� o�a+sroeu 100- YfAR REWRRiWCE lNTERVAL aorroµ su� wm�= u.o t�r �ystern-�Eead-Capa�city Curves
� DESfGN DUTY POINT 3.280(�!d 0 3t.8 fEET lUH �Tf���A� ti4.6 FE�T (
ESTRIATEC FlR11 PtA1PiNG^APAqiY 3.375 GPN{SUIGif PU11P) (SEE NGiE t) � BOTTW SLAB TFNCKNE55= 3S.D0 INUiES 70A
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� PUAIP MOTOR DA?A 45FIP, 160Y 3�, 7.37(1 RPY ! � [
a PRIAIARY LEV�'�CONiFtOt PRESSt1RE TRANSW?7ER VOLUAIE CF WATER Ot�LACE� 3,759 CJ91C FEET '-t I
� BAq(UP LEVEI.r'.ANiR� FLOA7-SNlTC�1 TOTAL UPLFT FORCE= 234,51fi i� �.8 , 2 PUAIPS ON PU4R CURV� --i----
PARALLEI.OPERAiION
a NETVrELL CONCRE7E. 30-�tET iN1ERNAL DIA►1ETER {SEE NOTE i) '
� V�UAIE Of CONCRE7E= 1.300 Ci18tC FEET `�� . . '
� HETWELL S70RAGE WWt1E 588 GAtLONS/f00T _ PUMP STATtON Dt$CtIARGE fORCOdAIN.
WEH�IT OF CANCRET£= t95,D2t L8F « - - �SYSiEN ClN24F
f PUYP OPERAil�G VOLF111E(SEE NOiE 2j 6,322 GAt10NS �4d.0 t Ptt1R ON �
� COLLE�nON SYS1F]J STGRAGE YOLUME 4.264 GAtIONS �PUMP CiJRVE - 1
�. i WLilbiE�SOIL A60VE$A$= 2�744 a161C iEET S
U EYERGENCY STAN�Y PONQi CENERATOR � DE4MCATED ON-SF7�2(M1KW.�IESEl Wq�tii OF 50�A804E SLAB= 301�803 L9S s 3�0 fSEE>10TE 1} '
TRANSFEft SMiTGH AUTOMAT3C = - �
Fl1Q VOIUYE STOREQ �f-9TE 336 GAtLONS TOTAL RESSTiVE fOf�CE= �96.823 EBS ' (
SAFETY FACT�t= 212 2Q.0 f 5.b75 GPIA 9 - �
fCKtCE IJARI OESIt�i DUiY PONJT= • 3gA'
LENGTM i60 if �8� 3.375 GPLi 0 28.67' , ' �
a""� 24-�"�" WET WELL BOUYANCY-TREMIE BASE (
�nr�u a 5s QucTx.e�aa�PE �� ' . � � � ; � {
DkSCHARGE 54-INpi qAMETER MAt�l01.E 20 FE€T ASSU4Ep WATER LEVEL ELEVA?ION= 27.00 DA'UN � �p ,� ',� � ,,p 4
NOR1H OF WAT�3t QUAi.1tY PCNO ME7NEEL�ti9DE DIA11E7ER= 10.0 FEET �3",yp�,y;��Q�,yii�(Y',��f�¢CII'' ��h�y��Ct'6�,`C3',�4i��������g������ I
WET WELL WALL THI��EESS= tt.a INf�iES j I
FLOW 11ETER 2G'iN-Llhlt MF(�.ETIC CUTTNlG SNOE THfCKtiES� 11.0 PI(]IES j vokana F�a�w itace,4 i�} �
NET MELL WAt;.�= 11.E3 f�T �
t�►�+ vLooa c��= �.o�T DISCHARGE,Q(gpmj
� ESilA1AiED PU61P Cl(a1NG FREOUENCY YOLiIAIE OF MfAIER DE�.ACED� 4.235 q{&C Fr.ET
70TAi.UPL�7 FORLf= 264,244 LBF
CONDi119N qJFLOW(Gi} PUMP CYCLES (SEE A�i: Jj �
DE'IMATERNIG 400 GPA1 1.7 5TARTS PER P�AIP PER HOUR �
2-YEAR ST�1 t.515 GPY 4.0 STARTS PER PUMP PER H�JR � YOIUI�OF CONl;RE7E= 1,776 ttJ�FEET
WEICHT OF CONCRESE= 266,4t�l.� �
100-YEAR STORM 3.280(,�1A 0.5 STARTS PER PUtJP PER HOUR
TOTA�RESIS7}VE FORCE= 256,432�S
�' SAfETY FACTOR= 1.61
� NOTES:
�
1. PUAIP CURifS BASED ON ITT FIYCT�IQDEI NP3202 LF W/314MM�IPELLER k 45tiP IAOTOR
� 1t70 R?9.1. C�Ni4E N0. 63-617-00-601�.
2. B:(WEEN IEAD PJMP ON Ai�PUMPS OFF SET PqNTS. tNCUJ6M}G COI.LECAON SY'S7EM
4 S70RAGE YQLi1ME.
�:
� 3. SEE 0'NG P5-7 FOR SET PORiT ELEVARONS BP.SED ON 'HE SYSTElA-HEAD-CAPAqTY CURVFS
� SHONM. ASSUYES 0.LTER?7ATiNG LEAD-lAG OPERATiON.
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� � HPP-1276(OCS) � Berge��BAM �� �" � �� RErI'F�I� PHASE 1,SEGMENT 2A
�' CALL 48 HOURS '
� 33301 vm avplr,e south,s,iP 300 .�'y c,f� �! �`� ?aTUY aubrc w«xs Devertrnen: �
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�i fER+JD:STPUt-7276(OD4) �,,��. , ,.,���,�x., �'ITY OF STRA.NDER BOULEVARD EXTENSlCN �l+�:"
� �-�2�s{ooa; ���7� ,� � tis sr:owri
�. � �Ig�I�1�►���t Vl �" RENTON PHASE 1,SEGMEIdT 2A
CALL 48 HOURS �'/ N ,� "",,,w P,,�rK www Deportment �
� B E F O R E Y O U D I G �w�.W��-� +��q,,L`4c � � e�--{ o�ruN ,�,P P„p,,,a �a c«+at���c•m� S T O f�A P U A�f'S I A T I O N P S—5
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� �VuyE 1'-6 7/6" t'-2 3/8' B 3
d, VAtAi 3 � � PS-B REINFORCID � WE7Mfli�F.1rT. SEE PS-tt
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i � ��8 � 6'-0' x t'-0'(qFJiR OPENING)DOUHLE IEAF AL�IRNU41 ACCESS HATCH. H20 RATED. LW PROIXICTS
0
NDSBS-3C OR i�PPROVft3 E�1AL
�� � �`� . � NOTES: Q 9'-0•. �'-a'(WTE�NAL D�IS)PRE-CASS CCMCRF� FLOW-AIF?ER VAULi. ��t1'HfG(NESS ��rnun
- i VAULT CUS10At OR APPROVED EWAL.
� ,ti1,� � / Q �18NERS�LE WASTEWA7ER PU4JP NITH pUlqC GISCOrCdECT ASSEIA�Y At�LtFTINC RAtS. tTT�I.YGT � 20' CL 53 OiP tPE}. L£NG?H AS RECID.
� . . / Af00E1 CP 3202 11 NITN,314 YN UIPE�IfR,OR APPROVED EOtiN..
21 24'z20' CONCENTRIC REDUCER(lJJ).
' , 1. {• ,i • .. �;� f/ O2 SO' �iSIDE DSftYETER NETINELL. WAII.C AST4 C-478.
. , /�, � O 12'-D" x 12'-0' (NIERNAL DMdS) PflE-CAST CONi'..RETE VAL4E VAUIT. FUIt hllq(NESS.UiiLiiY YAULT � 24'01 FORCEAIAIN. S£E DWG PS-2 fOR At;GNAIENT 1�PROFlLE
g � ��.. ;� � /' CUSTOM SI2E OR APPkdVfD EGUAL � 2fl' Mt-UNE 11AGI�11C FLOri MEIER(1G� SiEIAENS 9TRAN5 FII CR A?PROYfL EGUhL
m �9 O4 B'-0� x S-0�i CIEAR OPENMiG)DOU&'E IEAF ALUYII�AqI ACCESS NATC}+. HYO RAiEO.LW PRODUCTS
�„ � F�-S85-4D CR APPRO�ED EQUAL � MOUN'tNC PLA?E FOR PORTA2LE OAVIT CRANE SEE �11
r-�- -
.. � . \ /� �. . O5 36� Di INFt.UQIT GRA4ITY SEWER.
� �' / �5 20'RESTRA4DIm FLANGE COUPL)NG AD�PIER. ROMAC RFCA OR APPRG�ED EOUAL � �E 1 REIAQYA&E BOLLARD (TYP QF 5}. RFfERFI�CE CITY JF REN"ON STD PLMt H019.
� I ;./i _�_ i��� 2 / O7 60'DlAYElIIt M0.ET YANHOIE MALL C. REfEREMCE CITY Of RENTON STD PLAN 4p0.t � 4'PVC VAULT DRAtN PLUMBED TO NFTWELL
/
� ' - - �� ii� ft I�IE?ER YAtiIT� � � � FRP RETRACTABIE LADOER. SEE �
I . �i � • FIOW NfTER �, O8 fLEk�I.E�UBBER GASKEi. KOR-N-SEi,I OR APPRCYED EWAL FOR PIPE SIZfS 1' MID URG'ER. GROUT 5-2
� ` • E I _ 2'-6"AQt+�. / SfAI P1PE5 UNDER 1' 1Mi}i NUN-SHRk�K GROUT. � 8'-0'z�'-a' (CIEAR OPEhtNG} DOU��LEAF IIUAUNIAI ACCESS HAFCN. H-20 RAiED i.Vl PRC�UCTS
�! �` = Q9 12`SS 90'ELBOW. (FLG OR WELDED) HU-5 OR APPRO'�ED EQUAL.
7-6'11W. , � LEVE3.�T1SOR INSTALLED �J S1�LWG Yk].1.. SEE �
� o � � 1 � iY SqiED 8(1 SS CISCHARGE PIPE.LE'iG7H AS REO'D. (F1G X FE OR YIELDED} � �
1
� 1' 8 �, , / 31 CABLE TRENCii SYSiEAi. SEE _4;
11 12'fLEXIBIE ?�E COUPLNIG FOR D1551MLAR PIPE NAiEPoA1 NiTH RE57RAINT SYSIEM. RO/IAC 501 W/
� • I-: . . , 600 SERiES RESTRAINT OR APPROVEp-QtiAL E48ED LUG 30Li5 1iIN. 3�SN SUPPOR7 BLOq(. � 12�x 53 DF DlSCHARG£ PPE(PE}. L�JJG111 AS REQb.
8' PVC
�, ---- -- / �RAIN fR011 YARD � 12'IN-IJNE PRESSIIRE GAUGf. A91CRt�"OR hApROVED EWAL(FLG). � CONCREIE SUPPOftT�OpC. 1lMIAIVAI qNEN�CNS AS NC'ED.
� % CATCH 9ASlN
i � � tY fl 5MS►EG GiEpS YAL4E IIBH VALVE CO., STY(f 259-�2 OR APPROYED EqJ/� (FLG). � 12'RET/UNER GLAMD E118EDDED IN 0[1NCRETE St�PORT BLOq(.
y 21
a ' 20'RETAINER(�.N�O E►�EDOED IN C1rlCREiE SUpPpRT BEOGC.
$ , � Q4 12"PLUG YAiVE+M/GEAR OPERA7E4 Hu�O wiEEL APCO SERIES 500 OR E(]UAL IfLG}. �
LL � 4�-p.Fl.EwBLE RS1NqF LEAF AL YNtAl CCESSHATCH.�H-20 RA�D.�LW PR�UCTSRNS-SE�W.a1
� � 2D'&1N0 Ft.A1�iGE(FLG).
� 1 16 20'X12�REDU(:�lG TEE(FLC) APPROVED EQUAC.
� � � 36'KNIFE GAlE YALVE (FLG)ON SNLET SEWER. YMWALIY OPERAIED W/HANDYd�EL Pm VAIVE
, STORM PUMP STATION WETWELL AND VAULTS - PLAN �,��� „�,�„�E�,�.
� - sca�: ,�r=,�-o-
5 � 36�FLANCE NE!DF+�I TO INLET SEYYkR
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� BEFdRE YOU DIG �r�w�9e�oos-isoo �'4�"'`°b� � � oaTuu n�rowd Fw co�etti�t;o. �
�+�*�'`�� No F�wsww ' er wrE �wwt F��-� WET W0.0 AfJO YAULT PLAN PC_�,
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IVAI+rE vAULT 4'-0' WET NE1 T
� 3 RUI E1=27.42 k VAIUE VAJIT PS-4 ^�A1�EL i .� E WET riEli. S N�i ES:
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d . . '•, . �:� . . Al06EL N?3202 LT WJ�14 1M�t 111PELtER GR APPROVED EQUAl.
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i �' �I 2 3 ( WSTOAI SIZE OR APPFOVED EOUAL.
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f I
(J 4' 9CHID 4D PVC SUAP DRAIN PLUA�ED TO WETWELL. PROVIDE 4' C1��(YAl4E ON DISCHARGE.
� lf . � i1QEFLE)( SER7E5 Tf-4 OR APPROVED EWAL
PIPE
� �22D - - - -- - E I '
� � O 6Q'DIANET£R SFORY:tANHOI€. REFER£NCE GiY OF REN70N STANDARD PLAN - 400.t FQQ
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Q I • : (g� { � 4-�• � � B'-0':5'-0' (CL£AR 6?ENNG)DOUBCE IEAF A�l%tlNUU ACCESS HATCH.H20 RAiED. iYl PROOUCTS
� � � � �1 6• . ./`-' 1 � ! � � HD-SBS-4fi OR APPRUYED EWAL
� .� ' � I � I 09 CaJTNU0E15 LMIER. FUu HEIGHT ANO DEPTFi OF WETWEII ON ALL MTFRI�R CONCRE�E SURFACES.
� I
-�, HiCH GRO(1!� AiEft II ; RA4EN 4Q5 OR APPROVAt EWAL
� EL=+19.0� Q fLOAT SYAYCHE$ANJ �ABLE NOLOER(TIP. Of 3). 51NTCHES SET EOR LEAD PU►IP ON. UG PI:AiP QN,
� �� � � dt?1JLIP5 OFF.
�9 .. � " �� f� � 11 l£YEL SEHSOR WSTA!!FD ai S1ILJJNG Y�ELi. 5'cE „ �
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. , y !1 � � ? � $pAqNG PA�'I"iRN ANL BOLT$IZE.
7 4/2�-3/4'CR'JSHFSi 2=kIN !I !i � 1� SS �SCHARCE P�E ANqiCR BRACKET{TYP OF 6) =QUALLY SPACED.
ROpC COAlPACTED TO 95� kl t I I S4 p�PE pENETRAnON. PFJYIDE FLEXIBCE B40T(KOR-N-SEA!OR APPRO�ED EWAL) F�R PfPE SIZES 1"
1Y CEP?H �
s �� f ,
AND LARGR. GROUT:s".AL P9E5 UNDER t' NClN NON-SHWNK GRDUT.
� � ( 1Q 3' SCHED 40 STAINlf:�STEEL p:�OE 8AR RAILS(2 PER PllOIP}. ATTACN ltl LIP �'NETN£LL ACCE55
a2 ,, 4 ! .� � � HATCN OPEHit� WlTH SS GJ�E 8AR BRACKETS BRACKETS TO�PRONDID BY PUAIP 11ANUfACiURER.
� I 'r=1 16 PUA�P DISGiARGE E18�nY w/�n1'cqtAl BaSE PLnTE(iYP OF 2). fURW9i wht PiRIPS
Jp1NTENP.MCE ?!AT��f?iJ.F Lk7° �=fl'_5' � Q 12'PIUG VAtVE W/GEAft�ERATEO HANO WHE£L APCO SERtES 500 OR E�AL(FLG).
' n �y' 12° SAk1G QiECK YALt�.MkH VALU�CO.. SiYLE 259-02 OR APPROYEO EWAL (RG}_
; � . �
t6NEST ROA�J'�IAY'SURFACE EL=+9.5' � i � SBZ � i � 12'SS 9d'E1BOW(RG OR Nfi.DED). Z
i
' � f � tAOU?ITi4C PE.AZE FQR FORTA&f OAWT CRANf. REFEREkC£ ps_� .
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� { � � 1i MA:Nlt IAMCE • 4 2� '2� SCHFD 40 55 DISCHAR�?IPE. LEIJG7H AS REOU1�(FLG X FE A$WELQEC}_ I
� i PLASFORY
FLOOR � � S$L�iNiG CABLE(TYr�9F 2). S�IPPLY V11TH PU11?S.
� � � . Q=+6.5' � 3S�KNIFE;ATE VAL11:{tLG)ON INLET SE'8ER ItARUAILY OPERA cl`D W/HAttD Y4HEEi, RED VALVE
� � � ' SE'�r lES G OR APPROVE D EQUAL NUA�fR dc SPAqNG PER MANUFACT;�2Ef2.
VAUIi DRAIN CUiFAIL EL=+d.5' 6 � 2 ; I p � FRP WALI.11WNfEU LAUOER 1V/REiRACTABLE EX1EHSi0N.$EE �2
� I °D � STA(NLESS ST�L IYTfBIlEfNAiE GUIDE BAR BRACKET. SUPPLIED BY GUAiP kMAiFACTUf�2.
Q LAG PUY?fNl/WGH tEYEt AiM41=+J.S' � !
a� I ; p 14 � PRONDf 12'COtiCENTRIC REDUCER AS NECESSARY TO AIAlE PlkdP OISCHARGE EL90M(?YP OF 2). {ftGj
•'_EAD Fl,'AIP ON=+25' � i 4 5
I � 4'-Q'x4'-D' JNGLE LS:AF ALtANNU11 ACCfSS HATCH.H-20 RA�.LW PRODUClS FSS-5 Ofi APPROVED
_ I � £OUAL
i � 9'-0'x6'-0' (CLEAR ��'cNING)DGUBIE LEAf ALU6UkUM ACC£SS HATCH. H-20 RA'tID. LW➢RODUCTS
� p� --�- ►i0-5�2 APPR04E✓ :QUAE.
� j –���--+a.-s
� . 3 � t2' qAl�lER SZAAP CASt NT:1 BASE OF YALVE VAULT.
?UASP$�F�NVERI IE=-t.0' I ' • 1F=-0.9 3� 14�-G�R74�-0�i,AST-IN-PLACE CONCRE7E WET'AELL 3ASE. FOR AIT�RNAT: CU"!NG SHG£AND TREl11E
� � , BASE. SEE DET,VL �
� � > s f 14 I 4 4 ��
S-2 b 30+. p(PLOSION PROOF U6 iT fIXTlIRE SEE ELECTiiICAL DVY'S.
�a MH FLOOR
tlt � � , �,_�. EL=-2.9 , . � COkCRETE SU?FORi ELOCK. NR�iI►IUM DI11EN90NS AS NQiED.
i w�n��ooR a=-a.s' o � ' � AIORTAR JOINT(Sj(3/3'+�.)(rn�.}.
� t� � •. = ti� ,��,. ��� � 12'RETAWER q.1WD EM9EDDED IN�T£ SUPPORT BLOCK.
y PROYIDE(2) MATS�412' " _ ' 1Y FL:XEBLE PIPE CO;�LING FOR QIS9AfiLAR PIPE MATEFtIAi.SNTH �ES1RWhJT SYSTEM. ROMAC 501 WI
CN-CETIIER EACH-WAY TOP t :/2'-3/4' C}iuSHED � 600�PoES ftESTRAINF. OR APPROYEU EWAL EM3ED LUG HCtiS f.�N. 7'IN SUPP�RT HLOq(.
R &BOiTqA (3'CL} ROqC COAIPACTED TO 95R
• � . 12'DEPTH � 12"FL M-LNE PRE�URE{NSiRUIaFHT Yr/GUAGE AND ISOLA710N YALVE. ASHCROFT CR APPROVED
� A STORM PUMP STAT{ON WETWELL. AND VAtVE VAULT — SECTIQN ��aN�,wc�r�,;r�.
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� ��S R. q,� �JRfi� � ADJUS?ABIE PiPE SUFP01tT. CO�ER 3-UkE B3044 Cft APPR6UED EQUAL
� � FER4D:STP'J�t276(004) �Q��`"�'"� � ' °""m` ,.,�.x°„�, C�'j1'QF' STRANDER BOULEVARD EXTENSION �/�a�>>
�a-�2��(aos) �, �as srwwrt
�� Bergerl��AM "`" RENTOl� PHASE 1,SEGMENT 2A '""°`
�' CALL 48 HOURS �../ �,,,� p,;�A� ,,,�,,� ��.,1T1Q1t
� BEFORE YOU DIG ssto�9n,n�wesoutn.s,�eaao q, .�»+ �" „� �}a,�,,�..� �n:� nawa�ae vo. c�s�,�ror
r-�way,was�r�,9mn�-�oo �zw�,,,,�� �o. Re+ns�aa er oar� �R � �� WPT WELL,4N0 YA{�TPSECT10NS•SHEET t �PS-7
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�
'� � O ����W���E�� Wl1N Wlq(DIS�ktECT ASSEAIB�Y ANO 11fS1lIG RAIIS.17T fLYGS MODFl NP 3202 LT W/3t4 1AhE
10 �
j 2Q 10'NITERNAL DINiETER PRE-CA57 CONCRETE'NE7M£Il /S`Y C478. WALL G
I
� O3 4"SCNED 40 PVC SUAI?DRAiN FROM 4Al.VE VAIk.T. PROHDE 4' �p( VAL4£ON OISqiAR(�. 7�EflE7(SER�ES 1F-4 OR APPROYEC
` EQU?1.
5 ; 6 S !6 �
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� O4 8'-0'x 5'-0� (LI.EAR OPENING)DWBtE i.EAF'AUAdINU1i ACCE�S HATCH. H-20 RATED LW PRCIQUCTS!i�-S85-4D OR AFPRO'!EO
rc --- ---�DESQIARGE PIPES----- --- �- -3 - -- - EOUAt.
� 0.=22.0 -
� f O5 CONIINUOUS L1NER ftkl NEIGHT At�DEPTN OF Y�TWfLL ON ALL INiERIOR CONCRE'(E SUFFAC�S. RA1iE1l 4Q5 OR APPROVAL Eqt1AL
� f •
� ! � t 1 (� ROAT SW!TCH ANO CA�HOt�ER. SWITCN SEi r'OR LEAD?UI�ON. RYGT 110DE1 ENiA-10 CYi A?PROVAL Edt:AL
� �� 1
1 i I � 7� LEVEI SEAiSOR AND STaLJNG NEt..t_SEE 5-11 '
� I �
g � NlGN CROUN�WAi{cR ! 9 � 'g SS aSG�lA�Zf,E PIPE ANL�10R BRACKET(TYP OF 6}. FURNISHfC BY PlA1P YAHU�ACTIJRER. tNSTAt1 PER MMJUFACiURER�S WSTRUC?i0N5.
� = EL=+19.0 .
' � 9 PIPE e�iRATlON. PRCNDE FLE)0&E BOOT(KCR-N-SEAL C�2 APPRO�FA EQI:AI)FOR PIPE 9ZE5 S' ANO LARC�R. GROUT SEM.PPES
-----�----
g `�_ �_SUA4P DRA1N ENLET - - --- - � - - - O txJOER t' WliH NON-SI{RINK GRWT.
� � 10 3' SCkEO 80 STAINLESS STFEL GUVUE BAR RIllS(2 PER FUA�;. ATTACH TO UP �F 4YE7NELL A:CESS FtATCH 9PEN(MG W17H SS IX1�E
� f ' BAR BRA�(ETS. BRAq(ETS TO 8E PROVIDED BY PUMP MANUFACIURER.
f I 11 S�SCHED BO SS 015CHARGE PIPE LENGiH AS REWIRED (Fl.G X PE OR YYELDEU).
z 1 I (
. � � Q SS UF11NG CABIE(TY?UF 2).SUPPLiED BY PU4P AiANUFACTURfR. '
i
� I � � � 7 3 STAtNLESS STEEL IN1E�IcDIAiE GU(C{8AR BRACKET. SUPPJED BY PUIJP IAANUFACTURER. NUA+SER ANO SPACNG PER AfM�1fAC1URER.
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� FE°"'¢STatx-i 2's(ow) �°�a~� � '�`@ ��°..�t.. CTTY OF STRANDER BOULEVARD EXTENSION �/�+/��
� FPP-1276!OGS) �� �er�e��!►BAM � � � ��s 5"ow" , RENTON PHASE 1,SEGMENT 2A
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� DESIGN CRITER�A �N���N� CONCRETE REINFORCENG STEEL STRUCTURAL MASONRY PLYWOOD SHEATHING
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� A. Li'JE LOADS: 2 DETA�,fA�ttCA7E A!m PUCE REWFOR�7G ACCORDING ?0 Ap A. 1AAS(N1RY UNITS: A. GRADE: SHEA7HWG, EXP i.
� GRWND FLOOR._. i25 PSF 315. 'DETAtlS Al10 DETA�ING OF'CONCRETf R�NfORCOIENi'. 'YPE N, 1EEDIUY MiEICHT, 19Cq PSI IJIN. ON I�T SECTION. B. A1ARlC�D NRTH SFiE AkERICAN PLYN'000 AS"�0(]h'ION
►IAMI1FMAkCE ACCESS.... �0 PSF 3. Tl'P�CAL HEilB'ORCWG(WMYW. UNO ON DRAWWGS): CONFORiA TO AS1M C�. APA TR/hDEIYIARK.
B. SNOW LOA6S � COHNERS APiD INTERSEC710N5 Of WALLS AND FWN�A1tONS: SZE: Sx8ut6(NWUNAL}. 2 CFLL UNITS. 2. SHEA TYPE3
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5. p�q�E';FCif21CAl CON[,X11T NEAR CENlk3t Of SLAB. 4. L�OSE GRANULAR IH9L'LAiION
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AGAINST SQ.F-WEIGHT, SNOW,'A�T�.IAiERAI EARTF! AND S£1SAtIC FORCES �.£AD: 2 310RIZONTAL BARS, EGJAL IN SIZE SO TYPICAI. 8"SPA�NG AT 14i1ER10R OF SFIEETS
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A. �IBIItT ShOP DRANt!iGS OR tdANUFAC'URER DATA fOR: A^COFt01NG TO ACI 361,�STAkDkRa$PECFICAiION FOR STRUCTURA�CoNCR�tF�. � fOUNDA tON ALL S ItL DOWEt, EWl1 iN SIZE
t. CONCAETE AtlD YASONRY R�tFORqNG STEEi. TJ TYPiCAL VER1lCAL RE�ifORqNG AT EA;,Fi YfRTiCAL BN2. 1. PROVIOE CF�LNG x4SULA110D3 BEThEEN tRU55E5. INSlH.A7lON SHAU.9E
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5. MAN DOORS �OMPLEIE GROUIMlG OF ANY�CiION OF WAtt iN t DAY ,1(Y{NS MANNLLE,KNAilf FI9ER(7.ASS, OtlIENS �ORl�IG, Oat APPROVED
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i. �u�r u�r,�xnr ca�r�c�o w000 r�usses. ANCHORS IN CONCRETE ANQ MASOAtRY 9Y STO,�PING ALL WYhIES AT'HE SA11E EIEYATKJN ANp LlGHT METAL PIA�E CONNECTED WOOD TRt1S5E5
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3. EXPAN90td ANCHORS CONCf�7E ONl CONt�tE7E AUSOtiRY UTlkTS�iAi.t.BE DARK COLOREO. i1�1RUSS PUTE INS?INYE. UNO.
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PUBLIC'A�RKS DEPARiIt1ENT.
SITE PREPARATI�N �.,��, ,� �� ��5;
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� 4. ADHESIVE ANCHORS (CONCREIE OR GR011TED YAS�JRY� �� GRADE LUIIBER ACCOR�tdG TD RIA_ES OF NEST COASi LU418F3t 6.i�CHAtUCAL lOADS: AS SHO'NN ON ORAWINGS
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DENSTY, AS DE�ERAiNED 8Y AST11 D 698 CONCR£lE OR 11ASOPIRY ACCORDR�G TO ANPA STPNDARD C-2
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e � FEi�APPLY PRESERYAIIVE AT it�Q175 OF 2 pya�qt gOLT$: ASTM F 1554 GR 36.
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�sc aoc� u. ��o� P.E. Daie STRUCTURAL OETA►L5-SHEET 3 i 26 izy
Hydraulic Report
Strander Boulevard Extension Project
Cities of Renton and Tukwila, Washington
Appendix C - Drainage Calculations
Department of Ecology Requirements
Summary of Areas for Phase 11 and Phase III
MGSFIood Calculations
Pond Volumes
StormSHED Calculations
Gutter Analysis
Miscellaneous Calculations
Drainage Calculations
Department of Ecology Requirements
� Start Here
Does the site have Yes See Redevelopment
35%or more of Ivlinimum
existing impervious Requirements and
coverage? Flow Chart
Does the project convert (Figure 2.3}
No 3/4 acres or more of native
; � vegetation to lawn or
� Does the project add po landscaped areas, or
5,000 square feet or convert 2.5 acres ormore
mare of new of native vegetation fo
impervious surfaces? . pasture?
Yea Yes No
Does the project have
2,000 square feet or
�M�� more of new,replaced,
. Requirements apply to or new plus replaced
the new impervious impervious surfaces?
I
surfaces and converted
pervious surfaces. Yes No ,
f �� Does the project have
I Requirements#1 land-distutbing
through#S apply to acfivities of 7,000
the new and replaced Yes square feet or inore?
impervious surfaces
and the land disturbed. I�o
� See Minimum ,
' Requirement#2, '
Construction
Stormwater Pollution
Prevention
Figure 2.2—Flow Chart for Determining Requirements for New Development
I II
I i
E
February 2005 Volume 1—Minimum Technical Requrrements 2-9 i
(
1
i
2.4.1 New Development
All new development shall be required to comply with Minimum
Requirement#2.
The following new development shall comply with Minimum
Reqnirements#1 through#5 for.the new and replaced impervious
surfaces and the land disturbed:
� Creates or adds 2,04() square feet, or greater, of new, replaced, or
new plus replaced impervious surface area, or
• Has land disturbing activity of 7,400 square feet or greater,
� The following new development shall comply with Minimum
Requirements#1 through#10 for the new impervious surfaces and the
converted pervious surfaces:
� �Creates or adds 5,000 square feet, or more, of new impervious
' surface area,or
• Converts'/4 acres,or more, of native vegetatioa to lawn or
landscaped areas, or
• Converts 2.5 acres,or more,of native vegetation to pastnre.
Supplemental Guidelines
Basin planning is encouraged and may be used to tailor certain of the
� Minimum Requirements to a specific basin(Mi.nimum Requirement#9).
Treatment and flow control requirements may be achieved through
construction af regional facilities. Such facilities must be operational
prior to and must have capacity for new development. I�
Appendix C of Volume III directs users to model vaziaus low impact ;
development techniques as landscaped area, 50% landscaped area, or �,
pasture. Those same modeling credits may be used when summing project
areas to determine whether the thresholds zn Figures 2.2 and 2.3 are
exceeded.
Where new developinent projects require improvements {e.g.,frontage I'�
impzovements}thaf are not within the same threshold dischazge area,the
local government may allow the Minimum Requirements to be met for an '
equivalent(flow and pollution characteristics)area that drains�o the sa.me
receiving water. !
� 2.4.2 Redevelopment I
All redevelopment shaIl be required to comply with Minimnm
Requirement#2. In addition, all redevelopment that exceeds certain '
thresholds shail be required to comply with additional Minimum
Requirements as follows.
�
February 2005 Volume 1—.Minimum Technica!Requirements 2-91
Drainage Calculations
Summary of Areas for Phase II and Phase III
i
Strander Boulevard Extension - Project Area (Phase 2) I
Total Area = 228,867 SF � 5.25 Ac I'�
EXISTING -Areas
Impervious Pervious '
ACP Gravel / Land- scape
Rockery
SF SF SF
3,978 855 213,500
5,787 3,957
790
9,765 5,602 213,500
EXISTING AREA TOTALS
Impervious Pervious
15,367 SF 213,500 SF
0.35 Acre 4.90 Acre
6.7% 93.3%
PROPOSED -Areas
Impervious Pervious
Replaced New Landscape Gravel
Impervious Impervious
(SF) (SF)
104 28,563 46,288 51,863
3,597 5,142
2,448 27,994
716 48,802
5,787 7,563
12,652 118,064 46,288 51,863
PROPOSED AREA TOTALS
Impervious Pervious
12,652 SF (replaced impervious) 98,151 SF
118,064 SF (new impervious)
130,716 SF (total impervious areas)
3.00 Acre 2.25 Ac
57.1% 42.9%
Q:1FederalWay120091FAPWT-09-175'�ENGR'�CivillDrainagelHydraulic ReportllnfolTreatable_Areas_DOE 2005_STRANDER JULY 2011.x1s
7/20/2011 9:13 AM sheet: Project Areas July 20 2011 PH2
Strander Boulevard Extension - Project Area (Phase 3)
Total Area = 263,698 SF � 6.05 Ac
EXISTING -Areas
Impervious Pervious
ACP Rockery Sidewalk s ape
SF SF SF SF
743 1,735 616 217,523
730 3,357 1,461
18,726 9,697
9,110
29,309 14,789 2,077 217,523
EXISTING AREA TOTALS
Impervious Pervious
46,175 SF 217,523 SF
1.06 Acre 4.99 Acre
17.5% 82.5%
PROPOSED -Areas
Impervious Pervious
Replaced New New
Impervious Impervious Impervious Landscape
(SF) (SF) (SF)
701 1,232 14,996 64,382
30,709 566 1,461
3,350 1,701 75,172
3,645 534 9,405
1,266 682 3,511
13,435 36,950
39,671 18,150 141,495 64,382
PROPOSED AREA TOTALS I
Impervious Pervious I
39,671 SF (replaced impervious) 64,382 SF '
159,645 SF (new impervious)
199,316 SF (total impervious areas) I
4.58 Acre 1.48 Ac
75.6% 24.4%
Q:1FederalWay120091FAPWT-09-1751ENGR\CivillDrainagelHydraulic RepoA\InfolTreatable_Areas_DOE 2005_STRANDER JULY 2011.x1s
7/19/2011 11:21 AM sheet:Project Areas July 20 2011 PH3
i ,
I � � I I �E
GEND
�—�� I I I � NEW IMPERVIOUS AREAS
m � I I �i I I I � REPLACED IMPERVIOUS AREAS
E � ,
� ' I r 1 i� I �:�� � OFFSITE AREAS
�, WETLAND "J" `� i i •�
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a � r� q WETLAND "N" ��;y � � WETLAND I�I
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d ', � �l
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CALL 48 HOURS �j �erp-�IA17AM � ���^-� CITY OF
BEFORE YOU DIG `/ � � RENTON
Public Works Department
1-800-424-5555 33301 9[�Avenue Sarth.Sui�300 �� OATUM �pproved For Construdion �
Federal Way,Washing[on 98003-2600
(206)431-2300 Fax:(206)431-2250 N0. REVISION BY DATE APPR �'"��' Robert M. Nanson P.E. pote �
Drainage Calculations
MGSFIood Calculations
MGS FLOOD
PROJECT REPORT
Program Version:3.13 Run Date:07/20/2011 9:17 AM
Input File Name: Strander July 2011_Phase2.fld
Project Name: STRANDER EXTENSION
Analysis Title:
Comments: shallow pond, 3ft detention, 3 orifice
***"'*"`*'`*Precipitation Input'"`*"'""`**'`
Extended Precipitation Timeseries Selected
Climatic Region Number: 13
Full Period of Record Available used for Routing
Precipitation Station :960040 Puget East 40 in MAP 10/01/1939-10/01/2097
Evaporation Station 961040 Puget East 40 in MAP
Evaporation Scale Factor 0.750
HSPF Parameter Region Number:1
HSPF Parameter Region Name :USGS Default
""""`"Default HSPF Parameters Used(Not Modified by User)"""""""'
1of23
**********Watershed Definition '`*"*******
Number of Subbasins: 1
***"'*'*'Subbasin Number: 1'"'*"'***'
"'Tributary to Node: 1
"'Bypass to Node None
-----------•----•------------Area(Acres)---------------------
------------D ev e I o pe d------------
Predeveloped To Node Bypass Node
Tiii Foreet s.zso o.000 _.coc �
Till Pasture 0.000 0.000 G.QOG
Till Grass 0.000 0.000 0.000
Outwash Forest 0.000 0.000 0.000
Outwash Pastnre 0.000 0.000 0.000
Outwash Grass 0.000 2.250 0.000
wetland D.000 D.000 0.000
Impervicus O.Q00 3.Q00 0.000
Subbasin Total 5.250 5.250 0.000
-------------------------Lateral Flow Connnections-------------------------- i
----------Predeveloped---------•---- ------------Developed---------------
Surface Interflow Grnd Water Surface Interflow Grnd Water
Till Forest Node Node Ncde Node
Till Pasture Node Node Node Voce
Till GrGss Node Node Ncde Ncae
Outwasl: Fcres: Vode Node Node Node
Outwash Pasture Node Node No6e Node
Outwash Grass Node °7ode Node Node
Wet'�and Node Vode Node Node
Impervious Node Node I
La�eral 1
La�eral 2
*** Subbasin Connection Summary*"'`
Subbasin 1 -------------->Node 1 I
"'* By-Pass Area Connection Summary *'" I'�
No By-Passed Areas in Watershed
*"*Postdeveloped Node Connection Summary'*'
Upstream Node No. Link Type Downstream Node
Node 1 Pond Node 2
Predeveloped Compliance Node: 1
Postdeveloped Compliance Node: 2
2of23
i
I
*** Postdeveloped Structure Summary'`'`'`
Link No. 1,Pond: Stormwater Wetland-Shallow Pond 3 orifice
Upstream Node: 1, Downstream Node:2
User Specified Elevation Volume Table Used
Elevation(ft) Pond Volume(cu-ft)
23.70 �.
24.00 6392.
25.00 29073.
26.00 53923.
26.70 72651.
27.00 81016.
Hydraulic Conductivity . 0.00 in/hr
Depth to Water Table . 3.00 ft
Potential for Bio-Fouling :Average to High
Maintenance :Poor
Riser Geometry
Riser Structure Type :Circular
Riser Diameter 18.00 in
Common Length :0.000 ft
Riser Crest Elevation 26.70 ft
Hydraulic Structure Geometry
Number of Devices: 3
---Device Number 1 ---
Device Type : Circular Orifice
Invert Elevation . 24.00 ft
Diameter . 1.13 in
Orientation :Horizontal
Elbow :No
--Device Number 2---
Device Type : Circular Orifice
Invert Elevation . 24.50 ft
Diameter . 1.12 in
Orientation :Horizontal
Elbow Yes
--Device Number 3--
Device Type : Circular Orifice
Invert Elevation . 26.00 ft
Diameter . 1.25 in
Orientation :Horizontal
Elbow :Yes
3of23 II!
*"`'`**'`*'`*''Postdeveloped Hydraulic Rating Table'`********""'`'
Postdeveloped Link: 1
Elev(ft) Storage(ac-ft) Discharge(cfs) Infilt Discharge(cfs)
2a.�oo o.000 o.000 o.00c
23.715 0.007 0.000 O.00C
23.730 0.015 0.000 0.000
23.760 0.029 0.000 0.000
23.820 0.059 0.000 O.00O
23.880 0.088 0.000 O.00G
23.940 O.i17 0.000 O.00O
23.955 0.125 0.000 O.00O
23.970 0.132 0.000 O.00O
23.985 0.139 0.000 O.00G
24.000 0.147 0.000 O.00O
24.015 0.155 0.004 O.00O
24.030 0.162 0.006 O.00O
24.045 0.170 0.007 D.00G
24.060 0.176 0.008 D.OQO
24.120 0.209 0.012 O.OQD
24.180 0.240 0.014 O.OQU
24.240 0.272 0.017 O.00G
24.300 0.303 0.018 O.OQG
24.360 0.334 0.020 O.00G
24.420 0.365 0.022 0.000
24.440 0.376 0.022 O.00G
24.460 0.386 0.023 O.00G
24.480 0.397 0.023 O.00G
24.500 0.407 0.024 O.00G
24.515 0.415 0.028 D.000
24.530 0.423 0.030 0.000
24.545 0.431 0.032 O.00C
24.560 0.438 0.033 O.OGu
24.620 0.470 0.038 O.00C
24.660 0.501 0.041 O.00C
24.740 0.532 0.045 0.000
24.800 0.563 0.048 O.00C
24.860 0.595 0.050 O.00C
24.920 0.626 0.053 O.00C
24.980 C.657 0.055 O.00C
25.040 C.690 0.058 O.00C
25.100 0.724 0.060 O.00C
25.160 0.759 0.062 O.ODC
25.220 0.793 0.064 O.00C
25.280 0.827 0.066 O.00C
25.340 0.861 0.066 0.000
25.400 O.S96 0.070 0.000
25.460 0.930 0.072 0.000
25.520 0.9E4 0.074 0.000
25.580 0.998 0.075 O.00Q
25.640 1.033 0.077 0.000
25.700 1.067 0.079 O.00G
25.760 1.101 0.080 0.000
25.820 1.135 0.082 O.00G
25.880 1.169 0.084 O.00G
25.940 1.204 0.085 D_000
25.955 1.212 0.086 0.000
25.970 1.221 0.086 O.00v
25.985 1.229 0_066 0_OCG
26.000 =.238 0.087 O.00O
26.015 '�.247 0.092 O.00G
26.030 ;.256 0.094 O.00G
26.045 �.266 0.096 0.000
26.060 i.275 0.098 0.000
26.120 1.3�2 0.103 0.000
26.160 1.348 0.108 D.00G
26.240 1.365 0.112 O.OQO
26.300 1.422 0.116 D.OQO
�c�.�6n 1.459 0.11° O.00O
.-._ . _.__ _.-��_ 0._.._ L.L�C._
4of23
26.42G �.533 C.=25 O.00i;
26.540 1.570 0.126 O.00C
26.600 1.606 0.131 O.00C
26.625 1.622 0.132 O.COG
26.650 1.637 0.134 0.00��
26_675 1.652 0.135 O.00G
26.700 1.E68 0.13E O.00O
26.715 1.677 0.166 O.OGO
26.730 1.667 0.220 O.OGO
26.745 1.697 0.290 O.00C
26.760 1.706 0.372 O.00C
26.775 1.716 0.466 O.COC
26.790 1.725 0.569 0.00:
26.805 1.735 0.661 0.000
26.820 1.745 0.800 O.00�
26.880 1.763 ;.347 D_OC
26.940 1.821 1.975 0.000
27.000 1.660 2.650 0.000
27.060 1.900 3.337 O.OGU
27.120 1.941 4.00'_ O.00C
27.180 1.981 4.610 O.00C
27.240 2.021 5.135 0.00��
27.300 2.062 5.561 O.00C
27.360 2.102 5.866 O.00G
27.420 2.142 6.131 O.00G
� , .48p �.1g3 6.42� _.��r��
.., .5�(_; ...�_,_ �.�--- ,. .�:.�
5 of 23
*** Post-Developed Link Statistics ***
Postdeveloped Pond Water SurFace Elevation Statistics
Annual Maxima Water Surface Elevation(ft)
Link: 1
Max Date WSEL (ft)
i2/07/1939 25.234
O1/18/1941 24.774
12/20/1941 24.864
11/15/1942 25.Q68
10/17/1943 24.70s
02/07/1945 25.341
02/O5/194E 24.888
11/16/1946 24.585
10/19/1947 25.348
02/22/1949 25.057
03/OS/1950 25.245
02/09/1951 25.487 ',
10/02/1951 24.826 ��
O1/11/1953 25.20=
O1/06/1954 24.436 j
11/19/i954 24.91� '
O1/06/1956 25.263 ',
02/26/"�957 25.069 i
O1/17/i958 25.056 I
O1/13/1959 25.2�9 �
11/21/i959 25.3�6
11/24/":960 25.232
03/OS/i962 24.775
02/03/i963 24.81G
O1/O1/1964 24.8E0
� 12/O1/i964 24.975
12/28/1965 24.95?
12/13/1966 25.234
10/27/1967 25.OE2
12/03/1968 24.915
O1/27/1970 24.9E?
12/07/1970 25.1?c
03/OS/1972 25.73c
12/23/1972 25.249
O1/16/1974 24.9E5
12/27/1974 25.0?�
12/04/1975 25.07=
08/26/1977 25.8E=
12/15/1977 25.23�
03/O5/1979 2�.741
12/18/1979 26.031
12/30/1980 2�.961
10/06/1981 25.864
O1/OS/1983 25.033
03/21/1984 24.86=
11/04/1984 24.862
Ol/18/1986 25.42c
11/24/1986 25.81°
04/06/1988 25.115
04/OS/1989 25.095
Ol/09/1990 25.918
11/24/1990 25.838
0":/'sl/1992 25.186
0's/23/1993 24.737
Q3/03/1994 24.876
12/27/1994 25.191
02/09/1996 26.G87
Oi/02/1997 25.8_4
10/OS/1997 24.&"1
11/26/1996 25.808
C2,r'26;2000 24.?69
cs;os%zoci z�.�ee;
6of23
11/15/2001 24.854
11/26/2002 25.607
10/24/2003 25.':50
02/07/2005 24.889
11/27/2005 25.281
11/27/2006 24.914
O1/07/2008 25.298
02/18/2009 25.853
O1/10/2010 25.224
11/17/2010 25.538
10/02/2011 25.280
O1/20/2013 25.601
� 01/27/2014 25.:28
03/30/2015 24.880
O1/07/2016 25.570
11/O1/2016 25.C13
O1/31/2018 25.C84
O1/12/2019 25.168
03/31/2020 24.821
02/10/2021 25.522
12/20/2021 25.089
03/30/2023 25.183
O1/19/2024 25.151
12/24/2024 25.626
O1/04/2026 25.255
O1/28/2027 24.976
02/19/2028 25.113
12/10/2028 25.034
O1/26/2030 25.421
12/30/2030 25.124
O1/21/2032 25.465
12/23/2032 25.004
01/16/2034 25.957
02/19/2035 25.046
02/27/2036 25.OE4
08/25/2037 24.593
12/15/2037 25.193
:2/04/2038 24.724
O1/14/2040 25.141
12/25/2040 25.335
11/17/2041 25.162
OB/30/2043 25.012
03/21/2044 24.811
03/27/2045 25.031
02/17/2046 25.085
02/02/2047 24.955
'�2/C4/2047 25.355
_1/25/2048 24.875
12/04/2049 25.024
04/06/2051 24.851
C4/17/2052 24.736
12/10/2052 24.965
12/11/2053 24.960
11/Ol/2054 25.685
02/OB/2056 26.213
11/19/2056 25.970
OS/21/2058 25.076
=1/26/2058 25.399
OS/27/2060 24.785
O1/10/2061 25.105
O1/03/2062 25.013
12/30/2062 25.151
12/23/2063 25.483
12/C1/2064 24.998
O1/13/2066 24.75�
12/15/2066 25.123
O1/19/2068 25.493
09/23/2069 24.83c
04/09/2070 24.77G
02;�14/2071 24.7�?
--. _i3;_�"1 25._�6
7of23
=2/26j2072 26.15C
=2/15/2073 25.231
=1/20/2074 24.839
"_0/17/2075 25.474
08/26/2077 24.648
12/02/2077 24.947
02/25/2079 24.783
12/17/2079 26.082
11/21/2080 25.438
C2/15/2082 25.302
C2/20/2083 25.i38
11/18/2083 25.481
12/14/2084 25.089
Oi/18/2086 25.074
1�/23/2086 25.267
12/09/2087 24.970
li/OS/2086 25.401
11/04/2089 25.105
12/09/2090 25.522
O1/31/2092 25.499
11/07/2092 24.786
10/23/2093 24.823
11/30/2C94 25.024
12�14�2C95 25.C27
D3/13i2C97 25.345
�
�
8 of 23 ���
Postdeveloped Ranked Annual Maxima Water Level(ft)
Tr(yrs) Link: 1
i.co 24s��
1.01 24.64=
1.02 24.7C3
1.02 24.72-
1.03 24.73E
1.04 24.73-
1.04 24.7_-
1.05 24.7E-
1.06 24.77u
1.06 24.774
1.07 24.776
1.08 24.783
1.09 24.785
1.09 24.78E
1.10 24.791
1.11 24.81C
1.i2 24.811
1.12 24.811
1.13 24.821
1.14 24.823
1.15 24.82�
1.16 24.83�
1.17 24.83°
1.18 24.851
1.18 24.85=
1.19 24.86��
1.20 24.862
1.21 24.864
1.22 24.864
1.23 24.865
1.24 24.875
1.25 24.876
1.26 24.880
1.27 24.68=
1.28 24.888
1.29 24.889
1.30 24.9L"
1.31 24.914
1.32 24.918
1.33 24.93�
1.35 24.9<�
1.36 24.95�
1.37 24.9�"
1.38 24.96
1.39 24.��
1.40 24.9=
1.42 24.3E"
1.43 24.9>
1.44 24.9�
1.4E 24.9"'
1.47 24.°"'
1.48 24.°"'
1.50 24.04
1.51 24.°F
1.53 25.G,
1.54 25_G
1.56 25.0
1.57 25.G"
1.59 25.0:
1.60 25.D:
1.62 25.G:
1_64 25.G-�
1.65 25.0-
1.67 25.Os�
1.69 25.046
1.71 25.056
1.73 25.056
1.75 25.057
9of23
1.77 25.062 !i
1.79 25.064
1.81 25.074 '
1.83 25.074
1.85 25.076
1.87 25.079
1.89 25.084
1.92 25.085
1.94 25.088 ��,,
:.96 25.0fi9 '
_.99 25.08�
2.01 25.089 I
2.04 25.094 '�
2.07 25.105
2.09 25.105
2.12 25.113
2.15 25.115
2.18 25.123
2.21 25.124
�.24 25.i26
�.27 25.138
�.3i 25.141
2.34 25.150
�.?8 25.151
�.41 25.151
�.45 25.168
2.49 25.176
2.53 25.182
2.57 25.183
2.61 25.18E
2.65 25.191
2.70 25.193
2.75 25.201 �
�.80 25.207 i
�.85 25.224 ���
�.90 25.229 ���
�.95 25.230
: .Dl 25.23i
-�.D7 25.232
�.13 25.234
: .:9 25.234
3.26 25.245
3.32 25.255
3.40 25.263
3.47 25.260
3.55 25.261
3.63 25.298
3.72 25.299
3.80 25.302
3.90 25.328
4.00 25.335
4.10 25.341
4.21 25.346
4.32 25.348
4.45 25.355
4.58 25.399
4.71 25.401 ,
d.86 25.421
5.01 25.428 '
5.:7 25.438 �
5.35 25.465
5.54 25.474
�.74 25.481
5.95 25.483
e.19 25.467
�.44 25.493
�.71 25.499
7.01 25.522
7.33 25.522
?.F9 25.570
E.�B 25.6C"%
10 of 23
_ .52 25.638
�.00 25.685
?.55 25.736
:0.16 25.801
1C.86 25.908
11.6E 25.814
12.59 25.919
13.68 25.826
14.97 25.838
16.54 25.853
:8.47 25.864
�0.92 25.918
:.4.10 25.957
�8.44 25.970
?4.68 26.031
Y4.42 26.082
�1.77 26.087
101.36 26.150
:82.35 26.213
11of23
Postdeveloped Water Surface Elevation Data(ft)
Recurrence Interval Computed Using Gringorten Plotting Position
Tr(yrs) Link: 1
:.OS-Year 24.7�a I
1.11-Year 24.812 '�
1.25-Year 24.8?6 I
2.00-Year 25.C5� ��
3.33-Year 25.�55
5-Year 25.=38
10-Year 25.?88
25-Year 25.5°f
50-Year 26.02"
100-Year 26._47
Postdeveloped Infiltrated Water Statistics �
Volume Statistics Computed for Entire Simulation
Statistic Link: 1
Totai Inflow Volume (ac-fc) 131�
Total Volume Infiltrated (ac-Ft? 0.
Percent Infi=trated C.CC <
*'"`""`*"'**''*Water Quality Facility Data'`**'*'`*"*`'*"'`
Node No: 1
Basic Wet Pond Volume(91%Exceedance): 13048.cu-ft
Computed Large Wet Pond Volume, 1.5`Basic Volume: 19571.cu-ft
2-Year Discharge Rate :0.780 cfs
15-Minute Timestep,Water Quality Treatment Design Discharge
On-line Design Discharge Rate(91%Exceedance): 0.46 cfs
Off-line Design Discharge Rate(91%Exceedance): 0.26 cfs
Node No:2
Basic Wet Pond Volume(91%Exceedance): 4119. cu-ft
Computed Large Wet Pond Volume, 1.5'Basic Volume: 6178.cu-ft
2-Year Discharge Rate :0.060 cfs
12 of 23
"*"*'`**''*'"'Compliance Point Results **'"`*''`****'`**
Predeveloped Compliance Node: 1
Postdeveloped Compliance Node: 2
"Point of Compliance Annual Maxima Flow Data"
Predevelopment Runoff Postdevelopment Runoff
Date Mnual Max Q(cfs) Date Annual Max Q(cfs)
G4i?0!1940 0.142 12/Q7;'1539 0.065
C1/3_/1941 0.055 G"�/16/1941 0.046
12/15/1941 0_143 12/20/1941 0.051
02/10/1943 0.057 li/15/1942 O.OEO
Q1/23/1944 0.043 10/17/1543 0.043
02/07/1945 0.177 02/07/1945 0.068
02/OS/1946 0.109 02/O5/1546 0.052
02/02/1947 0.111 11/16/1546 0.056
03/21/1946 0.191 10/19/1947 0.068
02/22/1949 0.096 02/22/1449 0.058
03/03/1950 0.395 03/OS/1950 0.065
02/09/1951 0.158 02/09/1951 0.073
0�/24/1952 O.Q42 10/02/1951 0.049
Q�/11/1953 0.059 O1/11/1953 0.064
G_/22/1954 0.096 O1/06/1954 0.054
G4/i2/1955 0.045 11/19/1954 0.053
03/04/1956 O.1D3 O1/06/1956 0.066
C�2/25/1957 0.065 02/26/1457 0.060
Oi/'�6/1958 0.103 O1/17/1958 0.058
C�l/12/1959 0.11"i O1/13/1959 0.065
12/15/1959 0.119 11/21/1959 0.068
��2/i4/1961 0.102 11/24/1960 0.065
��3;OS/1962 0.054 03/OS/1962 0.046
��2!03/1963 O.D60 02/03/1963 0.048
Gl/O1/1964 0.097 O1/O1/1°64 0.050
D2/2E/1965 0.120 12/Ol/"_964 0.055
Ul/OE/1966 0.074 12/26/i965 0.055
O1/19/1967 0.167 12/13/196E 0.065
�2/03/1968 0.097 10/27/i967 0.059
:2/03/1968 0.104 12/03/=968 0.053
U1/13/1970 0.060 O1/27/1970 0.055
:2/06/1970 0.091 12/07/1970 0.063
U2j2g/1972 0.247 03/O5/1972 0.080
U1/13/1973 0.069 12/23/1972 0.067
02/18/1974 0.133 O1/16/i974 0.055
=2/26/1974 0.161 12/27/1974 0.059
O1/27/1976 0.111 12/04/1975 0.059
OS/31/1977 0.016 08/26/1977 0.051
=2/10/1977 0.094 12/15/i977 0.065
03/C4/1979 0.093 03/OS/1979 0.047
_2/17/1979 0.150 12/18/i979 0.094
_2/26/1960 0.059 12/30/196Q 0.055
=�/06/1961 0.190 i0/06/1961 0.083
Ol/OS/1963 0.106 O1/OS/1963 0.058
03/14/1984 0.102 03/21/1964 0.051
0�/11/1985 0.065 11/D4/1964 0.050
01/18/198E C.224 O1/18/198E 0.071
i1/24/198E 0.19^ 11/24/196E 0.082
04/Q6/1988 0.095 04/06/1968 0.061
r,�j05/1989 0.109 04/OS/1969 0.060
01/09/1990 0.358 Ol/09/1990 0.085
11/24/1990 0.305 11/24/1990 0.083
r,1/27/1992 0.093 O1/31/1992 0.063
05/09/1993 0.079 03/23/1993 0.044
0?/03/1994 0.060 03/D3/1994 0.051
02/19/1995 0.�25 12/27/1994 O.OE3
02/09/1996 0.290 02/09/1996 0.100
01/02/1997 0.182 O1/02/1997 0.082
02/28/1998 0.067 i0/08/1997 0.048
11/25/1998 C.:79 :1/26/''_998 0.082
C3;'26!2000 0._CO 02/28i2000 0.055
13 of 23
os/os/zooi o.o�� os/os/zooi o.osi
os/oa/zooz o.a�a ii/is/aooi o.oso
03/31/2003 0.210 �1/26/2002 0.076
Ol/23/2004 0.051 i0/24/2003 0.062
oz/o�/zoos o.osa oz/o�/zoos o.osz
02/27/2006 0.113 11/27/2005 0.066
_2/14/20D6 0.084 11/27/2006 0.053
03/21/2008 0.139 Ol/07/2008 D.067
02/17/2009 0.216 02/18/2009 0.063
oi/io/2oio c.��as oi/io/2oio 0.064
_i/i�/zolo o.-_a9 ii/1�/zaio o.o��
oi/3i/zoiz o.�_zo 1o/oa/aoii 0.066
O1/20/2013 0.274 O1/20/2013 0.082
=2/06/2013 0.115 Ol/27/2014 0.061
03/30/2015 0.070 03/30/2015 D.O51
01/04/20i6 0.199 Ol/07/2016 0.075
c�/o�/zoi� o.osa ii/oi/zoi6 o.os�
ci/si/zola o.io� oi/ai/zoia o.os9
C3/30/2019 0.106 O1/12/2019 0.063
04/14/2020 0.07C 03/31/2020 0.049
c2/io/zozi o.i�3 oz/io/zoai o.0�4
c�/z6/zozz e.osi 12/2o/zozi o.060
0?/30/2023 0.123 03/30/2Q23 0.063
C1/19/2024 0.097 Ol/19/2024 0.062
iz/zz/zo24 o.2cz iz/z4/zoz� o.oez
C3/09/2026 0.128 O1/04/202E 0.065
ci/2�/zoz� o.li2 oi/ze/zoz� o.oss
C2/19/2028 0.138 02/19/2028 0.061
iz/oa/zoza o.lo� iz/io/zoza D.058
C2/16/2030 0.143 O1/26/2030 0.071
12/30/2030 0.134 12/30/2030 D.061
c_/zo/zosz o.zis oi/zi/zosz o.0�2
03/Ol/2033 O.OE1 12/23/2032 0.056
Q-/15/2034 0.253 O1/16/2034 0.086
Q2/19/2035 0.119 Q2/19/2035 D.058
03/24/2036 0.112 Q2/27/2036 0.059
03/09/2037 4.591E-03 08/25/2037 0.036
12/"�5/2037 0.082 12/15/2037 0.063
02/07/2039 0.059 12/04/2038 0.044
�l/14/2040 0.222 Ol/14/2040 0.062
12/25/2040 0.126 12/25/2040 0.068
G2/2C/2042 0.132 ll/17/2041 0.063
03/31/2043 0.199 OS/30/2043 0.057
O5/O1/2044 O.C7B 03/21/2044 D.048
02/11/2045 O.C90 03/27/2045 0.057
02/16/2046 0.114 02/17/2046 0_059
02/O1/2047 0.071 02/02/2047 0.054
04/21/2048 0.063 12/04/2047 D_069
03/16/2049 0.071 11/25/2048 D.O51
12/04/2049 D.120 12/04/2049 0.057
04/OE/2051 0.093 04/06/2051 0.050
04/17/2052 0.056 04/17/2052 0.044
06/04/2053 0.216 12/10/2052 0.055
o�/oa/zos4 0.04o iz/ii/zos? o.oss
az/i�/zoss o.ies 11/O1/2054 o.o�a
oz/o�/aos6 0.33� oz/oa/zos6 o.iio
:l/19/2056 0.365 11/19/2056 0_086
O1/24/2058 0.127 OS/2i/2058 0.059
_2/28/2056 0.145 11/26/205& 0.070
O1/19/2060 0.054 O5/27/2060 D.047
O1/10/2061 0.118 O1/10/2061 0.060
02/03/2062 0.450 Ol/03/2062 0.057
=2/29/2062 0.095 12/30/2062 0.062
_2/23/2063 0.172 12/23/2063 0.073
_1/30/2064 0.062 12/Ol/2064 0.056 �
O1/13/2066 0.045 O1/13/2066 D.045
O1/19/2067 0.114 12/15/2066 0.061
O1/18/2066 0.236 O1/19/2068 0.073
O1/Q4/2069 0.063 09/23/2069 0.049
0-/09/2070 O.Q53 04!09/2070 0.046
0�;'14i�2C?i G.���54 .. ;'14r'2G"1 ,,.046
14of23
02i�27;2C72 C.063 -1/03i�207- O.C58
iz/zs/za�z o.z6z �z/z6/2o�z o.ioE
03/16/2074 0.141 12/15/2073 0.05�
O1/23/2075 0.030 11/20/2074 0.04�
03/24/2076 o.ls� lo/i�/zo�s o.o�z
03/02/2077 0.018 08/26/2077 0.03�
�2/oz/2o�� a.oss i2/oz/zo�� o.os�
02/25/2079 0.075 02/25/2079 0.047
12/17/2079 0.293 12/17/2079 Q.100
ii/zi/zoso o.iz5 ii/ai/zoso o.o�i
02/13/2062 0.161 02/i5/2082 0.067
02/19/2063 0.095 02/20/2083 0.061
11/26/2063 0.12C 11/18/2083 Q.073
12/14/2084 0.083 12/14/2084 0.060
oi/is/zoeE o.ii� oi/�a/zoa6 o.osQ
12/21/2086 0.110 11/23/2086 0.06�
oi/i4/aosa o.o7z iz/o9/zoa� o.os=_
ii/os/zosa o.iza li/os/zoae o.o�c
01/07/2090 0.060 11/04/2089 0.06C
12/04/2090 0.112 12/09/2090 0.07�
04/28/2092 0.191 O1/31/2092 O.C73
03/22/2093 0.05� 11/07/2092 0.047
03/Ol/2094 0.045 10/23/2093 0.045
oz/is/zo9s o.o7i 11/30/2044 o.cs�
O1/14/2096 0.090 12/i4/2095 O.C57
C1/29!20g? 0.1°7 03/_4i204' C.C58
15 of 23
"**Point of Compliance Ranked Maxima Flow Data"'* I
Predevelopment Postdevelopment I
Tr(yrs) Q(cfs) Tr(yrs) Q(cfs) I
1.00 4.591E-C3 '_.00 3.554E-02 I
1.01 0.016 1.01 O.G34 I
1.02 0.018 1.02 O.Q43 �I
1.02 C.030 1.02 0.04� I
1.03 0.040 i.03 0.04= I
1.04 0.042 i.04 O.G44 ��
1.04 0.043 1.04 O.G45 i
1.05 0.045 1.05 0.04=� I
1.06 O.C45 1.06 O.G4o
1.06 0.045 1.06 0.0�5
1.07 0.051 1.07 O.G<o
1.08 D.O51 1.08 0.0�?
1.09 0.053 1_09 0.0�"%
1.09 0.054 1.09 0.0="'
1.10 0.054 1.10 0.0�"
l.11 0.054 l.11 0.048
1.12 0.055 1.12 0.048
1.12 0.056 1.12 0.048
1.13 0.057 1.13 O.OY9
1.14 0.058 1.14 O.C49
1.15 0.059 1.15 O.C-;S
1.16 0.059 1.16 O.C�:
1.17 0.059 1.17 O.C4�
1.i8 0.059 1.18 O.CSC
1.18 0.059 ',.18 O.C5C
1.19 C.OEO i.19 O.C�?
1.20 0.060 i.20 O.GS;
1.21 Q.060 1.21 0.?S_
1.22 0.06: 1.22 O.OE_
1.23 0_063 1.23 0.��5:
1.24 0.063 1.24 0.��5'_
1.25 0.063 1.25 O.GS:
1.26 0.067 1.26 0.05=
1.27 0.068 1.27 O.DS:
1.28 0.070 1.28 0.0-�
1.29 0.070 1.29 0.0=�
1.30 0.071 1.30 0.0-�
1.31 0.071 1.31 O.G='
1.32 0.071 1.32 0.0=:
1.33 0.072 1.33 O.U=�
1.35 0.074 1.35 0.0 �
1.36 0.077 1.36 O.G��
1.37 0.078 1.37 0.0=F
1.38 0.079 1.38 O.C=�.
1.39 0.079 1.39 O.C-�
1.40 0.080 1.40 O.C==
1.42 0.082 L.42 O.C��
1.43 0.082 1.43 O.C55
1.44 0.083 1.44 0.�:;5=
1.46 0.084 1.46 O.C55
1.47 0.065 1.47 0.055
1_46 D.088 1.48 O.Q55
1.50 0.069 1.50 0.056
1.51 0.090 1.51 0.056
1.53 0.090 1.53 0.05�
1.54 0.091 1.54 0.05?
1.56 0.093 1.56 0.05?
1.57 0.093 1.57 0.05?
1.59 O.D93 1.59 0.05?
1.60 0.094 1.60 O.G57
1.62 0.095 1.62 0.05?
1.64 0.09E 1.64 O.GS?
1.65 0.09E 1.65 0.0�5
1.67 0.097 1.67 0.055
_.6? p.04? l.c� 0.055
16of23
1.71 0.097 1.71 0.058
1.73 0.098 1.73 0.056
1.75 0.099 1.75 0.056
1.77 0.100 1.77 0.059
1.79 0.102 1.79 0.059
1.81 0.'�02 :.81 0.059
1.83 0.103 1.83 0.059
1.85 O.iO3 1.85 0.059
1.67 0.104 1.87 0.059
1.69 0.106 1.99 0.059
1.92 0.106 1.92 0.059
1.94 0.107 1.94 0.060
1.96 0.107 1.96 0.060
1.99 0.109 1.99 0.060
2.01 0.109 2.01 0.06C
2.04 0.1-0 2.04 0.060
2.07 0.1-;1 2.07 0.060
2.09 0.111 2.09 0.060
2.12 0.111 2.12 0.061
2.15 0.112 2.15 0.061
2.18 0.112 2.18 0.061
2.21 0.112 2.21 0.061
2.24 0.113 2.24 0.061
2.27 0.114 2.27 0.061
2.31 0.114 2.31 0.062
2.34 0.115 2.34 0.062
2.38 0.117 2.38 0.062
2.41 0.118 2.41 0.062
2.45 C.'�19 2.45 D.OE3
2.49 Q.119 2.49 0.063
2.53 Q.120 2.53 0.063
z.s� o.izo z.s� o.oE�
2.61 0.120 2.61 0.063
2.65 0.120 2.65 0.063
2.70 0.123 2.70 0.063
2.75 0.125 2.75 0.064
2.80 0.126 2.80 0.054
2.85 0.127 2.85 O.C64
� 2.90 0.128 2.90 O.C65
2.95 0.128 2.95 O.C65
3.01 0.129 3.01 0.065 �'I
' 3.07 0.132 3.07 0.065
3.13 0.133 3.13 0.065
3.19 0.134 3.19 0.06�
3.26 0.138 3.26 0.065
3.32 0.139 3.32 0.065
s.40 0.141 3.40 0.066 I
3.47 0.142 3.47 0.06E
3.55 0.143 3.55 0.06E
3.63 0.143 3.63 0.067
3.72 O.1S5 3.72 0.067
3.80 0.145 3.80 0.067
3.90 0.150 3.90 0.068
4.00 0.157 4.00 0.068
4.10 D_158 4.10 O.OEB
4.21 0_16�_ 4.21 O.OEB
4.32 0.16i 4.32 0.065
4.45 0.172 4.45 O.Oc9
4.56 0.173 4.58 0.070
4.71 0.177 4.71 0.0?0
4.86 0.179 4.86 0.07_
5.01 0.182 5.01 0.0?=
, 5.17 0.183 5.17 0.0 Z
' S.35 0.167 5.35 O.C?2
5.54 0.189 5.54 O.C?2
5.74 0.190 5.74 O.C?3
5.95 0.191 5.95 O.C?3
6.19 0.191 6.19 O.C��
6.44 0.197 6.44 O.C?�
6.71 0.197 _ .?1 O.C?;
.Gl �.-- . .��1 �.� _
17 of 23
7.33 ��.1�9 7.33 O.C?4
7.69 0.202 7.69 O.C?5
8.08 0_210 8.08 O.C?E
8.52 0.215 8.52 O.C?7
9.00 0.216 9.00 O.C,�
9.55 0.216 9.55 O.C6C
10.16 0.222 10.16 O.C82
10.86 0.224 10.86 O.C82
11.66 0.236 11.66 0.08�
12.59 0.243 12.59 O.QB�
13.68 0.247 13.68 0.08�
14.97 0.262 14.97 0.�:�83
16.54 0.274 1E.54 0.083
18.47 0.274 18.47 O.G83
20.92 0.290 20.92 0.08�
24.10 0.293 24.10 0.0�5
28.44 C.305 28_44 0.02_
34.66 0.333 34.66 0.0�-1
44.42 0.356 44.42 0.=��U
61.77 0.3E5 61.77 0._GO
_ _.?F , .3?5 1C�1.35 0.=�6
�_�.�5 ��.4=U 3E'.2.�6 0.-10
18of23
i
•"Point of Compliance Flow Frequency Data"'
Recurrence Interval Computed Using Gringorten Plotting Position
Predevelopment Runoff Postdevelopment Runoff
Tr(Years) Discharge(cfs) Tr(Years) Discharge(cfs)
2-Year 0.109 2-Year 0.060 �
5-Year 0.181 5-Year 0.071
10-Year 0.221 10-Year 0.081� ;:.3 ' 9Y'/
25-Year 0.296 25-`!ear 0.066
50-Year 0.361 50-Year 0.100 .�Z !� M
100-Year 0.394 100-Year 0.105 � �1" J�
200-Year 0.431 200-Year 0.109
** Record too Short to Compute Peak Discharge for These Recurrence Intervals
19 of 23
"'Point of Compliance Flow Duretion Data"'
Predevelopment Runoff Postdevelopment Runoff
Discharge Exceedance Discharge Exceedance
(cfs) Proba bil ity (cfs) Proba bi I ity
O.O00E+00 1.00OCE+00 O.O00E+00 1.00CDE+�_
2.248E-03 2.3690E-01 5.505E-04 7.134EE-C.=
4.496E-03 1.6183E-01 1.lO1E-03 6.8643E-i;:
6.744E-03 1.4869E-01 1.651E-03 6.7231E-0:
8.992E-03 1.2486E-01 2.202E-03 6.6015E-C:
0.011 1.0625E-01 0.003 6.SO11E-?=
0.013 9.1206E-C2 0.003 6.41E3E-C-
0.016 7.8997E-02 0.004 6.3431E-C=
0.018 6.8893E-02 0.004 6.2357E-C-
0.020 6.0447E-02 0.005 6.0934E-�=
0.022 5.3261E-02 0.006 5.9649E-G-
0.025 4.7"_'ISE-02 0.006 5.6325E-6=
0.027 4.1832E-02 0.007 5.6893E-0=
0.029 3.7205E-02 0.007 5.5532E-��=
0.031 3.3133E-02 0.008 5.4018E-2:
0.034 2.9638E-02 0.008 5.2601E-G_
0.036 2.64's0E-02 0.009 5.0884E-U:
0.038 2.3649E-02 0.009 4.9226E-G:
0.040 2.1262E-02 0.010 4.7638E-G_
0.043 1.9150E-02 D.O10 4.6112E-G;
0.045 1.7267E-02 0.011 4.4671E-C1
0.047 1.5521E-02 0.012 4.3294E 0_
0.049 1.4036E-02 0.012 4.1702E-r�
0.052 1.2639E-02 0.013 4.0082E-C".
0.054 1.1278E-02 0.013 3.8512E C=
0.056 1.0348E-02 0.014 3.6998E-��-
0.058 9.4640E-0? 0.014 3.5528B-C=
0.061 8.5860E-03 0.015 3.3865E-C-
0.063 7.6�78E-03 0.015 3.2259E-C:
0.065 7.1543E-03 0.016 3.0699E-5=
0.067 6.5998E-03 0.017 2.9216E-CC
0.070 6.0469E-03 0.017 2.7590E-�:
0.072 5.5507E-03 0.018 2.6020E-�=
0.074 5.1067E-03 0.018 2.4465E-�=
0.076 4.7255E-03 0.019 2.2965E-G=
0.079 4.3558E-03 0.019 2.1410E-G�
0.081 4.0223E-03 0.020 1.9900E-G1
0.083 3.7104E-03 o.ozo 1.8435E-G':
0.085 3.4331E-03 0.021 1.6957E-01
0.088 3.1833E-03 0.021 1.5538E-01
0.090 2.9472E-03 0.022 1.4127E-C'.
0.092 2.7284E-03 0.023 1.2686E-C�
0.094 2.5234E-03 0.023 1.1287E-C:
0.097 2.3581E-03 0.024 9.9528E-C�
0.099 2.1942E-03 0.024 9.3706E-C�
0.101 2.03245-03 0.025 9.2545E-C�
0._03 1.9003E-03 0.025 9.1429E-C:
0.106 1.7624E-03 0.026 9.0336E-02
0.109 1.6051E-03 0.026 8.9275E-0�
0.110 1.5285E-03 0.027 6.8189E-Q�
0.112 1.4180E-03 0.028 8.7156E-�:
0.115 1.3350E-03 0.028 8.6159E-�2
0.117 1.2722E-03 O.D29 8.4159E-��
0.119 1.2043E-03 0.029 8.2064E-�^
0.121 1.1350E-03 0.030 8.0079E-���
0.124 1.0729E-03 0.030 7.8019E-02
0.126 1.0130E-03 0.031 7.5756E-02
0.128 9.6532E-04 0.031 7.3525E-02
0.130 9.1478E-04 0.032 7.1255E-02
0.133 8.6712E-04 0.032 6.8907E-G�
0.135 8.1225E-Q4 0.033 6.6598E-G_
0.137 7.6388E-04 0.034 6.4039E-C_
D.i39 7.2469E-04 0.034 6.1570E-0_
0.=�2 6.88073-p4 0.035 5.9201E-C�
-�-=� �--�4� " � -- _ '�'-� �_
20 of 23
0.146 6.2092E-04 0.036 5.4698E-02
0.148 5.8915E-04 0.036 5.2575E-02
0.151 5.6749E-04 0.037 5.0525E-02
C.153 5.4511E-04 0.037 4.8547E-02
0.155 5.2562E-04 0.038 4.6396E-02
0.157 5.0251E-04 0.039 4.4237E-02
0.160 4.7796E-04 0.039 4.2190E-02
0.162 4.5197E-04 0.040 4.03":7E-02
0.164 4.3609E-04 Q.040 3.8515E-02
0.166 4.1154E-04 0_041 3.6759E-02
0.169 3.9349E-04 0.041 3.5064E-02
C.171 3.6894E-04 0.042 3.3260E-02
C.173 3.5450E-04 0.042 3.1584E-02
6.175 3.3573E-04 0.043 3.0052E-02
�.178 3.1985E-04 0.043 2.8635E-02
�.180 3.0252E-04 0.044 2.7313E-02
0.181 2.9160E-C� 0.045 2.6004E-02
0.184 2.7653E-04 0.045 2.4667E-02
0.167 2.6281E-04 0.046 2.3439E-02
0.169 2.5198E-04 0.046 2.2193E-02
C.191 2.3609E-04 0.047 2.1004E-02
C.193 2.2599E-04 0.047 1.9927E-02
C.196 2.13715-04 0.048 1.8869E-02
C.198 2.0360E-04 0.046 1.7807E-02
��.200 1.9638E-04 0.049 1.6788E-02
��.202 1.8334E-04 0.050 1.5854E-02
�.205 1.7E89E-04 0.050 1.4987E-Q2
0.207 1.6245E-04 0.051 '_.4169E-02
0.209 1.5306E-04 0.051 '_.3372E-02
0.211 1.4440E-04 0.052 1.2E73E-02
r,.214 �.3140E-04 0.052 1.2009E-02
C.216 1.2563E-04 0.053 1.1378E-02
C.218 1.1552E-04 0.053 1.0784E-02
G.220 1.0830E-04 0.054 1.0168E-02
��.223 1.0108E-04 0.054 9.8598E-03
�.225 9.3860E-OS 0.055 9.1593E-03
0.227 8.9528E-OS 0.056 8.67E33-03
0.229 8.1586E-OS 0.056 8.1954E-03
0.232 7.4366E-OS 0.057 7.7500E-03
C.234 7.1478E-OS a.057 7.3420E-03
C.236 6.5702E-OS 0.058 6.9493E-03
G.236 6.2814E-OS 0_058 6.5435E-03
G.241 5.9926E-OS 0.059 6.1413E-03
D.243 5.7760E-OS 0.059 5.7442E-03
0.245 5.0540E-OS 0.060 5.3681E-03
0.247 4.7652E-OS 0.061 5.0230E-03
0.250 4.2598E-OS 0.061 4.6981E-03
0.252 3.8266E-OS 0.062 4.3789E-03
0.254 3.4656E-OS 0.062 4.0945^a-03
C.256 3.2490E-OS 0.063 3.6194E-03
0.259 3.0324E-CS 0.063 3.5775E-03
0,261 2.8158E-QS 0.064 3.3443E-03
0.263 2.4548E-OS Q.064 3.i263E-03
0.265 2.3826E-OS 0.065 2.9032E-03
0.268 2."iE60E-O5 0.066 2.7342E-03
0.270 1.9494E-OS 0.066 2.5660E-03
0.272 1.8772E-OS 0.067 2.3978E-03
0.274 1.5162E-05 0.067 2_2519E-03
C.277 1.4440E-OS 0.068 2.1220E-03
C.279 1.3716E-OS 0.068 1.9934E-03
G.281 =.2274E-05 0.069 1.8519E-03
G.283 �.1552E-OS 0.069 1.7509E-03
G.285 1.0830E-OS 0.070 1.6426E-03
0,288 1.0830E-OS 0.070 '.5429E-03
0.290 1.0108E-OS 0.071 1.4310E-03
C.292 8.6640E-06 0.072 1.3379E-03
C.294 7.9420E-06 0.072 1.2455E-03 ,
C.297 7.9420E-06 0.073 1.1523E-03 I
0.299 7.9420E-06 0.073 1.0751E-03 �i
n.?O1 7.4420E-06 0.074 1.0O21E-03 �'�
=.3U3 . .:4�0E-'J� 0.0?4 _.=36c`E-0= �'i
21 of 23
0.306 ?.2200E-G6 0.075 8.5600E-04
0.308 7.2200E-06 0.075 8.3247E-04
0.310 7.2200E-06 0.076 7.8193E-04
0.312 7.2200E-06 0.077 7.2056E-04
0.315 7.2200E-06 0.077 6.7146E-04
0.317 7.22DOE-06 0.078 6.1875E-04
0.319 7.2200E-06 0.078 5.7182E-04
0.321 7.2200E-06 0.079 5.2562E-04
0.324 7.2200E-06 0.079 4.8807E-04
0.326 7.2200E-06 0.080 5.4908E-04
0.326 E.4980E-06 0.080 4.1O10E-04
0.330 E.4980E-06 0.081 3.6678E-04
0.333 6.4980E-06 0.081 3.2273E-04
0.335 5.7760E-C6 0.082 2.6519E-04
0.337 5.0540E-06 0.083 2.5775E-04
0.339 5.0540E-OE 0.083 2.3609E-04
0.342 S.Q540E-05 0.084 2.1949E-04
0.344 5.0540E-06 0.084 2.0721E-04
0.34E 4.3320E-06 0.085 ;.8772E-04
0.348 4.3320E-06 0.085 �.6895E-04
0.351 4.3320E-06 0.086 1.3862E-04
C.353 3.6100E-06 0.086 1.1119E-04
C.355 3.6100E-06 0.087 1.0180E-04
0.357 3.6100E-06 0.088 9.9636E-OS
C.361 2.8016E-06 0.088 9.7470E-05
C.362 2.BBBOE-06 0.069 9.6748E-OS
Q.364 2.8860E-06 0.069 9.6026E-OS
Q.366 2.'_660E-06 0_090 9.3860E-OS
0.369 2.i660E-06 0.090 9.2416E-OS
��.371 2.1660E-06 0.091 8.8906E-OS
��.373 2.1660E-06 0.091 8.8084E-OS
.�.375 2.1660E-06 0.092 8.5918E-OS
0.375 2.1E60E-C6 0.092 8.2306E-OS
0.380 2.1E60E-06 0.093 7.9420E-OS
0.362 2.1660E-06 0.094 7.7254E-OS
0.364 2.1660E-OE 0.094 7.5810E-OS
0.387 2.1660E-Q6 0.095 7.2200E-GS
C.389 2.1660E-06 0.095 7.0756E-GS
C.?91 2.1660E-06 0.096 6.5702E-GS
C.393 2.1660E-06 0.096 5.9926E-GS
C.396 7.2200E-07 0.097 5.5594E-OS
C.398 7.2200E-07 0.097 5.0540E-GS
0.400 7.2200E-07 0.098 4.7652E-OS
0,402 7.2200E-07 0.099 4.0432E-OS
G.405 7.2200E-07 0.099 3.6100E-05 ,
��.407 7.2200E-07 0.100 2.9602E-OS
��.409 7.2200E-07 0.100 2.3104E-05
��.411 7.2200E-07 0.101 2.0216E-05
��.414 7.2200E-07 0.101 2_0216E-OS
0.416 7.2200E-07 0.102 1.8772E-OS I
0.418 7.2200E-07 0.102 1.8772E-OS
0.420 7.2200E-07 0.103 1.7328E-OS
0.423 7.2200E-07 D.103 1.6606E-OS '
0.425 7.2200E-C7 0.104 1.5884E-OS
0.427 7.2200E-C7 0.105 1.5162E-OS
C.429 7.2200E-07 0.105 1.2274E-CS
C.432 7.2200E-07 0.106 1.0830E-CS
C.434 7.2200E-07 0.106 1.0108E-CS
Q.436 7.2200E-07 0.107 9.3960E-05
Q.436 7.2200E-07 0.107 8.6640E-C€
Q.441 7.2200E-07 0.108 7.9420E-C�
0.443 7.2200E-07 0.109 6.3179E-G=
�.445 7.2200E-07 0.109 5.7760E-C=
0.447 7.22005-07 0.110 4.3320E-C�
0.450 7.22003-0? C.�10 7.220CE-0'
22 of 23
"*'Flow Duration Performance According to Dept.of Ecology Criteria"*'
Excursion at Predeveloped Y�Q2(Must be Less Than 0%): -12.6% PASS
Maximum Excursion from YZQ2 to Q2(Must be Less Than 0%): -12.6% PASS
Maximum Excursion from Q2 to Q50(Must be less than 10%): -93.9% PASS
Percent Excursion from Q2 to Q50(Must be less than 50%): 0.0% PASS
* POND MEETS ALL DURATION DESIGN CRITERIA: PASS
Fl��nr Duratian Pl�t-�hall�v�r Pond, 3
orifice
o�
ond Duraition Pertarmance
6caursian at 113 Q2: -12.6°� PAS S I III
x Excursian 1�2 Q3 to Q2: •12.6�6 PL�S S
�a x Exoursion Q3 ta Q50: -93.9�6 PASS
96 Pas Exaursian Q?to Q50: 0.096 PASS ;_;_„_,
-- - - - - x UUS EL for Link 1: 26.21 Fe�t- - -
r--�
�
� �a
� , ��
� � ,
Q I I
� �
02
�
�
� �
0.1 —— —- � — — —— a�
� � �;�r �`
r:V:
'' ' ' '' �� ' ' '_
(
i
��
��� ��� ��'� ��-0� ��� ��� ��-0� ��'��
Exceedance Probabiliiy
.` Predeveloped /� Postde�reloped
23 of 23
MGS FLOOD
PROJECT REPORT
Program Version:3.13 Run Date:02/21l2011 2:30 PM
Input File Name: Strander Jan 2011_Phase 3.fld
Project Name: STRANDER EXTENSION
Analysis Title:
Comments: shallow pond, 2.7ft detention, 3 orifice2nd orifice low, inlcudes +0.56 ac from jackinbox
**********Precipitation Input*"***'`****
Extended Precipitation Timeseries Selected
Climatic Region Number: 13
Full Period of Record Available used for Routing
Precipitation Station:960040 Puget East 40 in MAP 10%01!1939-10/01±2097
Evaporation Station 961040 Puget East 40 in MAP
Evaporation Scale Factor :0.750
HSPF Parameter Region Number: 1
HSPF Parameter Region Name : USGS Default
"""""Default HSPF Parameters Used(Not Modified by User)"""""""*
2/22/2011 Poge 1 of 22
""-""" Watershed Definition '""""'
Number of Subbasins:
""""" Subbasin Number 1 """""
`*'Tributary to Node: 1
"'Bypass to Node :None
------------------------Area(Acres)--------•------•-••--
------------Deve I o ped------------
Predeveloped To Node Bypass Node
Till Forest b.510 �.C��� �.i_
Till Fas=ure G.G�O ,.CJO J.C_
Till Gra�s 0.0��0 ,G�iii n,r:
Outwash Forest O.00G 0.000 G.O�
Outwash Pa�ture O.00C 0.000 O.GJ
Outwash �rass O.00C 1.980 0.05
Wetland O.00C G.000 0.0���
Impervicus 0.000 5.130 0.05
Subbasin Total 6.610 6.610 0.000
____________________.Lateral Flow Connnections--------------------------
-----Predeveloped---------- -------Developed---------------
Surface Interflow Grnd Water Surface Interflow Grnd Water
Till Forest t:cde Node Node taod=
^ill Pastcre [•:cne t;cde P]ode PIo_:�
Till Grass hode t:cde t]ode I•]ocle
Outwash Forest Node Acde Node tdode
Outwash Pasture t•Icde Node Node `]o i�=
Outwash Grass Ncde ivode Node 'dod=
Wetland tdode Node Nod= ._-_i=
Impervious `Icd� t1od�
Lateral :
Lateral ._
***Subbasin Connection Summary "''''
Subbasin 1 -------->Node 1
**" By-Pass Area Connection Summary"'
No By-Passed Areas in Watershed
"`Postdeveloped Node Connection Summary"'
UpsVeam Node No. Link Type Downstream Node
Node 1 Pond Node 2
Predeveloped Compliance Node: 1
Postdeveloped Compliance Node: 2
Strander Phase 3-MGSFIood
2/22/2011 Page 2 of 22
'`*''Postdeveloped Structure Summary"**
Link No. 1,Pond: Stormwater Wetland-Shallow Pond 3 orifice
Upstream Node: 1, Downstream Node:2
User Specified Elevation Volume Table Used
Elevation(ft) Pond Volume(cu-ft)
24.00 0.
25.00 51813.
26.00 107875.
26.70 149696.
27.00 168280.
Hydraulic Conductivity . 0.00 in/hr
Depth to Water Table 3.00 ft
Potential for Bio-Fouling Average to High
Maintenance Poor
Riser Geometry
Riser Structure Type :Circular
Riser Diameter 18.00 in
Common Length 0.000 ft
Riser Crest Elevation 26.70 ft
Hydraulic Structure Geometry
Number of Devices: 3
--Device Number 1 --
Device Type : Circular Orifice
Invert Elevation . 24.00 ft
Diameter . 1.13 in
Orientation :Horizontal
Elbow No
---Device Number 2---
Device Type : Circular Orifice
Invert Elevation 24.50 ft
Diameter 1.12 in
Orientation Horizontal
Elbow Yes
--Device Number 3---
Device Type : Circular Orifice
Invert Elevation . 26.00 ft
Diameter 1.25 in
Orientation Horizontal
E�bo:o �'es
Strander Phase 3-MGSFIood
2/22/2011 Page 3 of 22
i ' �!J✓�'
. J_� .
*********'"`Postdeveloped Hydraulic Rating Table*''***********
Postdeveloped Link: 1
Elev(ft) Storage(ac-ft) Discharge(cfs) Infilt Discharge(cfs)
29.000 O.00G 0.000 C.Gpr
24.015 O.G18 0.009 O.00C
24.030 0.036 D.00o O.00C �
24.060 0.071 0.008 O.00C
24.120 0.193 0_012 O.00r,
24.180 0.214 0.019 O.OGC
24.290 0.2E5 0.017 O.OGU
74.300 0.357 0.018 0.000
'4.360 0.426 0.020 O.OGO
29.920 0.500 0.022 O.00O
�9.940 0.523 0.022 0.000
�9.960 0.597 0.023 0.000
�9.980 0.571 0.023 0.000
�9.500 0.555 0.024 0.000
�9.515 0.613 0.026 0.000
?9.530 0.630 0.030 0.000
�'9.595 0.698 0.032 0.000
'4.560 0.660 0.033 0.000
=4.E20 0.737 0.038 0.000
�9.E80 0.809 0.041 0.000
'9.790 0_880 0.045 0.000
'4.800 0.952 0.048 0.000
24.860 1.023 0.050 0.000
�4.920 1.094 0.053 0.000
�4.980 1.166 0.055 0_000
�5.040 1.291 0.058 0.000
�5.100 1.318 O.OoO 0.000
�S.lEO 1.395 O.Oo'2 0.000
�5_22C 1.473 O.Oo4 0.000
�5.28C 1.550 0.066 G.000
�5.340 1.627 0.068 0.000
25.900 1.iO4 0.070 0.000
25.960 1.781 0.072 0.000
�5.520 1.859 0.079 0.000
�5.580 i.93o 0.075 0.000
'S.640 2.013 0.077 0.000
�5.700 �.090 0_079 0.000
?5.700 2.168 0.080 0.000
=5.820 2.245 0.082 D.000
=5.880 2.322 0.084 0.000
25.990 2.399 0.065 0.000
�5.955 2.919 0.08E 0.000
=5.970 �.938 0.08E 0.000
=5.985 2.957 0.086 0.000
�6.000 <.476 0.087 0.000
�6.015 2.497 0.092 0.000
26.030 2.518 0.054 0.000
�0'.045 2.53E 0.096 0.000
�0.060 2.559 0.09E 0.000
'0.120 2.641 0.103 0.000
�5.180 2.723 0.108 0.000
2n.240 2.806 O.112 0.000
_�,.300 2.888 0.116 D.000
�n.360 2.970 0.119 0.000
=6.420 3.053 0.122 0.000
=6.480 3.135 0.125 0.000
^_6.540 3.217 0.128 0.000
26.600 3.259 0.131 0.000
�6.625 3.334 0.132 0.000
?6.650 3.368 0.134 0.000
�6.675 3.402 0.135 0.000
�6.700 3.437 0.130 0.000
�6.715 3.458 O.lE6 0_000
�'0.730 3.479 0_220 0.000
�0."9° 3.501 O.G�iO 0.000
�o.76p 3.522 _.=�� O.v�G
Strander Phase 3-MGSFIood
2/22/2011 Page 4 of 22
P�
?,d�
26.775 3.543 0.906 / 0.000
26.750 3.565 0.565 0.000
26.805 3.586 0.681 0.000
2E.620 3.607 0.800 0.000
2E.880 3.693 1.347 0.000
2E.990 3.?78 1.975 0.000
27.000 3.eE3 2.650 0.000
27.060 3.95� 3.337 0.000
27.120 9.092 4.001 D.000
27.180 9.131 4.610 0.000
�7.240 9.220 5.135 0.000
�%.300 9.310 5.561 0.000
2?.3E0 9.399 5.88E 0.000
�7.920 9.988 E.131 0.000
�7.980 9.�?8 E.425 0.000
_ .59C 9.56� _,�'03 C.Opp
**''Post-Developed Link Statistics *"''
Postdeveloped Pond Water Surface Elevation Statistics
Annual Maxima Water Surface Elevation(R)
Link: 1
Max Date WSEL (ft)
IZ/0?/1939 25.ZSC
C1/18/1941 24.825
12/20/1941 25.079
11/23/1992 25.358
01/23/1944 29.707
G2/07/1995 25.250
���2/OS/1996 29.°81
12/OS/1°9E 25.195
10/19/1597 25.253
��2/22/1945 25.105
�il/22/1950 25.396
�i�!09/1551 25.577
:C/03/1951 24.881
O1/12/195s 25.934
ill/22/1559 25.078
il/19/1959 25.036
C1/06/1950 25.o'i6
���/26/195? 25.045
��1/17/1958 25.14�
C1/13/1959 25.421
11/21/1959 25.241
11/29/1960 25.483
1�/29/1961 29.935
1�/30/1902 29.955
li/14/1563 25.02G
1�/O1/1964 25.124
J1/07/1566 25.1E2
_2/lE/1966 25.385
=0/27/1967 25.127
:�/11/1968 25.197
O1/27/1570 25.294
12/07/1970 25.303
C3/13/1972 26.11E
1�/27/1972 25.oE1
C3/O1/1979 25.162
12/27/1974 25.1e3
G2/27/1976 25.225
G6/O1/1977 29.811
12/15/1°77 25.4E3
��3/OS/1979 29.992
12/19/1579 2E.216
12/30/1980 25.181
10/OE/1581 25.755
�3/09/1583 25.237
��3/�'�/-9F9 29.°59
:1/li/_S59 29.935
Strander Phase 3-MGSFIood
2/22/2011 Page 5 of 22
O1/1�/1986 25.330
11/24/1986 25.??8
09/06/1988 ZS.18E
09/OS/1989 �5.234
O1/05/1990 25.?56
11/29/19°0 25.956
O1/31/1992 25.35C
04/11/1993 24.531
03/03/1954 29.9G1
12/27/1994 2�.460 I
02/09/199E 26.06=' I
O1/03/1997 26.Os0
10/08/1997 25.004 I
11/20/1998 20.05_ I
02/28/2000 25.15E ��
OS/OS/2001 29.823 i
12/20/2001 29.8�9 I
12/OB/2002 26.G8� I
10/29/2003 ZS.11l I
02/OB/2005 24.940 I
11/G8I2OOS LS.9_4 i
11/27/2006 25.209 '
O1/G7/2008 25.<85 'i
02/19/2009 25.9�9 I
O1/10/2010 25.3G? ��
11/17/2010 25.?OC I
12/OS/2011 25.195 II�
O1/20/�013 26.095 I
O1/28/2019 25.23'e I
03/30/2015 25.01� �
O1/07/2016 26.00?
11/O1/2016 25.1s='
O1/31/2018 25.�1_
O1/12/2015 25.35t'
04/21/2020 25.OG`
11/GS/2OZO 2S.SS8
12/21/2021 25.L"r
03/30/2023 25.131
' O1/25/2024 25.3e6
' 12/24/2024 25.535
Ol/OS/2026 25.63�
O1/29/2027 25.027
I 02/23/2028 25.1E_
12/11/2028 25."�99
O1/2E/2030 25.8?'c
03/04/2031 25.184
O1/21/2032 25.4:1
12/23/2032 25.O�e
O1/16/2039 2o'.OGt
02/19/2035 GS.L1�
�Z�G��z�3b G5.�3(:
03/09/2037 24.�0_
12/15/2037p 25.9U��
ZZ�11�2�3C L4.�h_
O1/14/2090 25.2r1
12/25/2090 25.3E'1
09/15/2092 25.33
02/26/2093 25.�C=
03/21/2094 25.0'"s-
11/28/�099 25.1�]
02/17/204E 25."-9-
02/02/2047 25.055
12/10/2047 25.SC'
� 03/17/2049 25.Oc �
12/09/2045 25.01
04/05/2051 29.54-
04/17/2052 24.7u-
12/10/2052 25.C`_�-
12/11/2053 25.re�
11/02/�054 - . "
.,2!J�i�JS'o � . �
Strander Phase 3-MGSFIood
2/22/2011 Pnce 6 of ?,
G1IO2/��Si ���.9�=3
11/25/2057 25.0�'
12/02/2058 25.70��
� O1/23/2060 29_958
10/27/2060 25_252
O1/03/2062 25.144
12/30/2062 LS.L�?
12/23/2063 25.610
12/O1/2069 �S.ra�-
11/04/20E5 24.E18
12/17/20E6 �S.SEC
O1/20/20E8 25.SSC
10/29/2068 24.5-1
12/19/2069 24.8_�
02/19/20�1 24.8�?
11/03/2071 25.10�
1Z/27ILO7Z ZE.LI1�
12/15/2073 25.39c
11/20/2074 24.939
10/30/2075 25.599
0°/04/2077 24.61�
12/02/2077 25.085
02/25/2079 24.91:
12/19/2079 26.17�
11/21/2080 25.5��+
02/19/2082 25.56�
02/20/2083 25.4=��
11/27/2083 2n.0�5
12/14/2089 25.3=6
11/O1/2085 25.155
11/23/2086 25.36_
12/OG/2087 25.1i�
11/OS/20B8 25.3?3
11/10/2065 25.27'
1G/O9/2090 LS.G��,
O1/31/2092 25.64�-
11/07/2092 24.���r
12/19/2093 24.�63
12/27/2099 25.2?i
1=i1-� -- - --�--
2/22/2011 Page 7 of 22
Postdeveloped Ranked Annual Maxima Water Level(ft)
Tr(yrs) Link: 1
1.G0 24.61�
1.G� �4.?O1
1.02 24.707
1.02 24.794
1_03 24.811
1.09 24.811
1.09 24.812
1_O5 24.616
1.06 24.623
1.06 24.629
1.07 24.662
1.08 24.881
1.09 24.68°
1.09 24.693
1.10 24.90E
1.11 24.913
1.12 24.531
i.12 29.934
1.13 29.935
i.19 29.935
1.15 29.540
1.16 29.541
1.17 29.94�
1.18 29.955
1.18 29.G5�
1.19 29.Go3
1.20 29.981
1.21 29,9u_
1.22 29.c5'�
1.23 25.004
1.24 25.OG�
1.25 25.013
1.20 25.Ci-
1.27 25.C��-
1.28 25.C��
1.29 25.C�
1.30 25.C�-
1.31 25.C�_
1.32 25.CS
1.33 25.Ce
1.35 25.Ce`
1.36 25.C--
1.37 25,p-
1.39 25.Ch
1.39 25.C�
1.90 25.C�
1.92 25.r�
1.93 25.05
1.94 25.1'_
1.96 25.1�-
1.97 25.L
1.46 25.1_
1.50 25.1�
1.51 25.1_
1.53 25.1-
1.54 25.1
1.56 25.1_
1.57 25.1_
1.59 25.1-
1.00 25.1-
1.62 25.1-
l.0"4 25.1-
1.65 25.1- ��
l.0'7 25.1`_
1.09 25.1
1.71 25.1E3
1.73 �5.181
1.?5 25.18�
Strander Phase 3-MGSFIood
2/22/2011 Page 8 of 22
1.77 25.182
1.79 25.1n9
1.81 25.186
1.83 25.199
1.85 25.197
1.87 25.198
1.89 25.204
1.92 25.209
1.G4 25.211
1.96 25.219
1.99 25.225
2.01 25.230
2.04 25.239
2.07 25.�36
2.09 25.237
2.12 25.291
G.IS GS.G43
G.1H LS.GSO
2.21 25.253
2.24 25.256
2.2� 25.��1
2.31 25.271
2.39 25.27?
2.38 25.285
2.41 25.292
2.45 25.294
2.49 25.302
2.53 25.303
2.57 25.326
2.61 25.330
2.65 25.336
2.70 25.344
2.75 25.34E
2.80 25.350
2.85 25.358
2.90 25.36E
2.55 25.373
3.01 25.3�1
3.07 25.365
3.13 25.396
3.19 25.39'
3.26 25.398
�.32 25.900
3.90 25.919
3.97 25.921
3.55 25.931
3.63 25.939
3.72 25.450
3.80 25.4E0
3.90 25.463
4.00 25.475
9.10 25.483
9.21 25.504
4.32 25.550
4.45 25.55�
4.58 25.SE0
4.?1 25.563
4.86 25.577
5.01 25.575
5.17 25.594
5.35 25.610
5.59 25.616
5.�9 25.6s2
5.95 25.699
E.19 25.601
6.49 25.699 �
E.;1 25.700 �
7.01 25.755 ��i
7.33 25.?56
.e� 25. _��
8.04 _5. �_
Strander Phase 3-MGSFIood
2/22/2011 Page 9 of 22
N.S� G�.V^.
9.00 25.87e
9.55 25.G07
10.16 25.923
10.8E 25.53E
11.6E 25.956
12.59 26.00�
13.68 26.008
19.97 26.030
16.59 26.045
1�.47 L6.OSG
LO.gG L6.��5
24.10 26.062
28.44 26.084
34.E8 2E.116
44.42 2E.179
61.�7 2E.204
101.36 26.216
^_8�.36 �r.�o9
Postdeveloped Water Surface Elevation Data(ft)
Recurrence Interval Computed Using Gringorten Plotting Position
Tr(yrs) Link: 1
�.0�-Year 29.821
'.11-"i2Gr 29.917
:.�5-Year 25.014
�,CO-Year 25_228
. ,='�-Year 25.902
5-Year 25.579
i:�-'iear 25.921
-�-Year 26.059
==-_'ear �6.195
1;1�_-i_G_ -E.�lc'
Strander Phase 3-MGSFIood
2/22/2011 Page 10 of 22
Postdeveloped Infiltrated Water Statistics
Volume Statistics Computed for Entire Simulation
Statistic Link: 1
Total Infiow Volume ;ac-ftl 2�9=.
Total Volume Infiltrated (ac-'ti p.
Percent Inf_ltra_ed C.CC
*********Water Quality Facility Data'`**'`****""*''`''
Node No: 1
Basic Wet Pond Volume(91%Exceedancel 22301. cu-ft
Computed Large Wet Pond Volume. 1 5'Basic Volume: 33452.cu-ft
2-Year Discharge Rate: 1.333 cfs
15-Minute Timestep,Water Quality Treatment Design Discharge
On-line Design Discharge Rate(91°b Exceedance): 0.78 cfs
Off-line Design Discharge Rate(91°�o Exceedance): 0 44 cfs
Node No:2
Basic Wet Pond Volume(91°;o Exceedancel: 5012.cu-ft
Computed Large Wet Pond Volume, t5`Basic Volume: 7518 cu-ft
2-Year Discharge Rate 0 065 cfs
Strander Phase 3-MGSFIo
2177%?0�]
"*'`*****'""`Compliance Point Results***'""k*******
Predeveloped Compliance Node: 1
Postdeveloped Compliance Node: 2
"Point of Compliance Annual Maxima Flow Data*'
Predevelopment Runoff Postdevelopment Runoff
Date Annual Max Q(cfs) Date Annual Max Q(cfs)
04/30/1990 0.17c 12/07/lc3c 0.065
01/31/1941 O.uE9 C1/18/1991 0.099
12/15/1541 O.1S0 12/20/1991 0.059
02/10/1993 0.072 11/23/1992 0.070
Ol/23/1999 0.059 O1/23/1c94 0.093
02/07/1595 0.223 �2/07/1595 0.065
02/OS/1596 0.137 C2/OS/199E 0.055
02/02/1597 0.139 12/OS/1G9E 0.062
03/21/1998 0.241 10/19/1997 O.OeS
02/22/1999 0.121 02/22/1999 0.060
03/03/1950 0.998 O1/22/1950 0.06Y
02/09/1551 0.19° 02/09/1951 0.075
O1/29/1c52 0.052 10/03/1951 0.051
O1/11/1c53 0.074 O1/12/1953 0.071
O1/22/1°54 0.121 O1/22/1954 0.05�
04/12/1955 D.OSE 11/19/1954 O.OSE
03/09/195E 0.130 O1/06/1956 D.0??
02/25/1957 0.107 02/26/1957 0.05�
O1/16/1958 0.130 O1/17/1958 G.OE�
O1/12/195° 0.140 O1/13/1959 0.0?1
12/15/1959 0.150 11/21/1959 0.065
02/14/1961 0.128 11/29/1960 0.0?3
03/09/1962 D.G69 12/29/1961 O.G59
02/03/1963 0.076 11/30/1962 G.05=]
Ol/O1/1964 0.122 il/14/1563 0.05�
0�/26/1965 O.1S_ �2/O1/19E4 0.061
O1/06/1906 0.093 O1/0?/1966 0.06�
O1/19/196; 0.235 "�2/16/1966 0.0?C
02/03/1966 0.122 10/27/19E7 0.061
12/03/1966 0.131 12/ll/1968 0.063
01/13/1970 0.101 O1/27/1970 O.Oo-
12�O6I197O O.11S 1L�O7IlJ7O 0.06
02/28/1972 G.310 03/13/1572 O.1G3
C1/13/1973 0.112 12/27/1972 0.0%e
02/18/1974 O.lo7 03/Ol/1979 O.Or'3
12/2E/1974 0.203 12/27/1979 O.Oo�
O1/27/1976 0.190 02/27/197o O.Oc"�
CS/31/1977 0.020 OE/O1/1977 0.09�
1�/10/1977 0.119 12/15/1977 0.07=
03/04/1979 0.11? 03/OS/1579 0.05-
12/17/1979 0.18E 12/1°/i979 O.11_
12/26/1980 0.075 12/30/1980 O.Oe'
lu/OE/1981 0.239 10/06/1981 O.OE
O1/05/1983 G.134 03/0°/1983 0.0r`
03/19/1984 0.12� 03/21/1989 0.0`
02/11/1985 0.085 11/11/19u9 0.0`-
O1/18/1986 0.281 01/19/1986 O.Oe
11/29/1986 0.29� 1'_/24/1986 O.OE-
04/06/1988 0.129 u4/06/19£�8 0.0�_
04/OS/1989 C.137 04/OS/1989 O.OE_
O1/0°/1950 C.451 O1/09/1950 0.080
11/29/1990 G.389 11/24/1990 0.086
O1/27/1992 O.11? O1/31/1G52 0.065
06/09/1993 0.095 04/11/1G53 0.053
03/03/1994 0.075 03/03/1954 0.056
02/19/19c5 0.15E 12/27/1994 0.072
0�/09/1996 0.360 02/09/1996 0.098
O1/02/1597 0.�29 O1/03/1997 0.099
02/28/199& 0.089 10/OA/1997 0.056
il/�5/199r 0.�25 ll/26/1998 0.09?
03/�Ei�G00 0.12E CZ/28/20C� 0.069
Strander Phase 3-MGSFIood
2/22/2011 Page 12 of 22
U��'65,���,U1 _,,U9- U�%J�;`'�JC1 _. _:
OS/03/2002 G.395 12/20/ZU01 D.GS�
03/31/2003 Q.2o4 12/08/�OC2 0.10�;
O1/23/2004 O.On4 1G/29/2003 G.GeC
O2IO7/2OOS 0.111 OG/OBILOOS O.GS9
02/27/2006 0.193 11/28/�005 O.G?1
12/14/2006 0.106 11/27/2006 O.G69
03/21/2008 0.175 O1/07/2006 a,OE�
02/1;/2009 G.2?2 02/19/2009 p.Oc;9
O1/10/2010 O.lE3 O1/10/2010 0.0?C
11/1�/2010 G.2.i? 11/17/2010 0.0?9
O1/31/2012 0.151 12/OS/2011 O.G6<
O1/20/2013 G.395 O1/20/2013 O.G95
12/OE/2013 0.195 O1/28/2014 0.065
03/30/2015 O.OE8 03/30/2015 G.OS'
O1/G4/2016 0.251 O1/07/2016 G.OK9
03/07/2017 0.0?3 11/O1/2016 G.061
O1/31/2018 0.135 O1/31/2018 0.069
03/30/2019 0.134 O1/12/2019 0.069
09/14/2020 0.08E 09/21/2020 O.C56
02/10/2021 0.217 ll/25/2020 0.075
03/2E/2022 0.064 12/21/2021 O.C61
03/30/2023 0.155 03/30/�023 C.C'ol
O1/19/2024 0.122 O1/25/2024 r,C'o4
12/22/2024 0.254 12/24/2024 C,OHS
03/09/2026 0.161 O1/OS/20�6 0.0?�
O1/27/2027 0.191 O1/29/2027 0.05�
O2/15/GO28 0.174 OLIG3/2028 O.Oo'^
12/04/202� 0.155 12/11/202K O.Oo'3
02/lE/2030 0.18G O1/26/203G O.OE�
12/30/2030 C.i65 03/09/2031 0.063
O1/�0/2032 0.271 O1/21/2032 0.0?=
03/ul/2033 0.0?6 12/23/2032 0.060
O1/15/2034 0.3r,6 O1/16/2034 0.090
OZ/19/2035 C.145 02/19/2035 O.Oo�
03/24/2036 0.'�41 0�/27/2030' O.OoS
03/05/�037 5.78Gn-C3 G3/09/2037 0.092
12/15/�037 0."_C3 12/15/2037 0.0?0
0�/G�/2039 0.075 12/11/203E 0.050
O1/14/2040 0.280 Ol/19/204G 0.06r
12/25/�040 0.158 1</25/2040 0.0?0
02/20/2042 0.166 09/15/2042 0.068
03/31/2043 0.245 02/26/2043 0.0�•=
OS/Ol/2044 C.098 03/21/2044 0.06��
02/11/2045 0.114 11/28/2044 0.0�1
02/16/2046 0.143 02/17/2046 0.06_
02/O1/2047 0.090 02/02/2047 0.055
04/21/2098 0.08G 12/10/2047 0.07�
03/16/2099 C.090 03/17/2045 0.06J
12/04/2099 C.152 12/04/2045 0.0_`?
04/06/2051 C.118 04/09/2051 0.0`9
09/17/2052 C.071 04/17/2052 0.09^
Oo'/04/2053 0.271 12/10/2052 0.05=
09/G8/�054 O.OSQ 12/11/2053 0.05 �
02/17/2055 0.231 11/02/2059 0.0�:^
02/0�/2056 0.42G G2/09/2056 0.1_�
11/19/2056 0.46Q Ol/02/2057 0.08
O1/24/2055 0.15N 1'_/25/205? O.Or
12/26/2058 0.183 12/02/2058 O.OE'��
O1/19/20E0 0.065 O1/23/2060 0.0°`
O1/10/20b1 0.195 10/27/2060 O.Or
02/03/2062 O.SEo 01/03/2062 O.Oe-
12/29/2062 0.12C 12/30/2062 O.Or
12/23/<063 0.21c� 12/23/2063 0.0^.
11/30/�064 0.10� 12/01/200'9 0.058
O1/13/�066 0.05? 11/04/200'5 0.048
O1/19/�067 0.199 12/17/2006 0.075
O1/18/2068 0.29? O1/20/2068 0.075
Ol/04/�069 0.08C 10/24/200"8 0.048
09/04/20?0 O.OE? 12/14/20o'Q 0.048
�2;1�i�G71 0.079 02/14/2071 0.052
Strander Phase 3-MGSFIood
2/22/2011 Page 13 of 22
02/�?i2G�� O.G7� L"/r3/2G71 O.�c•ri
12/25/2072 0.330 12/27/2072 O.1G5
03/16/20;9 0.178 12/15/2073 0.070
O1/23/2075 0.038 11/20/2079 0.0��
03/24/2076 0.197 10/30/2075 0.07r
03/02/20?7 0.022 09/04/2077 0.0��
12/02/2077 0.079 12/02/2077 0.0���
02/25/2079 0.100 02/25/2079 0.053
12/17/2079 0.3E9 12/19/2079 O.1G8
11/21/2080 0.1E3 11/21/2080 0.075
02/13/2082 0.203 02/19/2082 0.0-5
02/19/2083 0.125 G2/20/2083 0.07�
11/26/2063 0.151 li/27/2083 0.05,
12/14/2069 0.105 12/14/2059 0.06�
O1/lE/206o 0.147 11/O1/2085 0.0�-'
12/21/2066 0.138 11/23/2086 0.06^
O1/14/2068 0.0°1 12/09/2087 O.OE_
11/CS/2068 0.1E2 11/OS/2088 O.Orc
O1/07/2090 0.07c. 11/10/2089 O.OEr
12/04/2090 0.140 12/09/2C90 0.08�
09/26/2092 0.241 O1/31/2092 0.0�?
03/22/2093 O.OE8 1?/07/2092 0.052
03/O1/2099 0.057 12/14/2093 0.055
02/1B/2095 0.0°0 12/27/2099 0.066
O1/14/2096 0.113 12/15/2095 0.068
O1/�9/20°7 0._'S8 10/2B/2096 0.�7=
Strander Phase 3-MGSFIo
2/22/2011 Page 14 of �
'•**Point of Compliance Ranked Maxima Flow Data***'
Predevelopment Postdevelopment
Tr(yrs) Q(cfs) Tr(yrs) Q(cfs)
1.00 5.?8CE-03 _.00 3.798�-;1�
1.0: 0.0��� �.01 O.Q4�
1.u2 0.022 1.02 0.043
1.02 0.036 1.02 0.047
1.03 u.050 1.03 0.04E
1.04 0.052 1.04 0.04E
1.04 0.054 1.04 O.G4£�
1.05 0.056 1.C5 0.04£�
1.OE 0.057 1.06 0.049
1.06 O.C57 1.06 0.049
1.07 0.064 1.07 0_G50
1.08 0.0b4 1.06 0.051
1.05 0.06' 1.09 0_052
1.09 0.068 1.09 0.052
1.10 0.069 1.10 0_052
1.11 0.069 1.11 0.053
1.12 0.06° 1.1� C.053
1.12 0.0?1 1.1� C.054
1.13 0.072 1.13 0.054
1.14 0.073 1.14 0.054
1.15 0.074 1.15 0_054
l.lo' O.G74 1.1E 0_054
1.17 0_Oi4 1.17 0.054
1.18 0.075 1.18 0.054
1.1Y 0.075 1_18 0.055
1.15 0.075 1.19 0.055
L�0 0.075 1.20 0.055
1.�1 0.070 1.21 O.OSE
1.22 0.07n 1.22 O.OSC
1.�3 0.079 1.23 O.OSE
1.24 0.080 1.24 0.056 '
1.25 0.080 1.25 0.05'
1.2E 0.084 1.26 0.057
1.27 0.085 1.27 0.057 I
1.28 0.088 1.28 0.057 I
i.2p o.oae i.25 o.osa �i
1.30 0.090 1.30 0.058 I
1.31 O.OGO 1.31 0.058
1.32 0.090 1.32 0.058
1.33 0.091 1.33 0.059
1.35 0.093 1.35 0.059
1_3b 0.097 1.36 O.OSG
1_37 C.098 1.37 0.059
1.38 0.099 1.3E O.O�G
1.39 d.100 1.35 0.050
1.40 0.101 1.40 0.0'eC
1.42 0.103 1.42 O.OoC
1.43 0.103 1.43 0.0"oC
1.49 ��.105 1.49 0.0"oC
1.46 0.106 1.40 0.0'oC
i.4? u.107 1.47 O.C"oC
1.48 0.111 1.48 0.061
1.50 G.112 1.SG O.Cbl
1.51 0.113 1.51 O.Ccl
1.53 0.114 1.53 O.Ccl
1.54 0.115 1.59 D.C'ol
1.50 0.117 1.56 O.Cul
1.57 O.11i 1.57 D.C61
1.55 0.118 1.59 O.C��'�
1.6G 0.11° 1.n0 O.Co'�
1.E2 0.120 1.62 O.Cc�
1.64 0.121 1.64 O.Cc'�
1.65 0.121 1.05 O.C�:�
� 1.E? U.1=� 1. , .C,"�
1.69 ).1_'=' 1.c., �,r;�_'�
Strander Phase 3-MGSFIood
2/22/2011 Page 15 of 22
1.71 0.122 1.71 0.062
1.73 0.124 1.73 O.Oo3
1.75 0.125 1.75 0.063
1.77 0.126 1.77 0.063
1.75 0.128 1.79 0.063
1.81 0.128 1.81 0.063
1.83 0.130 1.83 O.Oo3
1.a5 G.130 1.85 0.063
1.8� 0.131 1.87 O.Oo4
1.59 0.134 1.89 0.064
1.92 G.134 1.92 0.064
1.59 0.135 1.94 0.064
1.5E 0.135 1.50 0.064
L 59 0.137 L 99 0.064
2.01 0.137 2.01 O.O6S
�_04 0.138 2.09 0.065
2.07 0.139 2.Oi 0.065
2.09 0.190 2.09 O.OES
G.1Z 0.190 2.1L O.OES
2.15 O.i90 2.15 O.OES
2.18 0.191 2.18 O.OES
�.21 0.141 2.21 0.065
�.24 0.143 2.29 0.065
�.27 0.143 2.27 0.06n
�.31 0.149 2.31 0.066
2.34 0.145 2.39 0.066
2.38 0.147 2.38 0.066
2.91 0.149 2.41 0.067
�.45 0.145 2.95 0.067
�.49 0.150 2.99 0.067
�.53 0.151 2.53 0.067
�.s7 0.151 2.57 0.068
2.r1 0.151 2.01 O.On8
2.65 0.152 2.05 O.OoB
�.70 0.155 2.?0 0.068 '
�.75 0.158 2.75 0.068 I
2.80 0.158 2.80 0.06° I
2.85 0.15° 2.85 0.069
2.�0 0_161 2.90 0.055
�.95 0.162 2.95 O.D65
3.01 D.163 3.01 0.07�i
3.07 0.16E 3.07 0.0-5
3.13 O.lo7 3.13 O.C,���
3.i9 O.lo9 3.19 O.G�O �
_.26 0.174 3.26 0.0��5
3.32 0.175 3.32 0.0,0
3.40 0.176 3.40 O.G,1 �i
�.47 0.179 3.4i 0.0,1 �
�.55 0.180 3.55 0.0�1
=�.63 0.180 3.63 O.C"1 �
=.?2 0.183 3.72 O.C,=
�.80 0.183 3.60 O.0 '=
�.90 0.188 3.90 O.C"'�
�.00 0.197 4.00 O.C?>
4.10 C.iG9 4.10 O.C�3
�.^1 0.203 4.21 O.C-3
1_32 0.203 9.32 O.C-`
9.45 0.21'0 4.45 O.l';-`
9.58 0.21? 9.58 0.ii-�
9.71 0.223 4.71 0.0?5
9.,96 0.225 9.8E 0.0-5
�,01 0.229 5.01 0.0^5
5.17 0.231 5.17 0.��-�-
_.35 0.235 5.35 0.��- `
�.54 0.237 5.54 O.J ,
�.74 0.239 5.74 0.��--
�.95 0.241 5.95 0.5 -
5.19 0.241 E.19 O.G--
e�.44 0.298 6.49 O.G ' ,
_.71 0._48 e."'1 O.G,�
-.pl 0.�4� .pl O.OgO
Strander Phase 3-MGSFIood
2/22/2011 Page 16 of 22
7.33 �.�Si 7.33 D.C3G
7.65 G.254 7.69 O.r�p
8.08 G.264 8.08 O.C�1
$.52 p.271 8.52 O.CB9
9.00 0.271 9.00 0.0�9
9.55 0_272 9.55 O.Ge9
10.16 0.2E�0 l0.lo O.Ge�
10.86 0.281 lO.Bo O.C�P���
11.66 0.297 11.66 O.G°�c�
12.5° 0.306 12.59 O.G:��
13.68 0.310 13.68 O.Gc��
19.57 0.330 14.�7 p,Gc}
10.54 0.345 1E.59 O.G��
18.47 0.345 18.47 p,0�?
20.92 0.36r 20.92 p,0�?
24.10 0.3E5 24.10 0.0�=
2�.49 0.389 28.94 0.1):
34.08 0.420 34.68 0.1 5
94.42 0.451 44.92 0.1�-
61.?'7 0.4E0 61.�? 0.1:�
101.3c 0.49�� 1U1.�� �'.1-"�
. __._,� i;._�� _�_. �� �:.1_�
Strander Phase 3-MGSFIc
2/22/2011 Page 17 of 22
"'Point of Compliance Flow Frequency Data"`
Recurrence Interval Computed Using Gringorten Plotting Position
Predevelopment Runoff Postdevelopment Runoff
Tr(Years) Discharge(cfs) Tr(Years) Discharge(cfs)
2-Year ��.137 _-':'ear �i_0>_5
5-Year J.«8 5-Year �.U" `
10-Year 0.278 10-Year O.C=
25-Year 0.372 25-Year O.C�'
50-Year 0.459 50-Year 0.15,.
100-Year 0.497 100-Year 0.11�.
200-Year 0.543 200-Year 0.11
*� R.ecora teo Short te Comc�cte Pea}: �ischarae `:=�r ,.,��� F=_���:rr�__-c =rre_<sls
Strander Phase 3-MGSFIood
2/22/2011 Page 18 of 22
"'Point of Compliance Flow Duration Data"'
Predevelopment Runoff Postdevelopment Runoff
Discharge Exceedance Discharge Exceedance
(cfs) Probability (cfs) Probability
O.O00E+00 1.COr,Gg+pO p,CGO�-GO 1.OGOGE+r;
2.830E-03 2.3cY�CE-U� 5.6�4E-�4 d.7943E-i-�:
5.661E-03 1.8183E-01 1.137E-03 8.5759E-i-.i
8.991E-03 1.9869E-01 1.705E-03 8.4626E-�;l
C.O11 1.298oE-01 0.002 8.3�63E-C;1
0_019 1.0625E-01 0.003 8.3053E-J1
0.017 9.120E•E-G2 0.003 8.2959E-:)1
0.020 7.8997E-G2 0.009 E.1G42E-'�1
0.023 6.8893E-G2 0.005 8.1006E-'!'_
0.025 6.0947E-�� 0.005 7.9974E-��:
0.028 5.3261E-02 0.006 7.901EE-;�=
0.031 9.7175E-0� 0_OOo 7.7639E- _
0.039 9.1832E-OZ 0.007 7.6586E-�=
0.037 3.7205E-02 0.007 7.5412E-�5_
0.090 3.3133E-�2 0.008 7.9282E-C:
0.092 2.9E38E-C2 0.009 7.3006E-� :
0.095 2.6430E-02 0.009 7.1597E-�-:
0.098 2.3699E-02 0.010 7.0119E-� =
0.051 2.1262E-02 0.010 E.8755E-� =
0.054 1.9150E-02 0.011 6.7912E-C1
0.057 1.7267E-02 0.011 6.6131E-i;l
0.059 1.5521E-02 0.012 6.4733E-1i1
0.062 1.9036E-02 0.013 6.3117E-;il
0.065 1.2639E-02 0.013 6.1563E-��1
0.068 1_1278E-02 0.014 0.0069E-',1
0.071 1.0348E-02 0.014 S.A567E-��1
0.074 9.9690E-03 0.015 5.6895E-i1
0.076 6.5860E-03 0.015 5.5192E-51
0.079 7.8178E-03 0.016 5.3531E-5�:
0.082 7.1593E-03 0.016 5.1879E- �=
0.085 6.5598E-03 0.017 5.0067E- _
0.068 6.0985E-03 0.018 4.8255E-
0.091 5.5507E-03 0.018 4.6499E-
0.093 5.1067E-03 0.015 9.9554E-�
0.096 9.7255E-03 0.019 4.2556E-� :
0.099 9.3558E-03 0.020 4.0606E-� :
0.102 9.0223E-03 0.020 3.8597E-� !
0.105 3.7104E-03 0.021 3.6915E- :
0.108 3.4331E-G3 0.022 3.4309E- '
0.110 3.1833E-03 0.022 3.2155E- :
0.113 2.9472E-C3 0.023 2.9891E-
0.116 2.7284E-03 0.023 2.7542E- :
0.119 2.5234E-03 0.024 2.5096E-
0.122 2.3581E-03 0.024 2.9852E- :
0.125 2.1992E-03 0.025 2.9E91E-i.
0.127 2.0329E-03 0.026 2.9431E- :
0.130 1.9003E-03 0.026 2.9224E-i-
0.133 1.7629E-03 0.027 2.9023E- _
0.137 1.6051E-03 0.027 2.3821E- -
0.139 1.5285E-03 0.028 2.3627E-� :
0.142 1.9180E-03 0.028 2.3320E-� :
0.144 1.3350E-03 0_029 2.2920E-�- _
0.147 1.2722E-03 0.030 2.2529E-i :
0.150 1.2043E-03 0.030 2.2138E-� i
0.153 1.1350E-03 0.031 2.1679E-t'1
O.15o 1.072GE-U3 0.031 2.1237E-i'1
0.159 1.0130E-03 0.032 2.0799E-;1
O.lEl 5.E532E-04 0.032 2.0323E- .1
O.lE9 5.19i8E-09 0.033 1.9871E-)1
0.167 8.6712E-G9 0.034 1.9345E-:�1
0.170 8.1225E-G9 0.034 1.8810E-; :
0.173 7.63�5E-��9 0.035 1.82?0�-;�:
0.175 �• ���H-�� O.:i_5 L?,�=:=:-�_�_
Strander Phase 3-MGSFIood
2/22/2011 Page 19 of 22
G.17H r.�BJ,E-:9 V.V3o' _. ��2oE-C1
0.181 E_5124E-09 0.036 1.E795E-C1
0.184 6.2092E-09 0.037 1.E270E-�:1
0.187 5.6915E-09 0.038 1.5805E-C1
0.L°0 5.6799E-09 0.038 1.52E3E-01
0.192 5.4511E-04 0.039 1.4719E-01
0.195 5.2562E-04 0.039 1.4182E-01
0.19� 5.0251E-04 0.040 1.3671E-01
0.201 4.7796E-04 0.040 1.3177E-J1
0.209 4.5197E-04 0.041 1.2E92E-:�1
0.207 9.3605E-05 0.041 1.2206E-��1
0.205 9.1159E-04 0.042 1.1E97E-��i
0.212 3.9395E-04 0.093 1.1205E-���
0.215 3.6E59E-04 0.093 1.0735E-���
0.218 3.5950E-04 0.094 1.02E3E-G=
0.221 3.3573E-04 0.094 9.8391E-����
0.229 3.1985E-04 0.095 5.3952E-0='
0.226 3.025<E-04 0.095 8.9582E-Q�
0.228 2.51EOE-09 0.096 8.5294E-G-
0.232 2.7653E-04 0.097 8.1034E-C�
0.235 2.E281E-04 0.047 7.7113E-C�
0.238 2.5198E-09 0.098 7.3969E-C-
0.291 2.3605E-09 0.098 6.9896E-C;
0.293 2.2599E-09 0.099 E.E571E-CZ
0.29E 2.1371E-09 0.099 E.39°2E-0-
0.299 2.0360E-09 0.050 6.0507E-0�
0.252 1.9E38E-09 0.051 5.7968E-0=
0.255 1.8339E-G9 0.051 5.4946E-,)=
0.258 1.7689E-09 0.052 5.1515E-`i-
0.260 1.6295E-09 0.052 9.8687E-�i-
0.263 1.5306E-G9 0.053 4.6100E-2�
0.266 1_9490E-09 0.053 4.3E25E-_-
0.269 1.3140E-G9 0.059 9.1230E-J=
0.272 1.2563E-G9 0.055 3.8922E-02
0.275 1.1552E-C4 0.055 3.6712E-0�
0.277 1.Oe30E-C4 0.056 3.9609E-G=
0.280 1.0108E-C9 0.056 3.2580E-��=
0.283 9_3860E-a5 0.057 3.0562E-C_
0.286 8.5528E-OS 0.057 2.8762E-C='
0.289 8.1586E-OS 0.058 2.7095E-C='
0.292 7_9366E-OS 0.059 2.5418E-C=
0.2°4 7.1978E-OS 0.059 2.3826E-C=
0.2°7 6.5702E-05 0.060 2.2372E-C_'
0.300 6.2819E-OS 0.060 2.0870E-C:
0.303 5.5926E-OS 0.061 1.9923E-0=
0.306 5.7760E-OS 0.061 1.8145E-0�
0.309 5.0590E-OS 0.062 1.69E9E-0�
0.311 9.7652E-OS 0.063 1.5880E-0�
0.319 9.2598E-05 0.063 1.4839E-���
0.317 3.82E6E-OS O.OE4 1.3805E-���
0.320 3.4ESEE-OS 0.069 1_2873E-���
0.323 3.2990E-OS 0.065 1.1953E-���
0.325 3.0324E-05 0.065 1.1177E-b�
0.328 2.6158E-OS 0.066 1.0485E-0'
0.331 2.4548E-OS 0.067 9.8257E-G�
0.339 2.3626E-05 0.067 5.2394E-��3
0.337 2.1E60E-05 0.068 &.6550E-C3
0.390 i.9494E-GS 0.068 8.0631E-C�
0.392 1.8772E-05 0.069 7.6583E-C�
0.395 1.5162E-OS 0.069 7.1651E-C�
0.398 1.9490E-OS 0.070 6.6850E-C�
0.351 1.3719E-OS 0.070 6.2953E-C+
0.354 1.�274E-OS 0.071 5.8908E-0=
0.357 1.1552E-CS 0.072 5.5327E-1i�
0.359 1.Ob30E-OS 0.072 5.1655E-�i'
0.362 1.OE30E-OS 0.0'73 9.7539E-���
0.3E5 1.0108E-OS 0.073 9.4591E-���
0.3E8 E.6690E-OE 0.079 9.1392E-5:
0.371 7.5920E-OE 0.079 3.8692E-���
0.3,9 .9=1.^_CE-nr 0.D,5 ,.62955-��3
i�.� _ ."s9-»-�)r _. � �. 30==.-��3
Strander Phase 3-MGSFIood
2/22/2011 Page 20 of 22
0.3i9 �.9920E-On 0.076 3.1499E-03
0.3�2 '.9920E-Oo 0.077 2.8673E-03
0.385 7.2200E-Co 0.077 2.6757E-03
0.388 7.2200E-Co 0.078 2.9E92E-03
0.351 7.2200E-Co 0.078 2.26�0E-03
0.353 7.2200E-Co 0.079 2.1191E-03
0.356 7.2200E-Oo" 0.080 1.5480E-03
0.399 7.2200E-C'o 0.080 1.7703E-03
0.402 7.2200E-Oc� 0.081 1.6101E-03
0.405 7.2200E-Oe 0.0�1 1.9664E-03
G.408 7.2200E-Go 0.082 1.3177E-03
0.410 7.2200E-C6 0.082 1.1603E-03
0.413 E.4960E-Oe 0.083 1.0224E-03
G.41E E.4580E-C6 0.089 8.8951E-09
G.41° E.4580E-G6 0.089 7.8120E-09
�.422 S.i760E-Oo 0.085 6.8518E-09
�.425 5.0540E-Oe 0.085 5.9348E-04
�.427 5.0590E-Oe 0.086 5.1890E-04
�.430 5.0590E-Oe O.OE�E 9.3970E-04
��.433 5.0590E-Co O.OE7 3.8916E-04
G.43E 4.3320E-Co 0.086 3.8627E-04
G.439 4.3320E-Cn 0.088 3.8122E-04
��.492 4.3320E-C6 0.08° 3.7472E-04
��.494 3.6100E-Co 0.089 3.6966E-04
��.497 3.6100E-06 0.050 3.6605E-04
��.450 3.6100E-Cn 0.050 3.6100E-04
��.454 2.8016E-C6 0.051 3.5667E-04
G,45E 2.8680E-06 0.092 3.5595E-04
0.459 2.6880E-On 0.092 3.5017E-04
0.461 2.166DE-On 0.093 3.9295E-04
G.464 2.1660E-06 0.053 3.3284E-C4
G.467 2.1660E-C6 0.094 3.2129E-C4
5.470 2.1b60E-Ce 0.094 3.0685E-C4
:�.473 2.1b60E-C6 0.055 2.995EE-04
:�.47E 2.16o0E-C6 0.095 2.B15EE-04
��.478 2.1Eb0E-06 0.096 2.E719E-04
G.481 2.1E60E-06 0.097 2.5987E-04
G.484 2.1660E-06 0.097 2.3?59E-04
:�.487 2.1660E-Or 0.098 2.2959E-04
��.490 2.1660E-06 0.096 2.1O10E-04
J.492 2.1660E-Oe• 0.099 1.9711E-09
=�.455 2.1Eo0E-Ot 0.099 1.6772E-09
��.458 ?.2200E-07 0.100 1.7833E-09
G.501 7.2200E-07 0.101 1.6567E-09 �
G.504 7_2200E-07 0.101 1.6317E-09
0.507 7_2200E-07 0.102 1.5951E-09 '
G,509 ?.2200E-07 0.102 1.4569E-09 �i
��.512 7.2200E-07 0.103 1.3929E-�9 I
��.515 7.2200E-07 0.103 1.2130E-�i9 I
0.518 7.2200E-07 0.104 1.0902E-��4 I
0,521 7.2200E-07 0.105 9.6026E-��`_ i
G.524 7.2200E-07 0.105 8.0869E-�i5
0.526 7.2200E-07 D.lOo 7.3649E-��`
G.529 ?_2200E-07 0.106 6.4°BOE-��°
G,532 7.2200E-07 0.107 5.8982E-OS '
0.535 ?.2200E-07 0.107 5.1°89E-G5
O.SsB 7.2200E-07 0.10$ 9.9764E-05
0.591 7.2200E-07 0.109 3.5378E-OS �I
��.593 7.2200E-07 0.109 2.8156E-G5 ��
0,596 7.2200E-07 0.110 1.7326E-GS I
G.599 7.2200E-07 0.110 1.3716E-GS
G,552 7.2200E-07 0.111 1.1552E-GS
G.555 7.2200E-07 0.111 1.0106E-OS
0.558 ?.2200E-07 0.112 6.0640E-���
0.560 7.2200E-0' 0.113 "0.9980E-0�
0,563 ?.2200E-0' 0.113 9.3320E-?E
�.56� •--''��E-D� _.1_� -._=S�iE-?,
Strander Phase 3-MGSFIood
2/22/2011 Page 21 of 22
"*'Flow Duration Performance According to Dept.of Ecology Criteria""
Excursion at Predeveloped Yz�2(Must be Less Than 0%): -28.7% PASS
Maximum Excursion from Y�Q2 to o2(Must be Less Than 0%): -28.7% PASS
Maximum Excursion from Q2 to Q5o(Must be less than 10%): -93.9% PASS
Percent Excursion from Q2 to Q50(Must be less than 50%): 0.0% PASS
* POND MEETS ALL DURATION DESIGN CRITERIA: PASS
Flo�r Duratian Plat-Shallo�r Pond, 3
arifice
o�
ond Duration Pertormance
Eaccursion at t f2 Q2: -2$.7�6 PAS S I(h
x Excursion t l'2 Q2 to Q2: -28.7 9t PAS S
�� x 6ccursion Q2 to Q50: -93.9� PAS S
96 Pos 6ccu�sion Q2 to Q50: O.Ox PASS_ =��'�-�
x WS El for link t: 26.27 Feet
,-. o.i
� 1 I
U
�
� �� i 1
O
�— � �
�2
�!�
- - - - - - �- - - -
�.1 � '�i1�2
,
nn � �
t De-0r t De-06 �De-�s t De-0� t De-03 t Dr�2 �De-flt t De+�
Exceedance Probabiliiy
/ Predeveloped j Postdeveloped
Strander Phase 3-MGSFIood
2/22/2011 Page 22 of 22
Drainage Calculations
Pond Volumes
Phase 2 Pond
Detention Volume
,..�- ._,�y�--Y-��, Elev Area Vol Total Vol
�� (FT} (Sf) (CF) (CF)
�. /
�" � 24.0 21613 � 0
.
; ,
,
�,;`� 1
25.0 23750 22682 22682
, : .
��,, +� ' 26.0 25950 24850 47532
�\ ` 26.7 27558 18728 66259
`
� Cell 1(below berm)
� � t Elev Area Vol Total Vol
� (FT) (SF) (CF) (CF)
� .
' � 19J 3435 0 0
20 3689 1069 1069
� ��� 21 4483 4086 5155
�. ,
22 5322 4903 10057
22.7 5915 3933 13990
Cell 2(below berm)
Elev Area Vol Total Vol
Det Total Vol: 66259 CF (FT) (SF) (CF) (CF)
WQTotalVol: 56057 CF (CeII1+Ce112+WqAboveBerm) 20.6 9153 0 0
21 9675 3766 3766
TotalVol: 128708 CF 22 11003 10339 14105
(oet+wQ+�w) 22.7 11897 8015 22120 ,
Pond Grading wC1(above berm) �I
Pond Ex: 6744 CY Elev Area Vol Total Vol �
Pond Fill: 1563 CY (FT) (SF) (CF) (CF)
'Quantities above include 370 CY for key-in of pond berm 22.7 18862 0 0
23 19539 5760 5760
23.7 20997 14188 19948
Groundwater Storage I�
Elev Area Vol Total Vol I
(FT) (SF) (CF) (CF)
23.7 20997 0 0
24 21613 6392 6392
Drainage Calculations
StormSHED Calculations
Gi�-en that description, it is essenriall�� travel time shift. Tra�el ume shift as
implemented b�� StormShed2G has a slight �-ariauon. Since the h��drographs are
stored in a specified time intereal (the default is 10 minutes), a tra�-el time of less than
the inten�al «�ould require a shift to an odd interval. In order to do this correctl}', it
�vould mean interpolaring the values. Unfortunarel�- interpolating �-alues ��-ould
compromise the peal:over rime as one ne�-er interpolates up,just do��-n.
To avoid such a situarion, StormShed2G accumulated the tra�-e1 rime until it esceeds
the h��drograph rime step. At that point the program shifts the h��drograph the time
step duration and carries o�-er the remainder to be accumulated in future reaches. Tlvs
alle�7ates the necessitt- of interpolating peaks bet«-een rime steps and does not
compromise the peak.
Actually,compromising the peak�i-ould probably not be a bad thing since the ph�-sical
realitt= of h��drograph routing is moxe accuratel�� modeled b�- the �fuskingum-Cunge
n�pe methods, but in this case, compromising the peaks also affects the h�-drograph
volume,��-hich is unrealisuc.
Hydraulics of Storm Sewers
Bemouni Equation
t1'��.._'_____..'._'_............ ....... . . . ... ...... . ...... +
F �[�� �.''��.`�.
C'
`"-- '— -.�.`'�t_'�, h�--
_r+'- i�� �_�
•—.. H� •-�.
y '�•- � _.
•�- _ _ `.:_!2g
.�,_
.�,,
�-. ,.,., t;hamecl Bon� .
Z, , �
[la�urn --Z:
Figwe 14:Tertns in Brmou!G I:yuanun
�� Z
g +y, +Z, =ig +y, +ZZ +hl,_,
'I'l�e Bernoulli equarion is the basic equarion used to balance the energies associated
���th graduall�� �-aried flo��- through prismatic channels. �k'hile the �-elocih- (�-� and
datum (Z) data is generall}� l:no���n, most of the effort in the design of storm se�ver
re��ol�-es around esrimaring the losses(hl,_�.
Friction Losses
The equarions relating to fricrion loss hace been discussed in Chapter 2. The fricrion
slope is ripicall}- back computed based on the ��elocitt� or discharge and the kno«-n
cross secuonal properties of the channel.
s7
Transition Losses
Transition losses occur when storm «-ater enters the se«-er svstem and encounters
h��draulic structures such as manholes, bends, contracrions, and enlargements. Each
h��draulic structure that is encountered�rill result in a loss defined as:
i''
H = K—
2g
�t'here K is a loss coefficient.
Contraction Losses
L
H, =0.1 ��— �' �'�>�'.
2g 2g
Expansion Losses
V` V_`
H, =0.2 —' —— V, >p, !
2g 2g
��'here V,is upstream velocin�and�',is do«�nstream�-elocin'.
Manhole Losses
In straigl�t dlrough situations �-here there are no changes in pipe size and the slope
remains constant through the manhole:
,�
Hm =0.05�
g
Entrance Losses
The coefticient for entrance losses depends of the conduit See Appendix for a list of
coefficients used b�-the program.
Junction Losses
Losses at junctions�vere there are one or more incoming larerals:
z �
�H J +D, —Dz� A, + AZ� _ Qz _ Q, _ Q3 cos O
2 A,g A,g A;g
��'here D, and D,are the approach pipe diameters and O is the angle bett��een them.
Bend Losses
Bend Losses are estimated from
62
Vz
Hb =Kb 2g
��1�ere Kb =0.25 �0 , �=central angle of bend in degrees
For angles less than 40 degrees. If the angle is greater than 40 degrees, it can be
estimated from the follot��ng Chart.
1.4
j1.� A�Jlerior . .
� . . . . . . , .
I
�
II 1.�/ Lbried
�4
«-�i . . . . . . . , . . . �'� ,�,.`Y � . .
� , . . . . , , . . r, ,
�;. . . . . . . . . . . ,t. . .� . . .
� �3_a `'
�I •^ . .
� . � ;�a
� . . . . . _ , . .o �? . . , .
, .�.., . fi �,
tl% ��.� �Q
�; � . u�
�`•
� �� . � . . �
?'e �L L
;, ,� �',4
�I �.� .
. . : . : . . . . . . : . . .
� : . . . . : . . . : . . . .
� (? �� 4() �� �� 1 t?�
Deflectioii An�;l�, Y — in c.lz��ree�
Fi��ure 15:Se�cer Bend]_uss Coefhde�t
Direct Step Profiles
StormShed2G uses a direct step profile computation «�hen flo«- profiles are needed.
Generall�r, this«-ill be for cul�-ens and other reaches. The direa step method is fairl��
straightfon�-ard and can be duplicated on spreadsheets �vith a little work. ��'hile a full
discussion of the theon� behind the procedure is outside of the scope of this manual,
an e�arriple of the spreadsheet process is in order. Gi�-en the geometn-of a reach, the
flo���rate(cfs) roughness and slope,the steps for filling out a spreadsheet is as follo�s-s:
63
Y A R Ra;� p aV` l2g E DE Sr Sr Sp —S� 4x �i
(1) (�) (3) (4) (s) ��� C� (g) (�) (10) (11) �12� �13�
Co11. Depth of flo�r in ft.
Co12. ��'ater area in s.f. corresponding to the depth��in column 1.
Co13. H��draulic radius in ft corresponding to��in column 1.
Co14. Four-thirds po��°er of the h��draulic radius.
Co15. l�fean velocittT in fps obtained b�� di�-iding the flo«- rate b�� the water area in
column 2.
Co16. Velocin-head in ft.
Co17. Specific energ�-in ft obtained by� adding the velocin� head in column 6 to the
depth of flo«-in column 1.
Co18. Change of specific ener�-in ft, equal to the difference betz��een the E �-alue in
column?and that of the pre�7ous step.
Co19. Friction slope computed b�- soh-ing for the slope using �Ianning's equarion,
using values from columns 4 and 5.
Col 10. �verage friction slope bet«�een the steps, equal to the arithmetic mean of the
friction slope just computed in column 9 and that of the pre�-ious step.
Co111. Difference between the bottom slope and the a�-erage friction slope.
Co112. I.ength of the reach in ft bettieen the consecuu�-e steps computed b��dividing
the value in column 8 b�r the�-alue in column 11.
Co113. Distance from the secrion under considerauon to the starting point of the
computauon.
The procedure is taken from Cho���, Open Channel H��draulics, llcGra�v-Hill Book
Compan�-, '_�e«-York, 1959.
64
M
DR1-SD2
11756.60 SQ FT
0.2699 ACRES =_-_��-T----_- DR2-SD3
DR2-SD1 5408.51 SQ FT
' 6105.29 SQ FT 0.1242 ACRES
� 0.1402 ACRES
. - - _ _
_ � �
< - - -- - _- ____ - - - - - - - - - - - - - - -
• - _ _ _ - _ _ : - f • - - - - - -
,�.
0
z
h
u , � DR2-SD2 DR3-SD1
-Q �i r' 5983.11 SQ FT 6883.63 SQ FT
■-x-x-'-'� 0_1374 ACRES 0.1580 ACRES
I g O
�z
� ■ —
._---`y`3.�–t---.- . - - '—_
d `�
j I ��`r
L. � z.
_c—:—.` ' '•� ��,.
�\��Y
��
`�`�.
� �
}� _�Y Y Y %
�_____�_���
I
� �� / "\��\q�G I
/ ;� O
. '���','�� 1��I
/ 11 11'�1 �
.�� ��� \� /���� �N �I
, �.� / ,� ;;�� �
�' � � :i •;,
�' � \ i:��y I
�� / \
I ��,i, \
I �i;�ll,�l,%� ------------- ' I
/ I
'��Ir` J
�„� ��� ,
�° �;'� � ;� - .-.-,
W N;� ��i "'
V a�i i�� 'll � `/
Q '�1;� ;1� �';�r,�
IW i�h%;I ;i' i�''�iN 'I'i
2 ��r r' iji �i� jl�
i M�i ii i�i !i�� '��
t uii�i� ��r i�f4 i;i
uii � r�r r�4 i i
M� /
�ill �l ��ji i�9y = I�� .
��I 1� �1� �j N i j I
11.i � �I�( 1� �I I
(I��I %%%(11�r+ il�ll
%( '1
1�..�'. , � !vl , I�i
Appended on: Monday,luly 18,2011 12:05:41 PM
r,,�-11 i_'� I�I-'F --- _
IIUR �,'�,_F-� � � ���
�`� � P-i90�� P-205aR P-2200R
P-175�R
N-P�P
ROUTEH�'D�] THRU [Strander_Ph2J USING�25��r] AVD �Seattle]NOTZERO RELATIVE RaTIONAL
Ratiaial Med�od analysis
_�---- ---- _ _ ___ _ _ _
Reach Area TC i Flow Full Q Full nDepth nVel fVel
ID , (ac) (min) :(in/hr) (cfs) (cfs) ratio ({t� Size �ft/s) (ft/sj CArea
-'_ ___ ------'-- _--- --- ----- -- __ __ _ ------- , �-- __ - -__--
P 0.158 5.�0 2.8938 � 0.4115 ' 9.265 ' 0.0444 � 0.1435 I 12 in ; 5.9377 11.7965 B
2200R ' I i � � Diam 2200R '
I ' ', I i I �
�
---- r � -�-�I I 12 in . � g_ I
P 4 0.282 5 421 �2.7704 I OJ031 ' 9.6302 0.073 , 0.1828 � 7.1533 : 12.2616 '
2050R ' � , Diam , 2050R �
i I
-- ----;----__ -- -_ - - -;-----�_ - �I_-� �.---- �----�
P � 0 419 ' SJ705 '2.6787 ' 1.0101 �r 4.3235 !0.2336 � 0.3283 12 m ; 4.5006 i 5.5049 B !
1900R t i � Diam �; '� 1900R .
i,
, �
P- -. -__r-----� - ---� r---- �------� _-12 i n . _ ,---_ . _6--I
0.559 i 6.326 2.5492 11825 3.9719 0.3229 ; 0.3879 4.5551 : 5.0572
1750R � � I Diam ', 1750R
; i �
i
-r- � �- � - �--- ' i
P- �� I 36 in �--- B-
I 0.829 ;6.8 47 8.2.1 4374 � 1.8186 ^75.2934 � 0.0242 , 0.322 � 4.4554 ! 10.6518 !
1600R ! i ' ; ; �' Diam ! 1600R
i ;
j i i
HGL Analysis
-------r- ----._ - _-- ,
From Node I To Node HG EI(ft) '; App(ft) , Bend(ft) Junct Loss(ft) Adjusted HG EI(ft) �Max EI(ft) ;
--__----- -----__- --- -_ _ _ --_------- - ------ ---__--- ;-------
( 0.00
No approach losses at node N-1750R because inverts and/or crowns are offset. � � � '
---- -____ . .- --___ --- •--_- ------- _-- !
( N-1600R ' N-PUMP 0.0514 ( -- - ; 0.2089 ------ � 0.2603 9.5000 ':
� � ' � ; ' I
� ;
____�.------------_________-------I
No approach losses at node N-1900R because inverts and/or crowns are offset. '
r-----,r-- - -�
N-ll50R N-1600R '; 7.2594 � 0.0031 � ------ � 7.2625 � 10.2200 i
I ; . I
- - .___ , _ ___- - ---- - - --__ -- --- r__ ___- _ __ __ _--- - '
i N-1900R ; N-1750R ' 8J902 ; -- --- ; 0.0091 i ------ � 8.7994 11.9940 . i
� ' i '
; ;
---=- ------- -------____-- ----__ _
�No approach losses at node N-2200R because inverts and/or crowns are offset.
I
�.._- - -- __-- � ._--_ - �--_ ---- --- ---
� N-2050R N-1900R ' 15.2127 � ------ 0.0039 , ------ j 15.2166 18.2860
; � �
�___ . ____ -�- -'� ----- _ _ _._ _------__ ___ -- _
� N 2200R � N-2050R i 21.4719 �----- ' ----- ------ � 21.4719 24.6280
� � ' , ,
ConduitNotes
._ _ --_ _ _ _ _ _. __ _ . . _
` Reach 'HW Depth(ft) HW/D ratio Q(cfs) ;TW Depth(ft) !Dc(ft) ,Dn(ft) Comment
----- _ ____ - -- --- __ __ __---- --- - _ _ _ _ _ _----- -___ .
P-1600R 0.5514 0.1838 1.82 0.8920 j0.4110 0.3220 SuperCrit flow, Inlet end controls
r ______ ------ --,---- ---- --- - -------------------
�P-1750R ; 0.6794 0.6794 , 1 28 I, 0.4783 ;0.4783 i0.3879 ;SuperCrit flow, Inlet end controls
� ,
;- ----- ---- _ ---- __ ;---- - __ __ _ - _ _ _------__--- ------
'P-1900R �0.5902 , 0.5902 ' 101 0.4223 0.4223 �0.3283 SuperCrit flow, Inlet end controls
' , i
- --- ---------- �0.3497 �---f------ --- -
r --------
�P-2050R 0.4627 0.4627 0 70 ' 0.4994 I0.1828 ;SuperCrit flow, Inlet end controls
'
� '
r-- ;_ ____- - ---- - � �-__ �---�- --------- -------
�P-2200R : 0.3419 0.3419 0.41 0.2652 �0.2652 ;0.1435 jSuperCrit flow, Inlet end controls
Licens.ed to� � ���6��� . �
ROtiTEH1'D [] THRU �Strander_Ph2] LSInG [50 yrJ Al�D [Seattle� NOTZERO RELATIVE RATIONAL
w-soi-soi
s�� r�,��,-s�� .__�_�,,
�-SD1-$C�• P�1_Sp., �"
5
O`
u
O
� '-_?-;D2 N-SD2-SD3 N-SD2-SD4 IwS02-SD6 IwSC�3-SG1 ti SD3-SD�
P-SD2-�PS�2�Sa4#p-SD2-�505 �h P-SD2-3D6 �P-SD0.��PSaiSDJ
�
�
C
ti
CI
I
. -.i,..�.�
�
Rational'�iethod aoal��sis
__-- - ---- _ _ _
Reach Area TC i Flow Full Q Full nDepth Size nVel �'e� CArea
ID (ac) , (min) (in/hr) (cfs) (cfs) ratio '; (ft) (ft/s) '; (fds) ,
_ _---- - __ -- - - -- - -r-- - - - -- -_ _
P-SD1- � ' 1? in B-SD1-
0.0185 5.00 3.2778 ; 0.0546 10.765 I 0 0051 ' 0.0511 3.5944 : 13.7064
SD1 � ; I Diam SDl
P-SD1- - i -__ - -- ;- �1�in�- ;----;B-SD1-
SD: 0.0697 5.5022 3.1113 � O.195� ' 7.3138 '; 0.0267 � 0.1126 Diam � 4.012 ' 9.3122 ', SD�
' � i I ( � '
r--- --
P-SD�- I, � �� 12 in � � =, B-SD?-
0.0844 5.6701 3.0607 0.2325 5.1708 ` 0.045 0.1444 � 3.3273 � 6.5836
SD1 j � � Diam i i SDI
P-SD3- � �� ' �----�-- ��' �- -- � 12 �n � i �� B-SD3-
0.05 I 5.00 3.2778 0.1475 3.3217 ! 0.0444 0.1435 � 2.1286 i 4.2293
SD2 �, �i , � Diam ' ' SD2
_ - ----r-- �-- �- -r-----
�-------- -- -----
PSD13 ' 0.1006 5.9576 ',?.9793 � 0.2697 ' 2.9853 � 0.0904 0.2031 `. Diam ',' �•3601 � 3.80ll � B'SD3-
� ; � � SDI
P-SD2- � I- ( 12�n B-SD?-
SD6 i 0.2661 ; 7.37 ,2.6531 I 0.6354 ' 4.7203 0.1346 OZ477 ` Diam ; 4.1913 6.01 , SD6
P-SD2- �---- I--�-� �' ]2 in r � � B-SD�-
SDS 0.3522 ; 7.7676 ',2.5782 0.8172 10.1256 '; 0.0807 0.1918 : Diam ; �•�626 � 12.8923 . SDS
, i
r_...-_ r-_-�_-�_�_.
P-SD?- � ----�.i- --�� i-�- : 1�1❑ ! ' B-SD?-
SD4 0.4822 i 8.0897 2.5?18 1.0944 ', 2.0193 0.542 0.4374 :, Diam ; 3.7737 ' 3.702� ' SD4
� i 1
P-S�2- � I 1 I-_- � I21❑ f_- $-5��-
� 0.6098 8.6462 2.432 ^1.3347 � 4.2327 0.3153 0.3843 i 4.8007 5.3892
SD3 ( �; � i f Diam i j SD3
r--r--- �--
P-SD2- ; 0.�719 8.8 6 ��. 114 5 1.6753 I ?0.8514 I 0.0803 0.3826 � �4 in , 3.9913 ' 6.6372 i B-SD?-
SD? Diam SD?
tiu�andcr Pha.�2-511 l�car Stonn-�tom»hcd Ruut�Rep��rt I
HGL Anal�•sis
�From l�ode ! To Node HG EI(ft) ;App(ft) i Bend(ft) I Junct Loss(ft) �Adjusted HG El(ft) {Max EI(ft) �
.-- - --_ _____�______ __._ __�_ , ..___ .__-_______________.__ ___, _ ______
__ __ _ ..
1.5692 �
`No approach losses at node N-SD2-SD3 because inverts andlor crowns are offset. ���___�_ ____,________�
€
___---.-----_---,--�__.____.___.�._.___..._---------.____________ €
- -
N-SD2-SD2 f N-PUMP 2.0029 , ------ ; 0.4933 j�� 0.0483 � 2.544� ; 10.8150 =
Tv-SD2-SD1 � � ����#
_- ___._ _..______._____ __�___
� ;N-SD2-SDZ 8.0553 ; ------ 0�2278 ------ 8.2831 � 11.1600 �
�_________a�__�._____��_�_._ �; _ __,
N-SDI-SD2 jN-SD2-SD1 ' 93375 ; ------ ! 0.00�3 � ------ 93427 1� 6480 �
______ .__ __._�_ __.__�__;.__ _. �� ___ �___� __;
N-SD1-SDl iN-SDI-SD2 ', 16.3437 ' ------ �----- `� ------ E 16.3437 � 20.1800 �
, ; �
___------�___-----------_.-_�______.__--- ---------------
No approach losses at node N-SD2-SD4 because inverts and/or crowns are offset. J --______._____�
_-- ---�_.__.�_____.�_______� �
N-SD2-SD3 ;N-SD2-SD2 7.7964 � ------ �OQ24�; ------ ��� 7.7988 i 10.3460 I
� i ,
______.�_�._�__._�___._�;�._____�--�----_ .____�__� '
�N-SD2-SD4 :N-SD2-SD3 ; 9.6443 1 ------ ; 0.0102 ; ------ � �� 9.6545 t 11 9550 �
� ___�.��.__ - -.r__ �___._._ �_ ___ _�___._� �___.__________,
'�o approach losses at node N-SD2-SD6 because inverts andlor crowms are offset. �
____ _____________ _ r._________ �
_____r _.
___.�____��d_�� �___�._�._.__t.e .
N-SD2-SDS j N-SD2-SD4 17.9179 � ------ � 0.0017 ; ------ j 179196 ; 22.4100 �
_-�____�_______..._...._.,._..._.__-----:- `
�__.__---- ---
N-SD2-SD6 ;N-SD2-SDS 20.9375 ; ------ il0.0005 j ------ 20.9381 ; 24.5600 �
____�__�_.__ _____;�_--__ � • _�_____�.�.__�i
N-SD3-SD1 iN-SD2-SD6 ; 21.8729 r ------ 0.0007 ' ------ 21.8736 26.5600 ;
__..._____.___
� . ,.________________.._;
N-SD3-SD2 N-SD3-SD1 ' 22.6514 �_ ------ -- -- ; ------ 22.6514 ; 26.5400 ?
, --
Conduit Notes
�____ .__ _� __.____� .______ _ __ _ _.,_
--- - - ----�-r--.__ _... __.______. ___ �_
Reach ��'�'Depth HW/D Q TW Depth Dc(ft) �n Comment � �
(ft) ratio ; (cfs) ; (ft) (ft) �
___ . .____ r .� -____.___��_ _ __,__,_ __ , _-� --____ _______�;
_----- ----- ---,._, _ ____._.. ._.___
P SD2- 0.3014 1 68 j 0.4192 ,0.4482 0 3826 SuperC'rit flow,Inlet end '
��� SD2 � 0.6029 � �controls
F : ----- ---_ -----_
_ _______ �._____w_____ ,�_�_ __-- -��_ __ .
P-SD2- � 0.2603 0.2603 ; 0.23 ` 0.1979 �0.1979 0.14� SuperCrit flow,Inlet end
� SDl � ' I �;controls
____,____._. � ' : '
�__________,____- ---- ;-- r ._�____._____________
� P-SD1- � 0?295�� 0.229� � 0.20 � 0.3881 i0.1813 ;0.1126 ;SuperCnt flow,Inlet end
� SD2 ; � � jcontrols
�� P-SD1- 0.0947 �0.0947 ; 0 OS ` �0.1347 I 946 i0.0511 �SuperCrit flow,Inlet end �
SD1 ; � �controls
_.___ ____________� _�___ ____�
P-SD2- 0.6964 0.6964 t � ��� � ��Su erCrit flo�u,Inlet end �
� 1.33 i 0.4885 �0.4885 i0.3843 � p
SD3 � i fcontrols
--__-___r-_�_____._�___._.i-----------�----- r- r-------- ----_.�__.________` �_._�_____._._ �
P-SD2- ' j � �SuperCrit flo�v,Inlet end�
SD4 0.6843 0.8212 � 1.09 � 0.4660 '0.4660 0.4374 �controls
____.__ "_______�_______ �_______e_ _�
���_�w____ _���______� ___�__�
P-SD2- � i. �SuperCrit flo�u, Inlet end
0.4979 0.4979 ` 0 8� ; 0.8625 0.3782�0.1918 ;
SD� i i ;controls
__�_____ _______ _______ r_�_______ _ ,__ _,_.._____. ___.__� ---,�__._.___; __� __ ___.�_� ___w__�_.______
P-SD?- a f � ' �Su erCnt flow Inlet end i
'� SD6 0.4�15 0.4515 , 0.64 � 0.333a �a.3320 i0.2477 lcontrols
--- _ _______.�____.____
t _e_�_.__ �_�� e__�__��,__s___�_________ _ �_
P-SD3- 0.2869 0.2869 ; 0.27 � 0.3521 ;0.2136.0.2031 �SuperCrit flow, Inlet end�
' SD1 ' � ; i (controls
� : a .�
P-SD3- � �� ! � �� SuperCrit flow,Inlet end
' SD? ! 0.2084 0.2084 0.15 0.1876 '0.1569 0.1435 �Icontrols
Strander Phase 2-50 1'ear Storm-Stonnshed Rouce Report 2
i
Appended on: Monday,July 18,2011 12:05:41 PM
ROUTEHYD [] THRU [Strander_Ph2] USI�IG �2���r] AND [Seattle] NOTZERO RELATI�'E R�TIONAL
Rational Alethod analysis
�_ , __��__� _____ ___---- ----___ _._._ ___..._____,__�,-------
_�______ _ _-____ ____._
Reach Area '. TC � i Flow Full Q ' Full nDepth nVel fVel
i ID ; (ac) ' (min) ',(in/hrI ', (cfs) (cfs) ratio ; �ft) Size (ft�s� �ft�s� CArea ;
�� � � --- - . _ _-- - ---- - __ , � � r 12 in �_ - __- _ ____� �B
0.158 5.�0 2.8938 0.4115 9.265 0.0444 i 0.1435 ` 5.9377 11J965
'i 2200R ' Diam ', 2200R '
i
;
- -- --- = --�- -- r- �-- - r---- ----
� P 0 282 �5 421 !2.7704 0.7031 j 9.6302 ': 0.073 �8 �12 in ! �.1533 ' 12.2616 B
2050R ' Diam , 2050R
: � �
r .___ r__�_�. .__.__ __--- ------- - - � __^ __._ _, _------- --_.__
P 12 m B-
� 0 419 •5.7705 �2.6787 1.0101 4.3235 ; 0.2336 ' 03283 4.5006 ' S.5049
; 1900R ! � i '• Diam 1900R
� E
�__ _.__._ �__,__�_---,__ _.._._ A___.___._�_____� __---- - _._.____�__ ----- -- ----.�_. -.__.__
P- � 12 i n B-
0.559 6.326 :2.5492 1.2825 3.9719 ; 0.3229 � 0.3879 � 4.5551 5.0572 '
; 1750R i I Diam ', 1750R
;
�___ _ _ _ �� � � i �__ ,_ _�___.___
P ���.���,; �i � ; 36 in B-
0.829 ;6.8748 i 2.4374 1.8186 75.2934 � 0.0242 : 0.322 i 4.4554 10.6518
; 1600R ': ' Diam ' 1600R
i
HGL Analysis
From Node To Node HG EI(ft) ; App(ft) Bend(ft) Junct Loss(ft) ; Adjusted HG EI(ft) Max EI(ft)
i i i
-_�_____-_----_-----------------_�.__ _..---------_ __ _---- -
r_____�,__________.�.__--______ r_.
0.00
�No approach losses at node N-1750R because inverts and/or crowns are offset.
I
;---_- ��-- �- ��--- ---� �-- _- ___ ___.�__- � - - �-- --- ----- �- --
' N-1600R ' N-PUMP ' 0.0514 ------ i 0.2089 ' ------ 0.2603 � 9.5000
i
, i
�No approach losses at node N-1900R because in�erts and/or crowns are offset. � � �
;
:_____ � ______�. _ - - -� _---___ _ --.---_-------- ..� _____
� N-1750R N-1600R 7.2594 j --- 0.0031 ------ � 7.2625 ; 10.2200
I i ,
--- :-- � �
- ----�-�--------
N-1900R I N-1750R ; 8J902 , --- ; O.OQ91 ------ ( 8J994 11.9940
1 i ; E I
� �
;N po a proach losses at node N-2200R because inverts and/or crowns are offset.
�--_ _.______- ----_�_�-----_____ � - - ----__,__ _.-._ .__----._ ___._�____,_.---__._.____�_
N-2050R ; N-1900R ' 15.2127 j---- ! 0.0039 ------ i 15.2166 ; 18.2860
i ; I '
� ,
' - -_ _---- ;- ---- ----- -- - � ----__ - --------
�_--
; N 2200R N-2050R : 21.4719 ; -- --- - 21.4719 i 24.6280
� ( i i
Conrluit .'Vutcs
Reach HW Depth(ft) HW/D ratio Q(cfs) TW Depth(ft) Dc(ft) Dn(ft) Comment
__ _ _ _---- _-----__ _ --�— -- ---
P-1600R 0.5514 0.1838 , 1.82 0.8920 0.4110 I0.322Q 'SuperCrit flow, Inlet end controls
' , � i
._----- --- - ---- -- _-- P-
rP-1750R 0.6794 0.6794 1.28 , 0.4783 0.4783 0.3879 Su erCrit flow, Inlet end controls
�
�P-1900R .---- - — -- --- --_. _ _ --- _ . - -----
� 0.5902 0.5902 , 1.01 ', 0.4223 I0.4223 0.3283 SuperCrit flow, Inlet end controls
, i
i ', i
- ___-- �_ _.---- - ,--- _---- __----- --- ---
�P-2050R � 0.4627 , 0.4627 ' OJO ' 0.4994 �0.3497 I0.1828 SuperCrit flow, Inlet end controls
II `— ,
--- - � -- ---- � - - _ ------ — ;- -_
;P-2200R ; 0.3419 0.3419 0.41 0.2652 !0.2652 0.1435 SuperCrit flow, Inlet end controls
Licensed to: BergerABAM
Layout Report: Strander_Ph2
f�-i EuuR ��=F� �,, _
P-175�R P-ti9i1ClF'c P-2U50R P-�20��
N-PI�F
�
Appended on: Monday,July 18,2011 3:03:01 PM
Layout Report:Strander_Ph2
Event Precip(in)
----r--_—_
;other � 2.10
�
�yr 24 hr 2
; i
15 year � 3.50
�
I
� �10ear � 4.00
Y
I
.25 year � � 4.25
� I
100 year S 1
� � � � i �
Reach Records
Record Id: P-1600R
�Section Shape: � Circular �
____.________ __ _—_-_------- - .---- �_. ____- -----______n��_ _r�__._ e______ _a
Uniform Fiow Method: ' Manning's Coefficient: 0.01
__.__._ __ . __ .._ _ _
- _ .----- -_ __ _ ___
______ _______ -----,— ___._____. ______----;
Routing Method: Travel Time Shift Contributing Hyd �
i
_ _--- -_ _. --_ _____ ��__— ------r--- ____---------� ��
DnNode ; N-PUMP 'UpNode � N-1600R
. I
;
_ _ ____ _ _ ___ ----- -.-- ------______��__.� �
Material unspecified ;Size i 36 in Diam
i j
--__ _— � ---- �----- `— --- --- �--__ � ----------- .----_--'_---- ---�
Ent Losses Groove End w/Headwall
� i
_ . ____�______ �__�_ � _.--- --- --___r-- ____�,
Length 120.00 ft ,Slope � OJ5% i
;
_._ ___. __.__ _ .__.._
Up Invert -0.50 ft �� �Dn Invert � �-0.892 ft �i
Record Id: P-1750R
� _ .___e _ _ — _ __�_� --_____ _--- -------,- -�-- --------,
Section Shape: Circular
Uniform Flow Method:� � � Manning's �Coefficient: �_�� - 0.012 ��
------_ _____.___ ___._ ___ ___ ,__---- -_.__-- ----__ _..__. _.____ _ � ----
'Routing Method: Travel Time Shift �Contributing Hyd
�DnNode ��� � � N-1600R � UpNode � �� N-ll50R
�
�
---_____ __ -- ---- ----- ___ �_____� _ _____� �_� __ - — —�
;Material unspecified ;Size 12 in Diam !
.___.._ _ _ __ _ __ __ _ _____._____ _ _- --_.____ --- _ __ ______ _ __. _.____ _,
Ent Losses Groove End w/Headwall
I
__________________._�_ , __--__ r.______—�___._ _,--------- - �____________. __�,�w_���— -, -----,
�Length 15a.00 ft j5lope � 1.05% �
' I
Up Invert � �� � v' 6.58 ft ':Dn Invert ��� 5.00 ft � �
° � I I
Strander Pha,e 2 Layout ReFxi�t 2
Record Id: P-1900R
�Section Shape: � Circular
�
�Uniform Flow Method: � ����� �_���Manning's �Coefficient: � 0.01
i
r_..___ --.--. --_._._ ._...__ ----..__�_. ._ �_� __.__.__� d.._,_. ___
Routing Method: Travel Time Shift ;Contributing Hyd !
;
��� -_-- ----_ _,._ __ __----_ �___- -- --_.� � ___________________ _.------_----__ -� _ _�___________ _.;
DnNode N-1750R ;UpNode N-1900R
�---------______ _ _� �__ _ � _ � _�_ ___a _ �—_ _�a__�_ _�� � . _��. __ _
Material unspecified Size 12 in Diam ��
;------,__a______--------____.__�___.._------.--�__--._._._..___._._------._-----.--------__------.____------...__W�r___.._;
IEnt Losses � Groove End w/Headwall
i '
- -
iLength� 150.00 ft ESlope E 0.87%
�_ -_ __.___ ________-___.____---___� �___
__.,_.__.---_.___._.__,._-------_ __.__ �_ �__�.___�____�___� __._,_ ___.___-- ---__�_ �.____ ________.:
Up Invert 8.20 ft Dn Invert 6.90 ft
Record Id: P-2050R
_,__.. -----�__ �
Section Shape: Circular
__.___--- - _�-_._, __ __,___________��--- ------ . ___ __._��_ ___.---- _ _ ____,__- -------.,
'Uniform Flow Method: Manning's Coefficient: 0.01 �
_ ----- -----__..__,�_ _ - �---_---__--_____ .---- --- ------ ------ -.._.---------
Routing Method: Tra�el Time Shift ;Contributing Hyd
_______._._, _ ___.__._ --�___. . __-_--- �__ _.___,.__��____________�_ ______._ ______ ___--
DnNode N-1900R UpNode N-2050R
Material � � ' unspecified Size � �� �� 12 in Diam
- - - -___w,.�_
Ent Losses C W� ��v=vTT�^ Groove End w/Headwall
Length�__�_ _.___ _�— _�___ . - -�-�--150.00ft ^^ ^ �Slope �____________��� � 4.30%� -
________ .__ _..____ ._,______ _.. _�_.___ , ___�_ ___.------____ _ �____, �______._____m____ ____� _ _.� .___ �_�________ .,
Up Invert 14J5 ft Dn Invert _8.30 ft
_ _ ___ _ _ _ _ . _ _. _ _ _ _ _ _ _ _ _ _ _
Strander Phase 3 Layout Repott 3
Record Id: P-2200R
!Section Shape: � � � Circular
I
�_.-- ________ ..__ — - ._.�__________ _,____� _ _ ____.
;Uniform Flow Method: Manning's Coefficient: 0.01
--__ --- _- - ---
_ ---- ---- --__ ___
,Routing Method: Travel Time Shift Contributing Hyd
---- ----- ---- _�_ _____ � .____ ___�______� ____.___ --- ----- -------- _ _------,
DnNode N-2050R UpNode N-2200R �
� ------------�--- ----- --_...__ _ —__— _ _—-- ----- - ------
i
Material unspecified Size 12 in Diam i
�
;
--- -_-- - -�- -- --- �— - --� ----�---
Ent Losses � Groove End w/Headwall �
_-- - - - -
Length 150.00 ft ';Slope 3.98%
_ _---..__ _.__._ ___._ _____ _ __,_ __---._____�_ --_ _. _ __. ;.______________� _
,Up Invert 21.13 ft Dn Invert 15.16 ft
Node Records
Record ld: N-1600R
_ _- —�_ __ - -— - � ---- _--- ---- ---
iDescrip: :Prototype Record Jncrement 0.10 ft
IStart EI. �;A.50 ft � �Max EI.�� �9.50 ft �
�
�Void Ratio�100.00 �--__� ____�____,_�_�-� �_-----_.__ ---_�_��_
(
_----____ -- -- _ _ _ ---------- ---- - ----- -
Condition ,Existing Structure Type ,CB-TYPE 2-54
,
,—���______ _ �
iEnt Ke Groove End w/Headwall(ke=0.20) Channelization No Special Shape
i '
,
,_� --�,---- _�� ______—--- ------- -----
�Catch i0.00 ft Bottom Area 15.904 sf
�
!MH/CB Type Node__�_____________--,-------- ---- - ---
Strander Phase 2 Layout ReFx>rt 4
�
Record Id: N-1750R
_ ,_ ._ _________ __._� _ . --__, --- _--- --_ -- -,---.
iDescrip: 'Prototype Record Increment 0.10ft
�Start EI r4 58 ft � iMax EL '10.22 ft
; �
�
�------__
�Void Ratio ;100.00 �
� �Aj
r
� _� ____________ _________ __, ._� ____.__._ �_�_____._____.__ ,--- -- --------___
�Condition Existing 'Structure Type ;CB-TYPE 1
�
Ent Ke ;Groove End w/Headwall (ke=0.20):Channelization ,No Special Shape
�
� �
�---------;-.--_..___--___----_____ ________ ___�_._.�.__--_ __�— --___._. _._
;Catch i0.00 ft Bottom Area 3.97 sf
�
�
; , _---- - --- --- —�_______._____ _ �._._ . __ �
r���__�__ _______ �---—-
�MH/CB Type Node
Record Id: :�-1900R
_-___ _ .._ ; . ---._ _ _
:Descnp IPrototype Record Increment 0.10 ft
�
� ;Start EL � �6.20 ft � ---�� __._.______ ---------- 'Max EI. � '11.994 ft��
� ;
_�.r.__.___�___� �
I
:Void Ratio j100.00 �
�
�— ;--_--------------------------- ---------,_...____,_.�____.._.___.__
:Condition Existing I.Structure Type �CB-TYPE 1
'Ent Ke ':Groove End w/Headwall(ke=0.20);Channelization iNo Special Shape
�-___ . - �._,_ __.._________._.__ _--_._.___.._._._____.____.___
I
;Catch ;0.00 ft Bottom Area �3 97 sf ���� �
i
_.�� ------ —------------._._.a____ _ :
iMH/CB Type Node
I Record Id:N-2050R
;--_________. _____._ __. -_ ____
------ ----___ _.___�,______. _ -- ,
:Descrip: Prototype Record ,Increment 0.10 ft ;
' I
, �
� ' , _;
__- ____. ,,w__------_._
Start EI. 12.75 ft� Max EL �18.286 ft �
� �
r-----:---__ ----- -----_-- ------ — I I
;Void Ratio;lOo.00
� ��
_.___ _ ---- -_____ __ ---..____ __ n.______.___._..___. _____.______ -- ,
Condition Existing IStructure Type (CB-TYPE 1 �
____.______._______�_ ___---_ __--.,._ ____. - ------------ ---� _----______ i
,Ent Ke Groove End w/Headwall (ke=0.20) Channelization rNo Special Shape �
,
, i �
;
: �
_ _------�--------------____-----___. .___----------- --
Catch �0.00 ft 'Bottom Area 3.97 sf !
' i
MH/CB Type Node
Record Id: V-2200R
�------ �__ ---.__ - -_
Descrip: �Prototype Record Ilncrement j0.10 ft
` �
_______:�__._ ^.^____._ __,__ ___.___ .__�__v---- ;
Start EI. �19.13 ft Max EI. 24.628 ft
--_ ___�_ ______ ----- -`
Void Ratio 100.00 � �
;
_---I-------..-------------------, , ,;
�-----------
Condition �Existing �Structure Type jC6-TYPE 1 i
�
i
------!__ ----- --- -------- --------- _ '
Ent Ke !Groove End w/Headwall(ke=0.20)�Channelization �No Special Shape
, i
Strandcr Phasz?Layout Rcpurt 6
Drainage Calculations
Gutter Analysis
Gutter Flow: Strander East Bound East End
Zd=W idth
I- � 1
d=depth
1
S STA 24+11 to 22+00 Right side of the Roadway
Q= C 1 A pg 2-7 WSDOT Hyd Manual, 2007
C 0.90
Seattle m = 5.62 10-Yr MRI 7.88 50-YR MRI
n = 0.530 10-Yr MRI 0.545 50-YR MRI
Tc 5.00 min
I = m/(Tc)^n 2.39 in/hour
Runoff Coef Adjustment Factor 1.10 10% Safety Factor
Area Width
(pavement) Median 6.00
Travel Lane, 11.00
Travel Lane2 11.00
Shy/Shoulder 2.00
Planter 5.50
Sidewalk 4.00
Total W idth 39.50 feet
Length between CB's 210.00 feet
Area 8295.00 SF
Area 0.1904 A�
Qroad 0.45 cf�
Qbypass 0.00 cf�
Qtotal 0.45 cf;
Depth of Flow
d - IQ*St�137*�SL��0.5\�A(3/8)
/
d=depth of flow at face of curb 0.10 ft 1.26 incheS
Q=the gutter discharge 0.45 cfs less than 1.44 inches??
SL=the longitudinal slope of the gutter 0.0100 ft/ft y@S, OK
St=the superelevation slope 0.020 ft/ft (WSDOT Hyd Manual Fig 5-4.1)
Zd=the top with of the flow prism 524 ft
Check
Max Width allow from face of curb 7.50 OK
Zd=the top with of the flow prism(from above) 5.24
Bypass Flcw
QBP- Q � �l ZC-GW��Zd���813;
Zd=the top width of the flow prism 5.24 ft
GW=width of grate inlet perp to flow 1.67 ft (WSDOT Hyd Manual Fig 5-5.7)
Q=the gutter discharge 0.45 cfs
Q BP=portion of flow outside grate 0.16 Cfs
Gutter Flow: Strander East Bound East End
Zd=W idth
I 1
d=depth
1
S STA 22+00 to 21+08 Right side of the Roadway
Q= C I A pg 2-7 WSDOT Hyd Manual, 2007
C 0.90
Seattle m = 5.62 10-Yr MRI 7.88 50-YR MRI
n = 0.530 10-Yr MRI 0.545 50-YR MRI
Tc 5.00 min
I = m/(Tc)^n 2.39 in/hour
Runoff Coef Adjustment Factor 1.10 10% Safety Factor
Area Width
(pavement)' Median 6.00
Travel Lane, 11.00
Travel Lane2 11.00
Shy/Shoulder 2.00
Planter 0.00
Sidewalk 4.00
Total Width 34.00 feet
Length between CB's 92.00 feet
Area 3128.00 SF
Area 0.0718 Acres
Qroad 0.17 cfs
Qbypass 0.16 cfs
Qtotal 0.33 cfs *No CB's this range
Depth of Flow
d = �Q*St�(37*ISL��0.5��w�3l8)
d=depth of flow at face of curb 0.08 ft 0.98 inCheS
Q=the gutter discharge 0.33 cfs less than 1.44 inches??
SL=the longitudinal slope of the gutter 0.0200 ft/ft yes, OK
St=the superelevation slope 0.020 ftlft
Zd=the top with of the flow prism 4.10 ft
Check
Max Width allow from face of curb 7.50 O�
Zd =the top with of the flow prism(from above) 4.10
Bypass Flow
QBP - Q � � �Zd-GW��Zd��i8;31
Zd=the top width of the flow prism 4.10 ft
GW=width of grate inlet perp to flow 1.67 ft
Q=the gutter discharge 0.17 c�
Q BP=portion of flow outside grate 0.08 c'
Gutter Flow: Strander East Bound East End
Zd=W idth
I 1
d=depth
1
S STA 21+08 to 20+50 Right side of the Roadway
Q = C I A pg 2-7 WSDOT Hyd Manual, 2007
C 0.90
Seattle m = 5.62 10-Yr MRI 7.88 50-YR MRI
n = 0.530 10-Yr MRI 0.545 50-YR MRI
Tc 5.00 min
I = m/(Tc)^n 2.39 in/hour
Runoff Coef Adjustment Factor 1.10 10% Safety Factor
Area Width
(pavement)* Median 6.00
TravelLane, 11.00
TravelLane2 11.00
Shy/Shoulder 2.00
Planter 0.00
Sidewalk 4.00
Total Width 34.00 feet
Length between CB's 58.00 feet
Area 1972.00 SF
Area 0.0453 Acres
Qroad 0.11 cfs
Qbypass 0.33 cfs
Qtotal 0.44 cfs
Depth of Flow
d _ ra'`Sc� 137* �SL��0.51��1318)
l I
d=depth of flow at face of curb 0.08 ft 0.92 incheS
Q=the gutter discharge 0.44 cfs less than 1.44 inches??
SL=the longitudinal slope of the gutter 0.0500 ft/ft yeS, OK ',
St=the superelevation slope 0.020 ft/ft 'I
Zd=the top with of the flow prism 3.84 ft I
Check I
Max Width allow from face of curb 7.50 OK
Zd =the top with of the flow prism(from above) 3.84 �
Bypass Flow �,
QBP- Q � �l Zd-GW������8�3� I
Zd=the top width of the flow prism 3.84 ft
GW=width of grate inlet perp to flow 1.67 ft
Q=the gutter discharge 0.11 cfs
Q BP=portion of flow outside grate 0.10 cfs
Gutter Flow: Strander East Bound East End '
Zd=W idth
I 1 �
d=depth I
1 �
S STA 20+50 to 19+80 Right side of the Roadway
Q= C I A pg 2-7 WSDOT Hyd Manual, 2007
C 0.90
Seattle m = 5.62 10-Yr MRI 7.88 50-YR MRI
n = 0.530 10-Yr MRI 0.545 50-YR MRI
Tc 5.00 min
I = m/(Tc)^n 2.39 in/hour
Runoff Coef Adjustment Factor 1.10 10% Safety Factor
Area Width '�
(pavement)" Median 6.00
Travel Lane, 11.00
Travel Lane2 11.00
Shy/Shoulder 2.00
Planter 0.00
Sidewalk 4.00
Total Width 34.00 feet
Length between CB's 70.00 feet
Area 2380.00 SF
Area 0.0546 Acres
Qroad 0.13 cfs
Qbypass 0.10 cfs
Qtotal 0.23 cfs 'No CB's this range
Depth of Flow --
d = LQ*St�\37*�SLI�0.5���(318)
d =depth of flow at face of curb 0.06 ft 0.72 inCheS
Q=the gutter discharge 0.23 cfs less than 1.44 inches??
SL=the longitudinal slope of the gutter 0.0500 ft/ft yes, OK
St=the superelevation slope 0.020 ft/ft
Zd=the top with of the flow prism 2.99 ft
Check
Max Width allow from face of curb 7.50 OK
Zd=the top with of the flow prism (from above) 2.99
Bypass Flow
QBP - Q « � � Zd-GW�I Zd���$'31
Zd=the top width of the flow prism 2.99 ft
GW=width of grate inlet perp to flow 1.67 ft
Q=the gutter discharge 0.13 cfs
Q sP=portion of flow outside grate 0.03 cfs
Gutter Flow: Strander East Bound East End
Zd=W idth
I 1
d=depth
1
S STA 19+80 to 19+00 Right side of the Roadway
Q= C I A pg 2-7 WSDOT Hyd Manual, 2007
C 0.90
Seattle m = 5.62 10-Yr MRI 7.88 50-YR MRI
n = 0.530 10-Yr MRI 0.545 50-YR MRI
Tc 5.00 min
I = m/(Tc)^n 2.39 in/ hour
Runoff Coef Adjustment Factor 1.10 10% Safety Factor
Area Width
(pavement)* Median 6.00
Travel Lane� 11.00
Travel Lane2 11.00
Shy/Shoulder 2.00
Planter 0.00
Sidewalk 4.00
Total Width 34.00 feet
Length between CB's 80.00 feet
Area 2720.00 SF
Area 0.0624 Acres
Qroad 0.15 cfs
Qbypass 0.23 cfs
Qtotal 0.37 cfs
Depth of Flow
d = rQ*St!\37*1`SL`w0.5`���318)
L I 1
d =depth of flow at face of curb 0.09 ft 1.03 inCheS
Q=the gutter discharge 0.37 cfs less than 1.44 inches??
SL=the longitudinal slope of the gutter 0.020 ft/ft yes, OK
St=the superelevation slope 0.020 ft/ft
Zd=the top with of the flow prism 4.28 ft
Check
Max Width allow from face of curb 7.50 OK
Zd =the top with of the flow prism(from above) 4.28
Bypass Flow
QBP- Q � � � Zd-GW�I Zd���$!3)
Z�=the top width of the flow prism 4.28 ft
GW=width of grate inlet perp to flow 1.67 ft
Q=the gutter discharge 0.15 cfs
Q BP=portion of flow outside grate 0.10 Cfs
Gutter Flow: Strander East Bound East End
Zd=W idth
1= = 1
d=depth
1
S STA 19+00 to 17+50 Right side of the Roadway
Q= C I A pg 2-7 WSDOT Hyd Manual, 2007
C 0.90
Seattle m = 5.62 10-Yr MRI 7.88 50-YR MRI
n = 0.530 10-Yr MRI 0.545 50-YR MRI
Tc 5.00 min
I = m/(Tc)"n 2.39 in/ hour
Runoff Coef Adjustment Factor 1.10 10% Safety Factor
Area Width
(pavement)'` Median 6.00
Travel Lane� 11.00
Travel Lane2 11.00
Shy/Shoulder 2.00
Planter 0.00
Sidewalk 4.00
Total W idth 34.00 feet
Length between CB's 150.00 feet
Area 5100.00 SF
Area 0.1171 Acres
Qroad 028 cfs
Qbypass 0.10 cfs
Qtotal 0.38 cfs
Depth of Flow
d = �Q*St f�37' �SL��0.5`�nI318)
/
d=depth of flow at face of curb 0.11 ft 1.34 inChes
Q=the gutter discharge 0.38 cfs less than 1.44 inches??
SL=the longitudinal slope of the gutter 0.0050 ft/ft yes, OK
St=the superelevation slope 0.020 ft/ft I
Zd =the top with of the flow prism 5.58 ft
Check
Max Width allow from face of curb 7.50 OK 'I
Zd=the top with of the flow prism (from above) 5.58 �i
Bypass Flow �
QBP- Q � � �Zd-GW��Zd���$'31
Z�=the top width of the flow prism 5.58 ft
GW=width of grate inlet perp to flow 1.67 ft
Q=the gutter discharge 0.28 cfs
Q eP=portion of flow outside grate 0.15 cfs
Westbound - SAG INLET DESIGN WORKSHEET
Vaned grate at low point
�� E 0 �2
�— �1 —� �— �2
Q
_ Q� Inlet A Inlet 8 inlet C B� _�
dA dB d�
r
�
� c � c c c
0 0 � o $ o 0
o + ,�, �.
0 0 � + � v o
+ +
h � � � �
Transverse Slope S, OA20 ftrf� Shy,�Shoulder 2A0 ft
Allowable Z, 7.50 ft Lane Width 11 00 ft
Allowable de 0.�5 ft (d„=d�= 0.075 ft allowable)
Time of Concenhation T., 5.0 min{conservative) 0.9"
�Face of Curb
50 yr.rainfall m 7.88 Seattle ,� - . ..
ccefficients [ n o.545
Rairdall Intensi I --»''��
ty sc... 3278 inlhr (for 5 minute duratlon) �:::� .
`��~»� Length
Distance between last inlet L� 167 AO ft Lz 150.00 ft : I'`'
W idth of catchment area W, 45A0 ft W z 26.00 ft �'*�{
Bypass from last inlet oB�,° - cfs QE,,z' �11 ds j j-,�:�di i�.��
Discharge of catchment area Q� 0.54 ds Q_ 028 ds ��
QTdal � "�9Pt+Qt+QBF�+Q�
Q,�„i = 0.00+0.54+0.11+028 = 0.93 cfs
Combination',Vaned Grete',or
Grete Inlet for sag PB(C!V!G) 1 c
See Figure 5-5.6 ir
C P,, ,N` 000 fl Wiath� Length� Hydraulics�danual
Effedive Perimeter of pe 5.34 ft Width 1.67 Length 2 00 for grate dir-iersions
Grate Inlets(reduced fo
plugging) � P� 090 ft Witl'.h Length
Combination=�00°ro
Vaned Grate=75%
Grete Inlet =50%
TQ — QA+Q6+Q�
2 EQ =Cy�qPq�O.SdB��'+C�•�BPBde�5+ CN;,-P-10 Sdbl � 0.93 cfs Capacity is adequate,
design is complete.
F.Q 1��'
de -� G P 0.3536+C� P +C. +�., P�0.3536 J �.15 ft Check calculated d�against
� nn a .�e e �us vt allowable d8
1.79••
If dE<allowable dB,Ihe design is wmplete Design Gn r.�
If dE>allo�roable d�.additioral inlets must be acded�ano,he process repeated
Notes:
' If using a combinalion inlet for the s2g.7he flank grale inle-s are not requiree except in z tlepressed area{See Hyda�lics�.farual;�
2 Formulas based on weir ilow. See Hydraulic h7anual 5-5 2.
' To add more than one inlet in the sag or flanks just increase the width and length values to the sum of all values.
Inlets can be different sizes. See Figure 5-1 D in Hydraulics Manual for grate dimensions.
� `Qpp� and Qe�z come from the inlet spreadsheet.
5 Vanec grate cap2ci!4 based or guiaelires presented in Tzcoma S�.h'P,7 hlanual Vol.III pg 4-70 Inlet Grate Capacity fer'v'zred Crate,
G��FeuF�a`A'z,.20�;y FAP'JJT-C9-�TS.ENGR'.Cr�i�D�a�n3ae�Gu�ter a�arysis_N_1•.Is
' P��s=[CaJ '�'S'�i'11
Drainage Calculations
Miscellaneous Calculations
Project ��� Sheet of
JobNumber �AptilT-ay"ddy
�� 1 >c'I�t'l'I�I11V1 Subject STa� rU�J� SQI LI.WAH Designer � L E!°1/el Cs�
�L�.S Date ���/�� _
FIGURE 5.3.I.E WEIR SECTIOn FOR EMERGENCY OVERFLOW SPILLWAY
_ emergency overflow ,W - -. overflow
li� - X water surface �-��� .5'min. water
.T min. g �$ - - surface
� , � � �;�` .2'min. H
�'��c����+:'��£+�£��.,.� =
rock tining
• L - per Table 4.4.1.A
� (),, �2
Q/00 C C"..'l� [�3 L{}3h+ 8�5 �t8r�F��E} 5/�]
�,,,,�.���:�
�7•w�+4 L
Q��, = /ao YIt- 1'EAK FG��I ---� = C r�Q - ��.9��3,f9��� r', r, e : ;) 1 --� � � ' "
..-.
TR : f R l��Z/ ' Pi[. `�t�rt.) be ;
=�3.9 ,nx2.{,1��.3�-0.�3 j
= l3•q��0 4��5��
= 3.t°1 inlhr�
Qloo � �3.3b92q HtatE - liJ 1 h� \ y356o Fr2�/ 1 Fr �
_.-� s x r— �----- --�—
hr 360o s J C I AcaeC � �Z' },�
_ /3•y8 � cF5
C = naulna.c� CoEcf�c���+t z �.b
C� c C'ILA�Ity � 3'Z.Z. FT/SLCZ'
� = �ac�ra � we�t (Fr)
� = I�tit�{T oc W4'fER� `FT� = �•6�
Q = a�c.,uE oF s,oE sw�E,�a��=3 c�- 3�1 s�pEs►.�Es
Q _ 3 .2l C 1,N3�z � 2�� �-�S/:l
loo ' J
�
L. = C,Qtoo J(3•2� �;'z�] � 2 4N
L _ 13•�I�3.2txo,r��31i — 2.y ��.5�
�
- 10• b'l� _� vsE Il�
�
�j j;` ,``_t�M Project: Strender Boulevard Glcs By: Schurman Project 11: FAPVYT-09-175
' Subject: Wetland QR-Hydroperiod Threslwlds Checked By: Date: OS lanuary 2011
Date:
O:�Fm;rdWa']:J��FP.P:.?091'�F1Mli�C'�.�'Dr' �.MG5=1wd�J+Nbn�OPM r �mC�'etpnC OR Md IOG MM� �s
Destription
The Strander Boulevard project proposes to construd a grede separation below the BNSF and UPRR trecks. Stormwater will be
collected and conveyed to a stormwater facility located between the BNSF and UPRR tracks. The stormwater will be discharged from
the stormwater facility into Wetland QR. Per DOE,wetland need to be analyzed is stormwater is discharged into them to determine
if the wetland will continue to fundion properly.
The Wetland Technical Memo,dated November 2007,states that Wetland QR is a 25-acre wetland located between the BNSF and
UPRR tracks. The wetland is approximately 0.8 miles long and is classified as a Category I/II wetland per DOE ratings.
Design Source
+pepartment of Ecology Stormwater Management Manual for Western Washington(2005)
� -Guidesheet 2B
Threshold Requirements
The following are the thresholds that need to be met so that the wetland will continue to function properly even though additional
water is being added/removed from the wetland.
1. Mean Annual Water Level Fluctuations(WLF)»>does not exceed 20 cm(7.9 in�
2. Frequency of Stage Excursions of 15 cm above/bebw pre-development stage»>does not ezceed an annual average of six
3. Duration of Stage Excursion of 15 cm above/below pre-developed stage»>dces not exceed 72 hours per excursion
4. Total Dry Period»>dces not increase or decrease by more than two weeks in any year
5.Akernations to watershed and wetland hydrology[hat may cause perennial wetlands[o become vernal are avoided
6. Magnitude of Stage Excursions above/below the predevelopment stage»>should not exceed B cm for more than 24 hours in any 30-day period
�� I�cr�,t,7A�M Project: Strander Boulevard Calcs By: Schurman Date: OS January 2011 Project#: fAPW7-09-175 �
� Subject: Wetland QR-Hydroperiod Analysis Checked By: Date:
O�\FederelWeN2009\FAPWT-09-175\ENGR\CIvil�Dralnape\MGSFlootl\Wetlantl QR HverooRnomlWanand qR HMromriod AnxlvRin.xlsxl
r��a � a e
; I
Rating Table Development
4
The rating table for Wetland QR was developed using existing contour �� ; .___.
information in AutoCAD. The area of the wetland boundary was determined � `______ �,
and an elevation of 23.0 was used for the wetland boundary, An assumption
�,.
of 2H:1V sideslopes were used to offset the boundary and to generate a wetland ----f,,�
volume. The area of Wetland QR calculated using AutoCAD is 13.01 acres which � � � �
is 48-percent smaller than the size mentioned in the Wetland Technical ' t -
� ;
Memorandum developed by David Evans Associates dated November 2007. ��._''._.___._._ ? � "` * � '����
Therefore,the rating table below is conservative because water levels and would , � 1 ,11�''�..�`
be more likely to fluctuate in a smaller wetland. Additional assumptions made *��� 1 � ��,i��
was a wetland depth of two-feet and an additional foot above the wetland boundary � '' ,* �'
C'--'--'�-- �, �r
for water level fluctuation. �+ ' _�,,n 1
�------ '���
Volumes for the rating table were calculated using the Prismodal formula as
shown in Figure 3.52. This figure is from the ASCE manual Sedimentation
Engineering. ';
,...........
�.
� l------- _.:�
Discharge was assumed to be very low which would be conservative causing � -'�,�,'
� . .���
higher fluctuations in water levels. �� �.' ��,�
. .
.y,
�� - �:'f- ,
{...'� ____ _ ,-,
A
Va� IA+�E+Bt
WetlandQRRatingTable F7�R�.S2 Tcmudm�dilbdpiismnidalhxmul�ftK3eternuma�cy+rityafrcxervmr.
MGSFIood Rating Table
Area ID Elevation Surtace Area Volume Cumulative Volume ---- ------------- -------------- -
Elevation Area Volume Discharge
.T._ _..__.. ._._-- i -- — -----___ ....... _..
- (Jeet) (square%et) (acres) (cublc jeet) ' (acre Jeet) (cublc jeet) (acre jeetJ (feetJ (acres) (acre•feet) (cjsJ
_ .. _ __
1 2 3 4 5 6 S 6 7 8 9 10
AO 20.0 0 ' 0.00 0 0.00 0 0.00 20.0 0.000 0.000 0.000
---- -- - ___ _—._.._ ---.__. ___— ------ ----
A1 21.0 526,412 12.08 175,471 4.03 175,471 4.03 21.0 12 085 4.028 0.100
A2 22.0 552,743 12.69 539,524 12.39 714,995 16.41 22.0 12.689 16.414 0.200
A3 23.0 566,729 13.01 559,721 12.85 1,274,716 29.26 23.0 13.010 29.263 0.300
-- _ __ ...
A4 24.0 580,756 13.33 573,728 13.17 1,848,444 i 42.43 24.0 13.332 42.434 0.400
Project: Strander Boulevard Cala By: Schurman Projet[0: FAPWT-09-175
`�i i�;,,.'�t1Bt�M
Subjed: WMland QR-Hydroperiod Analysis CF�ecked By: Date: 06 January 2011
Date:
- Ia�2004:APNT-_.��S�ENGRC,wi�Lra J.•:;SF4ic�l':.l�..arv]��2?.Yu�>�oi�.�':N4vic�R H
Predeveloped Wetland Location:Link 1:Wetland QR
Postdeveloped Wetland Location:Link 1:Wetland aR
"""""'Mean Water Level Fluctuation Results(ft)"'••"•»•••
Month Predeveloped Postdeveloped Mean Annual WLF Check
"ct D.C=�D _.___' Pass
[Ic: O.CG14 _.OG1� pass
:ec O.G027 U.0014 Pass
.-a� 0.0033 0.0012 Pass
Feb 0.0036 0.0010 Pass
I�lar 0.0032 0.0008 Pass
7,Fr 0.0022 0.0007 Pass
'�1a}' 0.0009 0.0007 Pass
��ln 0.0003 0.0007 Pass
���1 0.0001 0.0006 Pass
A�g 0.0000 0.0005 Pass
Sep o.r.nn� n.nppg Pass
.,nn��al O.f,023 0.__�� Pass
Check Predevelopment Mean Annual WLF
�_�_ thar. i5 en 10.992 Etl -_es >» Ho effect te �. aetaticn species rictness
2_.:�:ter c=ar =5 cn 10.952 f[1 .:� »> Chect the nean ar.nnal (ar.9 mean morth=:i WLF fer 2C cm or rt,cre _ncrea=e
Mean Annual(and Mean Monthly)WLF
-_�i-� pcst3eveloped meaa i:LF co�=_ not :ncrca== ❑�_e ttan 2J _m :0.55E ftj :n an:i ;�or.th cr for th.e anrual
�. .__ _. .- a r.=_='. ftr, .�t-.- _�.r._ fl,.�t-.:.ri���n ..__1 r.a,•:-: co �f'��•. to ' .�. _>t:zci-��r sf�._c.. ri^h�e__
�..t 'L. ...c._n_._.
Projett: Strander Boulevard Calcs By: Scburman Projed#: FAPWT-09-175
��iC�i,'�:�
Subjett: Wetland QR-Hydroperiod Analysis Checked By: Date: 06 January 2011
Date:
yO�raMy�'-G�'MN'.)9.�'S.ENGRu'A�C�arage.MG5F4.T.hetr " - _
F M^� :.'��a�e�
"""""'S1age Excursion Results "'-""-"^
Slage Excursions Threshold(RJ:O.SGO
Avg Number of Stage 6ccursions Per Vear:0.006
VYY No.Excursions Max(ft) Max Dur�hrs) Avg Uuretion(hrs)
=a40 1 15.'ce°. =E2 1P2
:3d1 ., J �.- _
=34. 7
1943 C � G
1944 C 0 0
1995 0 0 0
199E 0 0 0
1597 0 C 0
1998 0 0 0
1599 0 C 0
1950 0 Q D
1951 0 0 0
1952 0 0 0
1953 D 0 0
1954 0 0 0
1955 0 0 0
1956 0 0 0
1957 0 0 0
1958 0 0 0
1959 D 0 0
1960 0 0 0
1961 0 0 0
1962 0 0 0
1963 0 0 0
1964 0 0 0
1965 0 J 0
196E 0 0 0
19E7 0 0 0
19E8 Q 0 0
19E9 0 0 0
1970 0 0 0
1971 0 Q 0
1972 0 C 0
1973 0 Q 0
1974 0 G D
1975 0 0 D
1976 0 0 D
1977 D 0 0
1979 0 0 �
1979 0 0 0
1980 0 0 0
1981 0 0 0
1982 0 0 0
1983 0 0 0
1989 0 D 0
19B5 0 D 0
15BE 0 D C
1987 0 D G
1588 0 0 0
1589 0 0 0
1990 0 0 0
1991 0 0 0 G
1992 0 0 0 0
1993 0 0 0 0
1994 0 0 0 0
1995 0 0 0 0
1996 0 0 0 0
1997 0 G D 0
1996 0 0 0 0
1999 0 0 D 0
2000 0 0 D 0
2DD1 D 0 0 0
zaaz o 0 o a
2003 0 0 0 0
2004 0 0 0 0
2005 O O O O
200E 0 0 0 0
2007 0 0 0 0
2008 0 D 0 0
2009 G J 0 0
2010 0 D 0 0
2011 0 D 0 0
Projec[: Strander Boulevard Cala By: Schurman Projec[N: FAPWT-09-175
�IX C:;l'�ABAM
Subject: Wetland QR-Hydroperiod Analysis Checked By: Date: 06 January 2011
Date:
p���=ede�M'.Y�DC"'+'4PN'.�]3-t�S�ENG3'Ci.fCraruoeJAGSFboSWEhar]OF.MNoperN�Wc9ari OR FYcnp��i2 Aral�se.kv��
�'YntUlJn:'�Ta�.-a - _ _- — ——__-
""""""Stage Extursion Results "'•»"•»:,
Stage Excursions Threshold(ftj:D.500
Avg Number of Stage Excursions Per Year:0.006
WY No.Excursions Max(R) Mau Dur(hrs) Avg Duration(hrs)
201z � � c n
2013 J C 0
2015 7 J C n
2015 0 � 0 0
2016 0 0 G 0
201? 0 0 0 0
zoie o 0 0 0
zois o 0 0 0
zoze e o 0 0
' zozi o 0 0 0
zoaz c o 0 0
2023 0 0 0 0
2029 0 0 0 0
2025 0 � 0 0
2026 0 C 0 0
2G27 0 C 0 0
2028 0 0 0 0
2Q29 0 0 0 0
ze3o o e o 0
2031 0 G 0 0
2032 0 0 0 0
2Q33 0 0 0 0
20°-9 0 G 0 0
2035 0 0 D 0
2036 0 0 D 0
203' 0 0 D 0
2038 0 0 D 0
�039 0 0 0 �
2040 0 0 0 �
=041 0 0 0 �
zo�z o 0 o a
=043 D 0 0 C
:045 D 0 0 C
?J45 0 0 0 C
z�ae o o a c
z�a� o 0 o c
2�48 0 0 0 0
��45 0 D 0 C'
2JSC 0 D 0 G
2J51 0 0 0 G
2J52 0 0 0 0
�'�53 0 D 0 0
_059 0 0 0 G
_„_, C 0 0 =
�CSE 0 0 0 r
�CS? 0 0 0 =
ac=_s o 0 0
zr.=_s o 0 0 =
acEo 0 0 0 �
zr,E-_ o 0 0 =
zcez o a o 0
�fE3 0 C 0
2n64 0 C 0
2pE5 0 Q 0
2C�E6 0 6 0 5
2067 0 0 0
�OES 0 0 D
2i c9 0 0 0
�070 0 0 0
�C�71 0 0 0 ..
_ii72 0 0 0
_ii73 0 6 D
_274 0 0 D
_075 0 0 D
2070 0 0 D �
2l^7 0 0 D
_]^9 D 0 D
.IO^9 0 0 0
=030 D 0 D
_731 0 0 0
, ADA7,� Projed: Strander Boulevard Cala By: Sthurman Projett#: FAPWT-09-175
,���C i-`C(All[]tvl
Subject: Wetland QR-Hydroperiod Malysis Checked By: Date: 06 January 2011
Date:
C:'=cdvaWa 1009'FhPVrT_��1]S�ENGR,C+�I�Drain �M1'�GSFbuC.Y`:HIaNORYr� W'::9aM OR MAc�a�v MaFSis.tlsi
"""'«»Stage Excursion Results """"""'
Stage Excursions Threshold(ft):0.500
Avg Number oi Stage 6ccursions Per Year:O.DO6
WY No.Excursions Mau(ft) Max Dur(hrs) Avg Duration(hrs)
2093 C C - ]
��_� C C - 0
�CBE n C � 0
2CE7 O C � 0
2CE8 G C� D 0
�CE9 0 0 D 0
zo�o o e o 0
�r,al o e o 0
�asz o 0 0 0
2ii93 0 0 0 0
_ii94 0 0 0 0
�pa5 p 0 0 0
�p95 D 0 0 0
�09' J 0 0 C
Check Frequency of Average Annual Excursions
Tl:e average aanual excirscon= o' O.np� is beiow the six annual excursions allowed.
Check Duration of Average Annual Excursions
Tk:e loncest dnration of the excurscon H�as 182 hours which is higY_ez tran tre allowed 72 tours. Hewever, thi=
c�ration is the only d�.�ration for the 158 year period and it occnrxeri durinq the first year. Therefore, it is
�_.=_r_.=_ _hat t':is �s ar. anoTaly and dces ❑ec. rep=esent t��^ act�ial •:retland hydroperio� �_raracteristics. _�,s a
_�s��lt, c!:- a_� �� o�,-.,r c�= rta' e _ _ _'F .:.� tosr t1-r,�=t_o_d.
���;`,_`l��M Project: Stronder Boulevard Calcs By: Schurman Project#: PAPWT-09-175
Subject: Wetland QR•Hydroperiod Analysis Checked By: Date: 06 January 2011
Date:
O•cM+al'.4a'+2009`=tPrVT.]3��t.ENGfYCiAiL.areoFM�.:;:cMc.].a,xl.Ttl7RHrQc cU.V:e1L�nc CR 1- r. .x%.nal�'-vsx
"""""'No Water(Dry)Excursion Results """"'•"'
Wetland Dry when Stage Drops Below(ft):0.01D
Dry Excursion Duration(hrs)
WY Predeveloped Postdeveloped Difference
19ac e�aa e-�a o
1941 E?6J b'S7 0
1942 6i6J 675J 0
1553 E76D 8^oJ 0
1549 8784 8'84 0
1945 8760 8750 0
1996 8760 8750 0
1597 8760 6'60 0
1998 8789 8'B9 0
1999 8760 9'6C 0
1950 8760 8'6C 0
1951 8760 9'EC 0
1952 8789 8789 0
1953 8760 87E0 0
� 1954 8760 87E0 0
1955 8760 87E0 0
1956 8789 87E9 0
1957 8760 87E0 0
1956 8760 8?EO 0
1959 87E0 87E0 0
' 1960 8789 Bib9 D
1961 8760 8760 0
1962 8760 2760 0
1963 8760 E760 0
1969 8784 5789 0
1965 8760 67b0 0
15EE 8760 876J 0
15fi7 8760 876] 0
1968 8784 8784 0
19E9 8760 8^00 0
1970 8760 8700 0
1971 8760 8700 0
1972 8789 8734 G
� 1973 8760 875C 0
1974 8760 87'00 0
� 1975 8760 976C 0
1976 8789 8789 J
1977 87E0 9'.EC J
1978 87E0 8760 ,
1979 87E0 87E0 :i
1960 8769 8789 ..
1961 8760 87E0 „
1962 8760 87E0 ,�
1983 B760 87E0 ,�
1984 8784 8789 ,
1985 8760 B?60 ��
19BE 8760 2i60 �,
� 1987 8760 8760 ',
1988 A784 Q784 �
1°B9 8760 8760 ��
1990 8760 876J �.
1991 8760 876� �
1°92 8784 8784
1993 8760 8'6B
1994 8760 8750
1995 8760 8760
1996 8784 8784
1997 8760 8750
1998 876Q 8'S0
1999 8760 8760
2000 8789 6'94
2001 8760 876C
2002 87E0 976C
2003 8760 876C
2004 87Q9 9789
2005 87E0 9'EO
2006 8760 87E0 0
2007 B7E0 876G 0
2008 8784 8789 0
2005 8?60 876G 0
2010 8760 87EG 0
20ll B?60 8?EO 0
�,��` ,`,`.�M Projec[: Strander Boulevard Calcs By: Schurman Project 8: FAPWT-09-175
Subject: Wetiand QR-Hydroperiod Analysis Checked By: Date: 06 January 2011
Date:
o��ra.va,zoos�=nc-,�'n3„s.��vcm:.an-a.�rnc=_=wrnP.�oFHwxH�+..�.«:�,�:�. -
��,��i����a
"""""'No Water(Dry)Excursion Results """'••'•"
Wetland Dry when Stage Drops Below(f1J:D.010
Dry Excursion Duration(hrs)
VYY Predeveloped Postdeveloped Difference
zoiz e�sa e-sa o
z�i3 e�Eo e-�o 0
2J74 e?eo e�n� o
2D15 Bi60 £7oJ 0
2016 8784 6784 0
2017 8760 5760 0
2018 8760 8760 0
2019 8760 8750 0
2020 8784 8794 0
2021 8760 8^60 0
2022 8760 8750 0
2023 8760 876C 0
2024 8789 8784 0
� 2025 8760 d76C 0
2026 8760 876C• 0
2027 8760 87EQ 0
2028 8789 9,'B9 0
2029 8760 8.'EC� C
2030 8760 87EG C
� 2031 B7E0 8760 C
2032 0784 8769 C
� 2033 8760 87E0 C
2039 8760 8760 C
2035 8760 8760 0
203E 8784 87&4 0
2037 8760 2760 0
2038 A760 8760 G
2039 876D &76J 0
2090 8784 5784 .
2091 8760 &76D �_
2092 8760 876D C
2093 8760 8^'0� "
2099 8784 8784 .
2095 876C 87'v0 .
2096 8760 8750 .�
2097 8760 8'60 .
2048 8789 8789 _
2049 8760 876C ��
2050 87E0 87E0 "
2051 87E0 87E0 "
2052 8789 6789
2053 8760 B?EO
2059 8760 87EG �
2055 8760 8?EG
205fi 8784 8?59
2057 8760 8?60
2058 8760 8?60
2059 E760 !?60
2060 8784 E789
2061 8760 8760
20fi2 8760 E760 �_
2063 8760 b76J 0
2069 8784 b784 0
2065 8760 8760 0
2066 876� 8760 0
2067 8760 8750 0
2068 8789 8^84 0
2069 876C 8700 0
2070 8760 8750 0
2071 8760 8750 0
2072 8789 8789 0
2073 8760 876C 0
2074 8760 876C 0
2075 B7E0 6?EC 0
2076 8784 6789 0
2077 0760 67E0 0
2078 8760 67E6 0
2079 8760 B?EO 0
2DB0 8789 8789 0
2081 8760 87E0 0
2082 8760 8760 0
2003 8760 8760 0
Projed: Strander Boulevard Calcs By: Schurman Project tt: FAPWT-09-ll5
� i i�t��t A�AM
Subjec[: Wetland QR•Hydroperiod Analysis Chedced By: Date: 06 January 2011
Date:
O-'.FinaJWa�^r 19. :TC�-"SEAGRCn+�Panaanl.'GSFboe��::elav]�3M:vKerc..1:.���- :� -
��� ��� a
"""""'No Water(Dry)Excursion Results """"""'
Wetland Dry when Stage Drops Below(fl�:0.016
Dry Excursion Duration(hrs)
VYY Predeveloped Postdeveloped Difference
�08� 9?E9 A'Ed 0
2085 _?E�; _?e�� 0
2D85 P,Ep g7E�� p
2087 97E0 9?EG p
� e088 9709 8?84 0
2089 87E0 8?EG 0
2090 87E0 876G 0
2091 8760 B?EL 0
� 2092 8789 6784 0
2093 87E0 87EC 0
2094 8760 876C u
2G95 8760 876C 0
20�c 6'94 B'84 0
2C5% 6760 8750 0
Check Dry Period Difference
Ttes�_ is �c char_ae in tho drr pezicd `�--�-n '.`� �.� : - � � ' - : �- �, � - �. . � �� � •
i
���:,�_ �,- �;A�M Projed: Strander Boulevard Calu By: Schurman Praject M: FAPW7-D9-175
Subjed: WMland QR•Hydroperiod Analysis Checked By: Date: 06 January 2011
Date:
p�FepeaNY '���]S�FqR'fliw.'.`S,ENGR�LmlRair�a.�VGS�uod�:'Jellai]ORN ala'M OF Mdre•enoJ r+na� isMv
e0
"""'•"•Amphibian Season Analysis`•»•»•••«•
Season Begins:02/01
Season Ends :05131
Amphibian Stage Excursions Threshold{fl):0250
WY Max Excursion(k) Max 30-Day Excursion(hrs)
l�qr l �
1�9= � ?
1c.]� f f
:�93 0 C
=344 0 0
=345 0 0
:746 0 0
7557 0 7
1�48 0 7
1599 0 7
i°50 0 0
=551 0 C
=352 0 C
�353 0 0
1759 0 0
1�55 0 0
iS=6 0 0
1557 0 �
1�58 0 J
=959 0 D
_37o e
=3�i o
�3sz o
1:53 0
15E9 0
1�E5 D
1466 0
_�67 0
=358 0
=309 0 0 I
1970 0 0
1571 0 0
15?2 0 0
1573 0
1�74 0
i?�irJ �
.a-;6 e
:3'7 0
19',B 0 0
1979 0 0
isee o c
i=ei a c
issz o 0
:483 0 0
:984 0 0
=365 0 D
:3�6 G 0
1597 0 0
1588 0 0
1589 0 0
1590 D 0
iG91 0 0
:992 0 G
=993 0 U
=334 0 �
i395 0 7
1596 0 0
1557 0 0
1�58 0 0
1599 0 0
=n00 0 C
2D01 0 0
�ooz o 0
_7J3 0 0
2�04 0 J
2005 0 J
2C06 0 �
zce� o 0
= og �
�j l�<'t`�c;�M Project: StranderBoukvard GIuBy: Schurman Projed#: FAPWT-09-175
Subject: WeUand QR-Hydroperiod Analysis Checked By: Date: 06 January 2011
Date:
0�=6frfa'Wa 1Q19`G0.PWT.,3�.%S.EN::?C�.iL�a - c�NNOFHr�Y �W'�':dbc CR YM�
"""•"»Amphibian Season Analysis•""""""
Season Begins:02/01
Season Ends :05131
Amphibian Stage Excursions Threshold(ft):0250
WY Max Excunion(ft) Maz 30-Day Excursion(hrs)
zoio 0
2ell C
20i2 :
2013 G C
2014 0 C
<O15 0 0
2016 0 0
2�17 0 0
2018 0 0
2019 0 0
2020 0 0
2C21 0 0
zezz o 0
zez3 0 0
ze2a a o
zozs o 0
:oze o 0
<oz� o 0
�oze o c
2J29 0 C
2J30 0 C
"<J31 0 �:
203Z 0
ZC33 0
�C39 D
�f35 0
_n�6 0 �
_n37 p
d036 0 I
_039 0 I
-040 0 I
�7A1 0 �I
�742 0
�J43 0
�J49 0
���5 0
2C4E 0 �= �
2C47 0 _
�caa o _
�099 0 n
2G50 0 _
_��51 0 _
:G52 0 =
_053 0
��54 0 !
:J55 0
='J56 0
2�57 0 �
�058 0
:..�_ 0
�f,EO 0
2CE1 D
�OE2 D I
�063 D
]i064 0
_065 0
_066 0
�067 0
�068 0
S7'o9 0
�7'0 0
: 1'1 0
2072 0
2�73 0
2C79 0
2C75 0
2076 D
20;7 0
�,��`�`,l,��M Projec[: Strander Boukvard Caks By: Schurman Projed#: FAPWT-09-175
- Subject: Wetland QR-Hydroperiod Malysis Checked By: Date: 06 January 2011
Date:
OF aIK 1}JgF,1PN'TC�--,-iEMGRi_�w�dara�r���C5�4xc�4':.iatl]RYY}eqe�c]'�l':e11adOR1Atr:�nc.f4d'.ssAssl I
�����II
"""""'Amphibian Season Analysis""""""'
Season Begins:02l01 �
Season Ends :OSl31 �
Amphi6ian Stage Excursioru TMeshold(f1):0.250
4VY Max Excursion(ft) Max 30-Day Excursion(hrs) '
�oac �
zcei o
2062 C
2G83 C
2084 0
2085 0
2J36 0
2�97 0
2088 0
2C89 0
2090 0
2091 0
_092 0
i093 0
2794 0 r
2095 0 r
209fi 0 C
2C5? 0
Check Magnitude of Excursion for 30-0ay Period
-1: _ o--.__- �c ,zrc�i icr.= __ .�r� ___�._ . _r. �".�'_ fr c_ coi<_ rtan �d � ___ '� - __ : F"c3oo.
Hydraulic Report
Strander Boulevard Extension Project
Cities of Renton and Tukwila, Washington
Appendix D - Renton's Standard Plans
Catch Basin Type 2
Combination Inlet
Bidirectional Gate
Q
Y
N ���
a / /��5`(ryp)see note 1
�
�'DIAMETER SMOOTH 4 hook clamps evenly
z BARS EQUALLY SPACED placed see cetail below
� ia•o.c.ti��vc.y �I I
o il ,
A t � � p Provide maintenance access
by welding 4 crossbars l0 4
vertical bars as shown.
�� I Hinge upper ends with flangesl
/ � � bol[s and provide locking
� I �� mechanism(padlock)on
lower end.
jLocale steps directly below.
PLAN V�EW \�
�
�,'�� NTS \��
Iaa'DIA.SMOOTH ROUND&QRS
LOWER STEEL BAND a"x 4"WIDE WELDED E�UALLY SPACE�.
FORMED TO FIT ON GROVE BARS SHALL BE WELDED TO
OF C.B.RISER UPPER 8 LOWER BANDS
(24 BANDS EVENLV SPACED SEE
NOTE�1
24" I
�� JUPPERSTEEL—. SEE
BAND a�a"X 4' NCTE 1
'JVIDE
I;�AC�� i��
'���� I li�;',,�\\
; j 'III ��li;; /ji
//' 11
rvPE 2 ce—
STANDARD GALVANIZED
� STEPS OR LADDER
45°
SMOOTH�
VERTICAL BARS
,—C.B.RISER SECT�ON A—A i
NT8
HOOKCLAMP �I
CNCHORED . �. ��..
TO C.B.RISER '�
OETA�L HOOK CLAMP
NTS
NOTES:
t. Dimensions are for illustration on 54'diameter CB. For different diameter CB's adjust to maintain 45°angle on
"vertical"bars and 7"o.c.maximum spacing of bars around lower steel band.
2.Metal parts must be corrosion resistant;steel bars must be galvanized.The use of steel is prefer.
3.This debris barrier is also recommended for use on the inlet to roadway cross-culverts with high potential for debris
collection(except on type 2 streams)
4.This debris barrier is for use outside of road right-of-way only. For debris cages within road right-of-way
Y
��� �.t, STD. PLAN - 234.20
• PUBLIC V�ORKS OVERFLOW STRUCTURE
+ � DEPARTMENT
�'� $ �4:�RCH 2O08
�'�,TO
-
NOTES
� ��t:
PIPE ALLOWANCES
Y �i�r� � �. � _, 1. As acceptable altematives to the rebar shown in the PRECA3T BASE
� �� >f '� � �T � � ��'� MAXIMUM SECTION,fibers(placed according to the Standard Spedflcations),or
m \� ? 7-: / PIPE MATERIAL INSIDE wire mesh havin g a minimum area of 0.12 s quare inches per foot shall
�./-:/ %" DIAMETER be used with the minimum required rebar shown in the ALTERNATIVE
� " � PRECA3T BASE SECTION. Wire mesh shall not be placed in the
o �'"I�� / PIAIN CONCRE E �Z" knockouts.
FRAME AND VANED GRATE 2. The knockout diameter shall not be greater than 20". Knockouts shall
ALL METAL PIPE �s" have a wall thickness of 2"minimum to 2.5"maximum. Provide a 1.5"
CPssP* minimum gap between the knockout wall and the outside of the pipe.
� � (STD.SPEC.a0520) 12" After the pipe is installed,fill the gap wlth joint mortar in accordance
with Standard Speciflcation 9-04.3.
,�; � � �p+ SOLID WALL PVC 15.
tiA ao, (STD.SPEC.9-05.12(1)) 3. The maximum depth Trom the flnished grade to the lowest pipe Invert
� � � ` �'.., � � PROFILE WALL PVC �S, ShBII b8 5�.
� S, (STD.SPEC.8-05.12(2))
5 � \\ 4. The frame and grate may be installed with the flange up or down. The
*CORRUGATED POLYETHYLENE frame may be cast into the adJustment section.
1 STORM SEWER PIPE
I e-aR�Z- 5. The Precast Base Section may have a rounded floor,and the walls may
/ ` be sloped at a rate of 1:24 or steeper.
i"
' 6. The opening shall be measured at the top of the precast base section.
\ __ ONE#3 BAR HOOP FOR 8"HEIGHT 7. All pickup holes shall be grouted full after the basin has been placed.
TWO M3 BAR HOOPS FOR 12"HEIGHT
RECTANGULAR ADJUSTMENT SECTION
�GN01 . �
��� �.'� rs����
l`'� / / ��\, e� + ;��I �"'. a�
. f \.. ��,N J. k. ���� I
Q�� � / .: ..,\..\ � I �/� I \�� T���oF WAsq���T�n �y� I
l` / g
t�1���. M =^� � ��"�`'" °�� � ��l�� ��
p /� � I �// I � �nroP�.W"" � ���`�
I �I I O� q�, issea y� .�, ��� � �
#3 BAR EACH CORNER--" � I I M9 BAR EACH C BRMEN - I I �r'r�0\41. ���` �t���� I
� 6�C�
�
I 'f Z
�,� I � // �xrin[;.�u�v i. znnr �$���
� N CATCH BA81N TYPE 1
� � - �
N3 BAR EACH 51DE � ___ I ,- � "' I .:I ff3 BAR HOOP
�� _ e .1 �p • I
8TANDARD PLAN B-5.20.00
�V � ��� /��� 9HEET 1 OF 1 SHEET
APPROVEO FOR VUBLICATION
`v
a3 snR encH wnv —� `" Harold J.Pete►leao OB-01-0B
SEE NOTE 1 �,,,,��ox�,o,�Em are
PRECA3T BASE SECTION ALTERNATIVE PRECAST BASE SECTION �'"�"'^�'°^'"�"°+^^^M^a*�+��^
- �
NOTES �I
� � � , � �, PIPE ALLOWANCES
� i✓,� i � � �; 1. As acceptable altematives to the rebar shown in the PRECA3T BA3E
�" 1 i� > � SECTION,fibers(placed according to the Standard Specifications),or I
� � � ? f. MAXIMUM W��mesh having a minimum area of 0.12 square inches per foot shall
m \ � , PiPE�,TERi�� DIAMETER be used with the minimum required rebar shown in the ALTERNATIVE li
PRECAST BASE SECTION. Wire mesh shall not be placed in the i
� I. ' REINFORCED OR 18. k�OCkOUtS. �
o PLAIN CONCRETE ��
FRAME AND VANED GRATE 2. The knockout diameter shall not be greater than 26". Knockouts shall
AL�METAL PIPE Z�" have a wall thickness of 2"minimum to 2.5"maximum. Provide a 1.5"
CPssP* minimum gap between the knockout wall and the outside of the pipe.
' � (STD.SPEC 9-0520) 18" After the pipe is installed,fill the gap with joint mortar in accordance
� � � ,�„ with Standard Specification 9-04.3.
va �, SOLID WALL PVC 2�.
(STD.SPEC.9-05.12(1)) 3. The maximum depth from the finished grade to the lowest pipe Invert
� � � '� � � shall be 5'.
PROFILE WALL PVC
5 � � S� (STD.SPEC.9-05.12(2)) 21�
4. The frame and grate may be installed with the flange up or down. The
� *CORRUGATED POLYETHYLENE frame may be cast into the adjustment section.
� STORM SEWER PIPE
C �e^oR�z^ 5. The Precast Base Section may have a rounded floor,and the walls may
j � be sloped at a rate of 1:24 or steeper.
: `
� 6. The opening shall be measured at the top of the precast base section.
_ ONE At3 BAR HOOP FOR 6"HEIf3HT
TWO#3 BAR HOOPS FOR 12^HEIGHT 7. All pickup holes shall be grouted full after the basin has been placed.
RECTANGULAR ADJUSTMENT SECTION e
a
����y
� #3 BAR EACH CORNER_
� ` �l F �gry #3 BAR HOOP -..\ 18"MIN. .�
�No�� � / \\ � (S��Q� �'�\
po � • '�6+ �S� // � ej /�,� � I � I
2A � ?�" � � I � /j \ i
� 0 I / \ ♦B i %/ I I I �\ . A// I \ Fi,���,o w SHi�'�,� �����
/ �, � I Nj � �'�� f ��\ , � I % �T �� ,� �}, �,. , �� ��
� �`"� �
- / � �
[�- _ � � i � �� I` � ,. ����
; �
i 4 � G�
- e� � I=� � , II I �,� F;�Sdd�'�o .�� ��� �
��� � -�..� F���1S'P8�` �A' �����
N
#3 BAR i I � ��NA1. �' �
T1N0#3 BAR - EACH CORNER I . � p
��.� � �E%PIRES Jt1LY I, 2007� �S��dF
HOOPS �
� ��� �:= . � �
REDUCING SECTION EACH S DE ` {�<_; � .; � � • I 'I �/ CATCH BASIN TYPE 7L
) STANDARD PLAN B-S.40-00
� I� - / ' SHEET 1 OF 1 SHEET
�^��� " APPROVED FOR PUBLICATION
#3 BAR � Haro/d J.Peterfeso OB-01-06
EACH WAY SEE NOTE 1 --- ,r„�„�„�„�,,,Fq, ,,,,�
PRECAST BASE SECTION ALTERNATIVE PRECAST BASE SECTION �WO���q�S����dT�sloNm
= NOTES
� 1. No steps ere required when height is 4'or less.
V
O
" '-- 2. The bottom of the pracast catch beain mey be aloped to fadlifate deaning.
� `-- _ CATCH BASIN FRAME AND VANED GRATE 3. The rectanguler frame and grate may be inatelled with the flange up or down.
� --___ ' OR MANHOLE RING AND COVER The frame may be cast Into the adJustrnent section.
m
� ��--- �/ �WWDHo�D 4. Knockouffi shall have a wall thidcneas of 2"minimum to 2.5"maximum. Provide
o � - a 1.5"minimum yap between the knockout wall end the oulside of the pipe. Aker
� _" i' tha pipa fs installed,Iill the gap wiM joint mortar in accordance with Standerd
RECTANGULAR ADJUSiMENT SECTION
I� � z --- Specification 9-04.3.
, �� OR CIRCUUR ADJUSTMENT SECTION
.� .. ,..e.,...", ' `'v:- " ^ FLAT SLAB TOP
• - � CATCH BASIN DIMENSIONS
���� - _ _-- - -- --
�'' MINIMUM BASE REINFORCING STEEL
zl CATCH MAXIMUM
� BASIN WA�� �SE lOdOCKOUT DISTANCE Ir�/ft.IN EACH DIRECTION
o DIAMETER THICKNE8S THICKNE88 S� BETWEEN
� KNOCKOUTS SEPARATE BASE INTEGRAL BASE
�B".5�'�90".72'.84'OR 9B'
�' ° .P ' • 48" 4" s" 36" 8" 0.23 0.15
b, ,. . __ ° . � MORTAR(TYPJ ....._ —
54" 4.5" 8" 42" B" 0.19 0.19
�i -
� 80" 5" 8" 48" 8" 0.25_ 0.25
STEPS OR_\' 72" 8" 8" 80" 12" 0.35 0.24
�'I LADDER ,�
gq" 8" 12" 72" 12" 0.39 029
— Q8" 8« 12" 84" 12" 0.39 0.29
�� _ _
PIPE ALLOWANCES
�" -_ ^ , � _ '� �' � e BASIN PIPE MATE MAXIMUM ISOLIDDI PROFI E
RIAL WITH
MORrnR FiuFr -�. � Y � . � ' ,-- REINFORaNci STEEL(TYP.) CONCRETE ALL CPSSP WALL WALL
N � N o � ORAVELBACKFI p DIAMETER METAL �O PVCOO PVCO �
. � 12" PIPE ZONE BE�D NO R t`c N � N' i k
a-.=. r r=, ��.- � � qg., 24„ �„ 24�� 27,� ��� T�C RE aF WASp���'f ���e��
i 8, �. Y;:� q w Y,�� ,�� � �.,a�:� t�,�, x���,�8" ryq. �,� ��� �,� 27„ ��� ;. ��° �--,���i i �� �
�
-3 a .t.��t [ i F���_�v ;�1 �%e,
� 80" 36�� 42�� ��� �„ yZ,� "—_ '" ���n�
SEPARATE BASE INTEGRAL BABE .e , Q. q y
CAETaN�LACE PRECAETWRFiRIEER 9F, ,pF �ssae ,�o .�� ��
72" 42" 54" 42" 38" 48" o � `i
\ � �����
G P
'0`RING ��� �. �» ��� ��� ��� '�'rB/ON�L ���� ,�
' .;' ___— p
,r ' se° eo° �2. �,. �„ 48�• �5���
' ����,. k%PIRfS JIJLY I, 70D7
� ' ORAVEL BACKFILL FOR CU CorruflaMd Polyelhylene Storm Sewer Pipe(Std.Spec.9-0520)
g•�3o�4�y",��f��7,����6,6�-,-�"" PIPE 20NE BEDDINO �(Shl.Sp9C.9-05.12(1)) CATCH BA$IN�PE Z
�l (3)($td.$peC.9-05.12(2))
SEPARATE BASE
PRECAET STANDARD PLAN B-10.20-00
SHEET 1 OF 1 SHEET
APPROVED FOR PUBLICATION
Harold J.Peterleso OB-01-OB
_ Rf�TE DEAqN BqINE91 MTC
�Wmti��.�.o.�.m,.M.�,�.
�
� NOTES
� 1. The pipe auppor�end the flow restridor ahall be wnstructed of the same meterlal and be anchored
� �� at a maximum spacing of 38". Attach the pipa supporls M the manhole with 5/8"steinless steel expansion
��� bolts or embed the supports into the menhole wall 2".
REMOVABLE
-LL _ wa�rtncrrr 2. The vertical riser atem of the flow restrictor ahall be the same diameter as fhe horizoMal outlet
� f 1 ` couauNo plpe wlth a minimum dlemeter of B".
o � 3. The flow restric[w ahell be febnceted from one of the following maEerials:
�v�`�.; `,__ 0.080"Cortupated Aluminum Alby Drain Pipe
r �� 0.084"Cortugated GaNanized Steal Drain Pipa wRh Treatrnent 1
� �---�;� ;; � � oRi CE�TH 0.084"CorrugaUd Aluminized Steel Drain Pipe
� � 0.080"PJuminum allay 11at sheet,in acxoMence with ASTM B 209,5052 H32 or EPS
� '1'._' ! � ELBOW DETAIL High Denslry Potyethylene Stortn Sewer Pipe
A 4. Tha frame and ladder or steps are to be offset so that: the shear gate is visible from the rop; the dimb-down
\ space is dear of the riser and gate; the frame is clear of the curb.
\��
�y � ^ 5. The multi-0rifice elbowa may be loceted as ahown,or all plaoed on one aide of the naer to easure ladder
�`` dearance. The aize of the elbowa and thair placement ehall be apecified in the Contrad
�
8. Rastrictor plate with orifioe as speeified in the Contred. The opening is to be cut round and smooth.
PLAN VIEW 7. The ehear yate shell be made o}aluminum alloy In accordance with ASTM B 28 and ASTM B 275,
0 dealgnatlon ZG32A; or cast Iron in accordance witli A5TM A 48,Class 308.
ADJUSTABLE LOCK HOOK The lift hantlle ahall be metle of e aimilar metel to ttie gete(to prevent yalvanic corroeion),it may be of aolitl
�nnTM�ocK scR�w _ rod or hollow tubing,with adjustable hook as requiied.
MANHOLE RING AND COVER �"DIAM.ROD DR TUBING A neoprene rubbar gesket is required between the riser moundng flange and the gate flange.
�nnrH�ocar+G e0�r3, Install the yate so that the level-line mark is level when the yate is Gosed.
MARKED"DRAIN'
The mating surfaces of the lid end the body shall be mechined for proper fit.
4^MiN. All ahear gete bolis ahall be stalnlesa ateel.
��M�' HANDHOLD
e^MiN.- ; ����o�E 8. The ahear yate maximum opening ahall be ooMrdled by limited hinge movement,a atop tab,
-- ATTACHMENT— Of 80l116 OU1Bf dBVICB.
SET OVERFLOW ELEVATION � '. 9. Altemative shear gate dealgna are acceptable H matedal speGllcatbns are met and Ilange bolt pattem matches.
TO PROVIDE DETENTION AS- -STEPS OR LADDER
SHONM IN THE CONTRACT _���
O'
.. � _- IIFT HANDIE
�� '. _ -' uFrru�Na.e ���F,w J. w�� �i��
PIPE SUPPORT- _='"� '' -� � OF wASy/ F b
3"c 0.075'ALUMINUM � - � SHEAR OATE � ��� �"�T ^'�' � � �
OR 3"x 0.079"87EEL � 12" . __ �• F �� i'd P�. '�r � ��
(SEE NOTE 1) i M�IN. �- '- _" 8"MIN.DIAM. � - `;j�r9�s���s� � �
� :- �� ��g�
__� o _—� A vF�� � 4k`W
OUTLET � INLET o 90 q �sseo o �`� g�� �
_ MAXIMUM OPENIN6 .�� F,,�STE�`L \., s
MORTM(f`/P.)- � 1IYHOLESONIOSIB' s'r�ONpL E�� �����
� � % BOLT CIRCLE � �
FLOW RESTRICTOR- ,n CxPiRES JULr i, 2007 �5���
.
„ _.�__—,� . °,,�-. .. .
REBTRICTOR VUTE CATCFI BASIN TYP!2
VNTH ORIFICE--
�BEE r�oTE e> ___� 54"DIAM.MIN. o WITH FLOW RESTRICTOR
� . LEVEL LINE ; ° STANDARD PLAN 8-10.40-00
(SEE NOTE� CLOSED
SHEET 1 OF 1 SHEET
Vf� /_'� FRONT SID!
�� APPROVED FOR PUBLICATION
Harold J.Pete�/eso OB-01-08
SHEARGATEDETAIL8 � e*.�o�.����a o.+�
�Wwhl�qbn Sb1�D�pwlmw�td7�v�wh�lw� ,
�� -....._... �I
� 6�/Z" ',R NOTES
�
� ��� 1. The asymmetry of the Combination Inlet shell be considered when
� HooD- � ' _ wlculatlng the otFset tlistance for the catch basin. See SECTION A.
1"MIN.
m ��.M�N O e _:__==�"'� 2. The dimenslons of the Frame and Hood may vary sllghtly among dff-
ferent manufacturers. The Frame may have cast features Intended
� : 1/2 OPENING OPENING HEIGHT to support a grate guard. Hood units shall mount outside of the
� HEIOHT a•MiN. Frame. The methods for fastenin the Safe Bar/Debris Guard Rod
0 TO 1'CLR.--� 9 tY
:== to the Hood may vary. The Hood may indude casting lugs. The top
_' TOP OF bRATE of the Hood may be cest with a pattem.
SEE NOrE 3- � _' � - - , — 3. Attach the Hood to the frame with two 3/4'x 2"hex head bolts,nuts,
// / � /� \�� - FwuNE and oversize weshers. The washers shall have diameters adequate
' ._-- - , to assure full bearinfl across the slots.
---- - ---- ---------
----- ---- ---
- --
�_—___ - - � 4. When bolt-down grates are speclfled in the contrad,provlde two
1��, .�� holes In the irame that are verUcally aligned with the grate slots.
- - --- - - - - - Tap each hole to accept a 5/8'x-11 NC x 2"allen head cap screw.
--- Locatlon of boR-down holes varles among diifere�t manufacturers.
SAFETY BAR/DEBRIS QUARD See BOLT-DOWN DETAIL,Stendard Plan B�0.10.
5/8"MIN.DIAM.STEEL ROD
SEE NorE 2 DETAIL SECTION OA 5. Only dudile iron Vaned Grates shall be used. See Standercl Plans
8-30.30 and B-30.40 for grete detalls. Refer to Sfandard Specifl-
cetlon 9-05.15(2)for addkional requirements.
8. This plan is Intended to show the Installetlon defails of a menufao-
CATCH BASIN tured P►oduct. It is not the intent of this plan to show the specific
M�, � details necessary to fabricate the casdngs shown on this drawing.
(�o.5e') I I
2�'MIN. FACE OF_ ��' ���0.25� CURB OR CURB AND GUTTER -
1"MIN. 20 1/4" CURB � I i
TYP. ; — O��� MATCH TOP OF HOOD �'" i
I i� TO TOP OF CURB(TYPJ
b
Z ..� — ... r+oou _ �� T��Ew N r. �y�r� �����
, � ������ ,fsH,�� �� � �a
�!.' ay SEE NOTE 4 I 3AFETY BAR/DEBRIS GUARD ����:, �� � ����
` F �P.) .� ..I '. � A � y�E�5
z 34"(WIDE SID� '• /�% -j 20"■24"VANED ORATE ' g
3EE NOTE 2 _ : �"-�j A �+ a
(7yp,) + ? CATCH BASIN TYPE 7 =- j`.. o,�, qF�s5ea0.Qo �v 5��pi
� � A i;l<I -.: �<T�% Fs �STQ, ,.� ��,i�
N 1 � /!� I "'%' "��"� � � FRAME r�01v'AL ��, � S
HOLE OR SlOT FOR � ' I�40"(1MDE SID�I.�. r'" '�2�' < �
�;:' ',, �:
_ '<f'-� �-`;�..::- �!
ATTACHING HOOD(TYP•) CATCH BASIN TYPE 1L -�.�� �-� [zriR[s du�Y i, zoor 45���
I \ ��, , ,
" ,�=" COMBINATION INLlT
�
-- sTANDARD PLAN B-2S.20-00
SEE NOTE 1 �' BHEET 7 OF 1 SMEET
TOP VIEW
nvrreoveo Foa vueucnnor�
FRAME DETAIL SECTION OA ISOMETRIC VIEW Haro/d J.Petsr/sao 06-OB-06
COMBINATION INLET R•��� a�
FRAME,HOOD,AND VANED ORATE �~�"�"�°"""'°ij'""'"'MT""+'"'"°"
ze v�' NOTES �
� J � 1. Thh freme h denigned to ecoommodaEe 20"■24"gretss or covero as ahown I�
� on Stnnderd Plam B�0.20,&30.30,&30.�0�nd 8-30.50.
2. Whsn bolt-0own prates or coveis ais ap�alisd in the Contrad,provids lwo
m hobs In the frams that��veNcNly aligned wilh ths praE�or eovx slota. Tep
sech hoN to aoospt a 5I8"-11 NC�2"alNn Rsad cap ecrew. Location of I
� — boR down holsa wriu�morg dlffeient manufaclunrs. I
0
3. Refer to standard Specifiution 8-Ob.15(2>for additional nquinrtisnfs.
RECE89ED ALLEN
BOLT-0pVJq HOLE(TVP.) HEAD CAP 9CREW-,
-61E'-71 NC,SEE � _,Y ��, N!"-11 NC x 7 �-
DETNL 8 NOTE S �..{
!l4' ORA7E- �
Y ��
N, � �
N `= � I
o r �� , � F��
� _
_..�� j/.: '� � �� �
L
�
_ -__ .. I .__ Z��
r aecTwn
1 BOLT-DOWN�ETAIL
�- � DETAIL OB SEE NOTE 2
TOP
�FUNGE UPWARD p`�
FRAME CAST INTO PRECAST :.-... / ��F,W J. (f�'r I Q�t
a �
ADJUSTMENT SECTIOH-SEE .-'� t �'. � �Q pp WASy�� iC+n ���6�
STANDARD PUN&30.Y0 FOR� -� �/� Z' e 1' � �
ADJUST}AENT SECTION DETNLB .. �� " .�� �� �-. � `'� ��ti� �' f
. -/. '\ '. .. � .
� . -
i' - _
� � � .. I
. �...,`\::\ ..
2�t1M' .�' ���� �:�`�: \.'�..... 4 �. " �M � �k3�EY
__ - --/�'�
;�v> .-' y y C'y'
/" O� .pF 15598 �O �V :1{ �
:�''�� Fr �rsreP ��:
�'�-��. � \�"�. S�ONAL �'� ��g��
��� „ .E%PIRE�JULY I, 200T YS��Q
i/
RlCTANGULAR FRAME
���
/%/"%% ���,... (REVCRSIBL!)
°'�� "'%''� 3TANDARD PLAN B-30.10-00
:.%
��- -' ` \�� !'/%�� SHEET 1 OF 1 SHEET
�''�.� �� � j i
EECTION OA � �w�eoveo Foa rueuc�nor�
.i
� ' Haro/d J.PKerRsao 06-OA-06
.�'-.,Ij'�...,'l'i" R�llWOMBIO�IFH1 M1E
�B�M�R�i�� �YYaµ�n f�yy p�yslin�M d T�v�rll/�n �
SH01MN0 TT1E VARIATIONS ��� ��
- �4 � � ------ -� I� 3^ _ NOTES .
� � 1. When bolt-down covers ere speafied in the Contrad,provide two alota
� In the cover ttiat are verticaly allgned with fhe holes In the hame.
� � � Locetion of boft-down elots variea emong dlffarent manufacturers.
�
� _ u� 2. AttemaWe relnfordng desipna ere axeptable In Ileu of the rib design.
_
m 1 �
� a 3. Refer to Standard Specificatbn 9-05.75(2)for additbnel requiremenb.
� BOLT-DOWN SLOT-SEE �
0 oeTN�nNo NorE i i 4. For hama deteils,aee StendercJ Plan B-30.10.
�I
I �
i-z�rz•ouM.H � �� __ _—
� � + � � L-'
_ -.
!� � I �--�- -- _ _,.__-_=--- i - _ � 'I —._
�. . . � �, 'v, =_�__ . � NI � __91/Y � I I.
J -_ � � — � -- i I �
. _ ; � _ ; -' _-,� �. ':\. T3M' f y,' �I
�� _.,; ' ,_�. __ _ ' ` �� i \ � ����� I r�•
_-_ _--' _- '__ "-_'' --_ ' ' i \����� �._ . 7 7/4'
� I 14'DIMI.HOLE
.-. .-.. ____ --' . "__= _-_ "__- _-_ '-'" _ _ I I�;17 1Q'DIAM.HANDLE , ___ .
-_ ' __I ___. -�_ _ - ___. � \� � I
\�
\ . �
SECTION C ,
� O \
B \�
TOP SECTION OB \ I � \`�`.
\ ,
BOLT-DONM SLOT DETAIL
SEE NOTE 1
� ��a•_ ��rz• . '� b W�' �9���
�` W J. �
~� .. ���� `/ � '��OF WAS%�/�„ F( e'6
� � . ����
,.� l���'�`j .. . � g� �$Z:iy �/� i �
�` ,`��`�f����� :._ < � ���CQ ,
} ,. -�l>>���>��y l�i y� < . �d J R' g k M
�` ` �� �I .��`��>��`,�<>iJ�``�> �< y � ��� � Cy� i
1 /, � l 1 O 1.5(ie O .�V !$�
} i _ + � 1^ : l /,. � F F Q�
-°� >G�9 !�j<<I != i �l�,:! > /-> ! ,l STF.H
- , `���>`�j�r�pi�G�j�>i<<��>j�J�,� ��'r/0.\.41, F�C` �����
' � ara-seeNorez `"v��l���>G����>�����J���?.>l? " �5���
SECTION OA `lG'�j'���/j���7�116i":': , f%NIHEs JULY I, 2007]
> '!7 _
.. G�;j`1�b��y f�`l<-�y!-�>< :/
�<<���!����,>>`� --� RECTANGULAR SOLID 'I
� ��:.
���>_�l>_�t->= -' METAL COVCR
'�-...11r1��,�� � I
L l, .
<<� 8TANDARD PLAN B-SO.ZO-01 !�
SHEET 1 OF 1 SHFFT I
APPROVED FOR PUBLICATION I
ISOMETRIC Kevin J.Dayt�on 11-21-06 'I
� ei�re oeeiow aoixea -wrz
Tw''"".,.""°"°"'�."d'"'°"�."
NOTES
�
� , ,� 1. VVhen bokdown grares are spedlled In the CoMract ProNde Mro slote
Y In the orete that are veNcelly eligned wkh the holea In the freme.
g �i� LocaUon oi bolt�own abts verles emonp different menufaclurors.
3
� 2. Refer to Stendard Spedlkatlon 9-05.15(2)for eddltlonal requlremente.
b
� _ � .. SLOT-SEE DETNL h 3. For Fram�detalls,see Stsnderd Plan 8-30.70.
.... AND NOTE t
u -
4 J y , � .v-_
H ; �
_ � _ �_
� H -- --" � �+!
� a � �- y� ''
� _— 1 1M' I
g ' �1
h I I
[a FLOW� -_. 'al I \�.,. .
1 '
d I
TOP � secnoN e I
O
BOLT-DONM ELOT DETAIL
SEE NOTE 1
��,w r. ry, �S� �
z,• z
7 OR 8 EOUAL SPACES ���qQ��p W��h�Ay,,�Fr� �
_- a
� . _ ._ ? 5� ���5-� �' � �� �5
�
� �DIRECTION OF FLOW � � � �r�k�
A �
o,r, qp issee Qo � ��� i
� Fs����sTv,����• �����
' o`�� �
[[a�iRE>.�u�v i;zno7 �5���
aecnoN O
RecrnNauu►R
VANlD GRATC
STANDARD PLAN B-30.30-00
BHEET 1 OF 1 SHEET
MPROVED FOR PUBUCATION
isoMETRIC Haro/d J.Peterfsao 06-01-08
-n.h��� a,�
�w.��A.�.�.r�w�.�wat�.�r.�
vi
DRlll AND TAP SIB'-71NC 1 31B' 1 7A6'� �'I
= HOIE FOR 1 12"x'SIE' �� i VIMSMFA ��8 �I
STNNLE$S$iEEL$OCI�i
(SEE NOTE� �
� I HEAD CAP SCREW(7YP.) . _ -_� �} � �!- ��I �. T}10 Q88k�811d QIOOVE RICy bE IfI 1�M 8E81 �'
! � � I � � �_ (frame)or in the underelde of the cover.
���. � + The gaeket may be"T"sheped In eecllon.
� � I� � t�e^ � � -��� The groove may be cast a machined.
w � i �
> -- --- 1 -- A - - - �_---- A � } 2. Forbolt�am menhols dnp and eovere
m i ��rj-_ �l_��� that aro not desipnated"WetertlphY.1M
�` ' � ' �ej R� � N � �1M(MIN.) �rone geekel,9roovs and washer are
� � � rsquirsd.
�. ; ! vr owera�ortoove 3. Washer shall be neoprene(Delail"B'�.
�.. 4� � �-NA7H NEOPRENE OABKET
(SEE No�s) 4. In Ibu M bllnd pldc rwtch for atam sewer
12'(TYP.)-' i SEE DETNL'B' � �/r Ryp,� BLA1D PICK NOTCH WLT-0OYMI I WATERTOHT menhole oovere,d1111 tlIfBB 7"d18f119bBf
DETAIL^A" DETAIL"8" hdes at 120'epadny.
RINO PLAN RIN(3 PLAN
5. Proprietery manhab oovers wlthout bottom
rlbs are ac:oepteble.
9 1YfE' e�+�"
- �� 1� ��� �--1 �, � e. Fo���, �„����,��
Seetlon h�s been exagperated,ft b 1.5
��'� r' � tlmen the horizontal scab(1H:1.5�.
a
� ;:� '�
m� � �. b � � ti �� „ �
T �• z+�•, � � � ,
�I �y4• � � � x_=�, +�M• ^sre•n�icK
� z, _ � � �" ' N� m t� � �.� y
s�va- si i�a s v�• are^TrncK I �
sar on c�ut rne�oavw oewce ��r*
� , �
RINO SECTION OA RINO BECTION OA I----e�'�_ � ' ;' ' I
BECTION OC _---�
EIOD f3ROOVE PATTERN
ao�r on c�M rrre wcaaHo olwcE DETAIL
sao oRoove DETAIL"C"
PATTERN-SEE
DETNL - SEE DETNL"A• SEE DETAIL'A' ��- (i
�o,ee. �i � ...,e, �.
.�vo�a
�••��� eeesee � " SPEGFY LETTERINO
....�.
TOP - � TOP W J. y
_ �_' _ B ,... , ' B `___ _ e �� w' i�
eorra� � - eorroM �'� ov es �' �A �F
W
/� ! S���'CQ �j,�h�'�F,'pa�r'� � �!�
��F'� / r � �
��� ' r 8EE DETAIL'A' �,SST �A tl�C
� � UFT HOIE _T
� � � � ��g F�
COVER PLAN COVER PLAN COVER PLAN ' r 7 l � �'o�.S q F��sg q70.l�C�`" °°�<�
♦' g� ��
eEEDETIuI'B' s�ONAL �'P �
� �e SEE DETAIL•A• L° SEE DETAIL'A' �o b SEE DETNL'A' _ p��C
^� N I �� � � �I �+ � E%PIRES JULY I, 2009 YS�a�
1 L
T T T CIRCULAR�RAME(RING)
v.•����1I�'i°� � 'a� ���'�r 'I }—II-°i'� k1 AND COV[R
� N N �E p���� N I 3TANDARD PLAN 8-30.70-07
COVCR EECTION �B COVER EECTION �B COVER SECTION �8
SHEET 1 OF 1 SHEET
(SEE Iq7E� (8EE NOTE� (SEE NOTE� MPItOVED FOR PUBUGTION
Peaco Bakotich II/ Od-91-07
STANDARD BOLT-DONM/WATERTIOHT CAMLOCK s �"�"��� ��
TYPE 1 TYPE 2 TYPE 3 ISOME7RIC vtew �/w�`""""`�`"~�''�'��`"
� TRENCH WIDTH _y_ NOTEa
(SEE NOTE 3)
1. See Standard Spedficatlone Section 7-08.3(3)for Pipe Zone Badcflll.
k �,�' 7 l) " � #
piaE zoNE encKFi�� 4'�x�'�����r"��'"( �, I 2. See Standard SpecNlcadona SecHon 9-03.12(3)for Gravel Backflll for Pipe Zone Bedding. I
(SEE NOTE 1) �- ��7r���i ����c,_, � �'
)C)��� °� ' ' I 3. See Standard Speciflcations Seetlon 2-09.4 for Measuroment of Tiench Width. I
X) �'�(y j:f W i �
) ,i
��,�n� �� t i.
�rSr_+�,� c.��`� h �; 4. For eanitary sewer installatlon,conaete pipe shall ba bedded to aprinp line.
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(SEE NOTE� - � s
-16%O.D.
FOUNDATION LEVEL Jp'�. —I
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CONCRETE AND DUCTILE IRON PIPE _ rnE"°"""oT"
(SEE NOTE 3) �
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GRAVEL BACKFILL FOR �ry_�1' �..�,X-��' � o PIPE ARCH 18��O�" 1z•' AND BACKFILL
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,.y� �`+'� 148"to 200" 48"
.
ri\r .4.—� � -- � __ SHEET 1 OF 1 SHEET
FOUNOATION LEVEL J�•Y , � b I APPROVED FOR PUBLICATION
� ` -! -'! � _ ��A� � Harold J.Peterfeso 06A1-0B
� e..,��,��.E� an
METAL PIPE T w������i� �
ReFow�eo rire eNos� COUPLING BAND DIMEN310N TABLE
vr.e�eo�r�rw.�
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���;�', -i1'
� ^ �'� o � 2 2/3 x 1/2
s� ��,., OR
flJ�„y � i-�� 3"� 12-84 12 SLEEVE
� I j' REFORMED TO
��. BAND lAP NOT 9HOWN � 2 2/3 x 1/2
_-_:-..� :_.-..t,.. �. :.� �� FORcwxmm'P.) 3x�— _
TYPE D TYPE D REFORMED TO �'�� 24 SLEEVE
ANNULAR CORRUOATED BAND BAND ANOLE CONNECTOR DETAIL W 2 v3 x�2
�u 2213■1/2. .
� OR
REFORMED PI�ENDB F 3"� 12-84 10 12 O-RINO
W j ia-•e-ao�r RrP.) _ REFORMED TO
�'�;9 2?!3■1/2
`r � _�_ � 5iv J 2 2/3•12 12-48 2 3/4 BUTYL
� � � �_�i -.. � 2?J3 x 1/2 12-48 12
�,-_'`' u = K 54-84 24 SLEEVE
,�\ .�../! ..� //%/" � '�3K1 54-144 24
. , % / // m� � _ 2 Z3•1/2 72-72 12
�/ LC p 3■1 38'60 12 SLEEVE
"" "" l� % �� � REFORMED TO ���08 24
TYPE F TYPE F TYPE F = 2 y3"�r1
SEMI-CORRUf3ATE0 BAND BAND ANOLE CONNECTOR DETAIL BAR 8 STRAP CONNECTOR DETAIL j F 2 2/3 x 1f2 12-48 10 12 O-RING
a 22/3x1/2 12-46 12
REFORMED PIPE ENDS K 54-84 Z4 SLEEVE
w�rrf FwacEe «3�1 64-98 24
` i
W / "PIPE ARCH ONLY
i �
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TYPE� BAND ANGLE CONNECTOR DETAIL y � F, g G
FLANOEBAND o,�,F qf�ISTM0.yo �� °3Y� i
rs �C` �����
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EXISTINO PIPE NATH NEW MPE EXTENSION , 1/2"•8'BOLT(fYP.) � ��
HEl1GLL END �'�� i W� ��� �TH REFORMED END ; . _ � p
OR HELICAL END f �ExPieE°..iul v i, 7007 ���'�P
1�
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\ ��pJ- rr3� -4�"�-�'� - �� '�� COUPLING BANDS FOR
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�
SHEET 1 OF 1 SHEET
/ APPROVED FOR PUBLICATION
-��"��-:� _ _ \. : ....1 .
TYPE K TYPE K TYPE K Harold J.Pets►Aeso 06-01-08
� rt�n ocao�a�axEa wa �..
FLAT BAND OR DIMPLE BAND BAND ANOLE CONNECTOR DETAIL DOUBLE BAR 8 STRAP CONNECTOR DETAIL �"�'�"°'°"f'°"'°'°'""""N T�
NOTE9
END SECTION LENGTH SHALL BE AT LEAST SIX T1MES THE DIAMETER OF THE PIPE(SEE STD.SPEC.7-02.3(1)) 1. The culvert ends ahall ba beveled to match the embankment or dRch
I� � slope and ahall not be beveled flatter than 4H:1V. When ebpee are
beNueen 4H:1V and 6H:7V,shape the slape in the viCintiy of the
culvert end to enaure thet no pert of the cuNert protrudea more than
�J 4"above ffie ground line.
''''''''''''''' 4N 2. Field culting oi alvert ends Is permitted when approved by the Engineer.
i I I i i I:',I,;j',; 1V pR S All 11e1d-cut wlvert pipe shell be treffied with heatrnent es ahown in t�a
I:I i i i I: TEEPfR Stenderd Specifications or General Special Proviaions.
iiiii
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THERMOPLASTIC PIPE
--- "�� --- --- ----- -_
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4H'V oR S�EPER
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END SECTION LENGTH SHALL BE AT LEAST SIX TIMES THE DIAMETER OF THE PIPE(SEE STD.SPEC.7-02.3(1)) � ,�'�,�,a 4r°` ����y
_ ___ _ _ _ ._—_ _ _ _ . .
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���?--R S�EPFR sEVELED!ND 8ECTION8
,� \�\� �,�� \ � � I STANDARD PLAN B-70.20-00 ��,
\ � �� , .. � .. , . . . . �' \ , ` .. �. �,. . ... � � 1 SHEET 1 OF 1 SHEET �
... , . ., . ... � .
' ' ... ..- . . .. '.. .. ...:.. .. ... �..� -. .-. - _ _ . _ . , .. ,.. . �..�..' _ _ - - , I APPR F R WBLICA i
. . _ _ .. .. .. _ _ ._. ._ _ . . .. :... . ...:..:.. ..,.. ,.. .. _. OVED O . ._ TION
- - - - - - - - _ _ _ . . _ - 4"MAX. I
Harold J.Peterf�eso OB-01-OB I
R�TEDENOMBIWx[a � MlE i
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Hydraulic Report
Strander Boulevard Extension Project
Cities of Renton and Tukwila, Washington
Appendix E - Pump Station Memorandum
�� ���_�.���� /, * �( %QO"�orthea<_t Mu tnomah S ce;,5�itc Q�,: Gortiand.Orf�,lon 9�i32 41�t9
�/ ��
1"11V1 503 Fs7� 91CU • SO '872 41Q` FGx • .v;u obam com
Memorandum
Date: 2 February 2011
Subject: Strander Storm Pump Station—Preliminary Design Concept
From: Matt Huxley, BergerABAM
To: Jim Guarre, BergerABAM;Naomi Selove, BergerABAM
Project Strander Boule��ard Extension, FAPVVT-09-175
Name &
Number
Route to: File
Executive Summarv
This memorandum has been prepared to present preliminary cost estimates for constructing
storm water pumping stations for the Strander Boulevard Extension Project. Preliminary cost
estimates were prepared for four pump stations, described as follows:
1. Pump Station A-Storm water pump station to serve the phase II area only
2. Pump Station B -Storm water pump station to serve the phase III area only
3. Pump Station C-Storm water pump station to serve the phase II area initially but
expandable to serve the Phase III area
4. Pump Station D—Storm��ater pump station to expand pump station C to serve the
phase III area.
The estimated costs of construction for each pump station are summarized in Table 1 below.
Table 1—Estimated Construction Cost Summary
Pum Station A-Phase II $820,325
Pum Staiion B-Phase III $1,234,750
Pum Station C-Phase II Initial $920,150
Pum Station D -Phase III Ex ansion $286,000
Pum Station C+D Total for Phase III $1,206,150
�� Ber erAI3AM �00 Northeast Multnomah Street,Suite 900,Portland,Oregon 97232-4189
�� � 503/872-4100 • 503/872-4101 Fax • www.abam.com
Project Understandin�
The Strander Boulevard Extension Project will be constructed in three phases. Phase I will
extend and improve existing roadway from Oaksdale Avenue Naches Ave SW. Phase II will
construct a two lane underpass from the western end of Oaksdale Ave SW to a new Sound
Transit parking lot between the Union Pacific Railroad (UPRR) and Burlington Northern Santa
Fe(BNSF)railroad rights-of-way. Phase III will extend the underpass to the West Valley
Highway and expand the width of the roadway beiween from the highway to Naches Ave SW
by adding two additional vehicle lanes and a multi-use path. The phase II project will be
constructed by the City of Renton. The phase III project will be constructed by the City of
Tukwila.
Storm water from the phase II and III projects will be conveyed to a new water quality wet
pond that will be constructed in a wooded area south of the underpass. A storm water
pumping station will be required to transfer storm runoff from the underpass to the new ti�ater
quality pond. The phase II pump station will also be required to convey appro�cimately 400
gallons per minute (gpm) of groundwater in addition to surface stormwater runoff.
Governin�Design Criteria and Standards
The Cities of Renton and Tukwila defer to the King County Surface Water Design Manual (2009
edition)for goveming standards and criteria pertaining to the design and construction of new
stormwater conveyance facilities,including pump stations. Both Cities have amendments that
apply to new stormwater facilities within their jurisdictions. Key design criteria and standards
that apply to stormwater pumping facilities for this project are summarized in Table 2 below.
Table 2—Governing Pump Station Design Criteria
Desi Storm 100-Year'
Peak Runoff Estimatin Methodolo Rational Methodz
Minimum Number of Pum s 23 ,
Backu Power Re uired Yes4
Notes
i—Reference KCSWDM Section 1.2.4.1. The 25-year storm event is typically used to size new com-eyance
facilities unless the 100-year event would cause significant flooding problems. Given that the pump station
�vill protect a sag curve of a road�vav�vhere storm���ater can pond,the 100-year event should be used.
2-Reference KCSWDM Table 3.2.
3-Reference KCSWDM Section 4.2.31
� 4—Per Citv of Renton amendments
�� � . . : �� . i 1'�,:;'r'1• .�1 �a`.,.: ,���-� .. • _ � . - �,. .�,�.� , .��-)
�� � �,...,_
The Cit�r of Tuk�vila is in the process of developing detailed storm�-vater pump station design
standards w�hich will apply to all new pump stations within their jurisdiction including phase
III of the Strander project. These standards are based on an existing stormwater pump station
at the 180�''Street underpass which was designed by BergerABAM in 2000(pump station no.16),
and a new stormwater pump station currently being designed by David Evans and Associates
(DEA)for the Southcenter Parkway Extension project(pump station no.11}. BergerABAM staff
met with the City of Tukwila Engineer,Superintendant, and maintenance staff at the 180�Street
pump station on 3 December 2010 to review the 180�and Southcenter pump station designs,
verify appropriate standards for the Strander pump stations, and "lessons leamed" from the
180th pump station design.
At this time the City of Renton does not have codified design standards pertaining to
stormwater pump stations aside from the basic criteria listed in Table 2 above. However,
BergerABAM design team members met with City of Renton Public Works and Engineering
staff on 10 January 2011 to review the project stormwater management concept, including the
pump station. City of Renton staff stated specified design elements that they will either require
or prefer to have incorporated into the new phase II pump station. These requirements and
preferences are largely based on the City's experience with their existing stormwater pumping
stations. The City also provided BergerABAM with example drawings and specifications for
two stormwater pump stations to be used as design guidelines for the phase 2 pump station.
T'hese include the Stonegate and Baxter Lift Stations.
In general, Renton and Tukwila's design requirements for stormwater pumping stations are the
same. Where the guidelines differ,the City of Renton's standards will take precedence for the
phase II pump station as this facility will be constructed by, and initially owned and operated
by the City of Renton. The only major difference between the two jurisdictions is the choice of
pump manufacturer. The City of Tukwila expressed a preference for Cornell units whereas the
City of Renton stated that the}'prefer not to have Cornell pumps due to their poor performance
record in an existing lift station.
Stormwater pump station design standards for each jurisdiction,based on the meetings and
subsequent review of the guideline pump station designs, are summarized in Table 3. These
standards��ill apply to the new Strander Boulevard Extension storm�vater pump station.
�� Ber erAI3AM �00 Northeast Multnomah Street,Suite 900,Portland,Oregon 97232-4189
�/ � 503/872-4100 • 503/872-4101 Fax • www.abam.com
Table 3-Stormwater Pump Station Governing Design Standards
Pump Station City of Tukwila Standard City of Renton Standard
Com onent
Wetwell Circular wetwell preferred with Circular wetwell with maintenance
"Raven" lining,maintenance platform. No preference stated for
platform at high water level, liner or fitting materials.
access ladder, and stainless steel
i e and fittin s throu hout
Minimum Number Two,with single pump capable of Two,with single pump capable of
of Pumps meeting design flow. Altemating meeting design flow. Altemating
operation. operation. Consideration given to
dedicated groundwater dewatering
um .
Pum T e Submersible Submersible
Drive Type Constant Speed Constant speed. Consideration
given to variable speed for
groundwater dewatering
o eration.
Pump ITT Flygt or Cornell ITT Flygt or WEMCO-Hidrostal
Manufacturers
Primary Level Pressure Transducer Ultra-Sonic
Control
Backup Level Single float switch to cycle pump No preference indicated.
Control for 30 secands
Standby Power Required for storm pump stations Required for this application.
protecting roadway sag vertical Diesel genset housed in a building
curves. Diesel genset with sound for noise attenuation. No
attenuated weather enclosure and preference for manufacturer.
skid mounted fuel tank. Sole
sourced from Cummins.
Controls Building CMU block controls building Controls to be housed in generator
required for motor control center building.
(MCC), power feed,
instrumentation, telemetry,
generator automatic transfer
switch(ATS), and breaker panel.
Controls building to have double-
door access.
�� �����e���z�� A � /( 700 tr'ortheast Multnomah S;reet.S�ite 9�0.Pcrdanc+,Oregc�n 97237 4189
1"11�i1 503!872-4100 � 503i87[ 410 i �ax • w�a��v.abam.rom
�� �
Conduit Routing Provide"fibercrete" utilidor Non preference indicated.
between controls building and
wetwell for routing conductors.
Mount pump disconnect box on
outside wall of controls buildin
Flow Metering Not required for storm water Required
um stations
Lessons learned from the 180�h Street pump station include providing sufficient pump operating
volume, paving all vehicle access areas,locating all facilities within close proximity, and placing
the disconnect boxes above grade. The 180th Street pump station has a 6 foot diameter wetwell,
no upstream storage volume, and thus very low operating volume. Pump station records show
that the cycling frequency approaches 60 starts per hour during the wet weather season which
is well in excess of the typically recommended maximum number of 10 starts per hour for small
submersible pumps. The high cycling frequency reduces motor life and increases the
probability that the pumps ma}' overheat and shut doH�n during critical periods.
Desigrt FlozUs
Using the Rational Method per the KCSWDM, the peak runoff volume flow rates �vere
estimated and are summarized in Table 4.
Table 4-Peak Runoff Volume Flow Rates
Pro'ect Total Im ervious Area Peak 100-Year Flow
Phase II 2.1 acres 2,870 m
Phase III 6.8 acres 9,380 m
Additional stormwater pump station design guidelines and standards that pertain to this
project include:
• Washington Department of Transportation-Hydraulics Manual (2010)
• Washington State Department of Ecology-Criteria For Seti�age Works Design Manual
(2009)
• Federal Highway Administration-Highway Stormwater Pump Station Design Manual
(2001)
• Hydraulics Institute-Standards for the design of sewage pumping stations
Refer to the main body of the project Hydraulic Report for design guidelines, methodology, and
calculations used to derive the design flo�vs stated above.
'� Ber �ll u.Jl 11r1 �00 Northeast Multnomah Street,Sui[e 900,Portland,Oregon 97232-4189
�� � 503/872�100 • 503/872-4101 Fax • www.abam.com
Storm Water Pump Station General Design Considerations
This section is intended as a general stormwater pump station design reference and describes
stormwater pump station components and configurations,in addition to the aforementioned
Cities of Renton and Tukwila design standards.
The basic components of a stormwater pump station include the pumps, discharge piping,
valving, valve vault, wetwell, and controls. Additional components may include standby
power, control and standby power housing, inlet and outlet structures, and
equalization/operating storage. The main components are described as follows:
Stortnwater Pumps II
The most common types of pumps typically chosen for small to mid-sized stormwater pumping �
stations include vertical turbines and submersible pumps. �'
1. Vertical Turbines-The motor and um are connected ��ia a shaft that extends throu h I'
P P g
the pump discharge piping. The pumps are immersed in the pumped media and I
connected to the motor via an extended shaft. The motors are either installed at-grade �ii
or on an intermediate motor level. The advantages of this iype of pump are lower �,
installed and operating costs for larger units (>75 horsepower(HP)), ease of access to '
the motors, and slighdy higher efficiency. Disadvantages include the need to provide
protective noise attenuated housing for the motors, reduced cycling time, and the
requirement to decouple the motor and shaft to access the pump. The installed costs
increase substantially as wetwell depth, and hence shaft length between the pump and '�
motor increases.
2. Submersible-The motor and pump are usually mounted tugether on a common frame
in a close-coupled arrangement with the entire assembly sitting submerged in the
pumped media. The main advantages of submersible pumps are that the entire unit can
be removed in one piece,motor submergence allows for more frequent pump cycling
(and thus lower wetwell operating volume), and they usually have lower installed costs
�vith smaller(<75HP) sizes. Submersible pumps range in size from 0.5 HP to 400 HP but
are usually the preferred choice in smaller(<75 HP} pump stations.
In accordance with the Cities preferences, submersible pumps are considered to be the
preferred choice for this application. This is especially true given the expected depth of the
ti�etwell (<30 feet) and limited required size of the pumps. Preliminary sizing calculations
�� �,�}�������.'I.1 1.LJJ: 11l�1 ;CO�crtheast"v1u�nom.,h S, Ee?.5uite�G;,Fertiand.�rec on G�23� i i89
�� ,p,. 5'si8?2 4+00 � ��_�n7�-410' Fax �.i'�s 7bam.c�m
s.._
suggest that a 40 horsepo�ver(HP) (nominal) pump �vill be required to meet the phase II design
flow.
The number of pumps t}�pically varies from two (duplex) to three (triplex), although four or
more pumps(multiplex)are not unusual in a stormwater pump station that might experience a
wide range of flows during its design life. Multiple pumps (three or more) allow for greater
flexibility of operation over the wide range of flows often experienced by stormwater pump
stations. In accordance with the City's requirements, the pump station will need to have 100%
redundancy meaning that the design flow must still be met ti�ith one pump out of operation. As
such, the new facility ti�ill have a minimum of two pumps.
Both Renton and Tukwila have expressed preference for the ITT Flygt brand of pump. The
manufacturer's recommended pump model to meet the phase II design flow is a Flygt NP 3202
LT with a 314 millimeter(mm)impeller and 45 HP (40HP nominal) motor. The pump curves
for single and parallel operation are shown on Figure 1—System-Head-Capacity Curves.
Dewatering Pufnp
The City of Renton requested that consideration be given to a dewatering pump in addition to
the primary stormwater pumps. The dewatering pump would be used to pump groundwater
and augment the primary pumps to meet stormwater flows. As groundwater contribution is
expected to be constant and vary little throughout the year, the dewatering pump w�ould
operate on a mostly continuous basis. The main advantages of a dewatering pump are that the
life of the stormwater pumps might be extended as they would not cycle as frequently during
dry weather periods, and the size of the stormwater pumps could be reduced as they would not
be required to singularly meet combined storm and groundwater flows. The disadvantages are
the increased capital cost of the dewatering pump plus piping and controls,space limitations in
the wetwell (potentially requiring a larger wetwell which would substantially increase project
cost), and the fact that a continuously operating dewatering pump would likely cause the
stormwater pumps to lie idle for much of the summer dry weather season. In general,pumping
units need to be run fairly frequently to ensure lubrication is distributed around moving parts,
coolant gets Elushed, and solids do not settle out in the volute and impeller. Some
municipalities, including the City of Portland Bureau of Environmental Services report
recurring problems with pumps that sit idle for a substantial length of time. Furthermore, the
low anticipated ground water flows suggest that the stormwater pumps would not be reduced
in size with the addition of a groundwater pump. For these reasons, a continuous duty
dewatering pump is not recommended at this time. However, preliminary sizing suggests that
a maximum 5HI'pump could meet the dewatering requirements. A small sump pump of this
size could be added at a later date with little modification required of the wetwell. If the City
�� „ � =�� %�;[l�'JOr[t�ed�; 4^���i t� �h� rt t _, t � ,,. F r I,r i rF ,.,,.. �� ?lii9
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e
prefers a ground�a�ater pump��ith a quick disconnect and lifting rail assembly, then this should
be added during initial construction given the extra space requirements of this arrangement.
Wetwell
An adequately sized wetwell provides enough physical space for the pumps along ��ith
sufficient operating volume so that the pump cycling frequency does not exceed the pump
manufacturers recommended limits. An undersized wetwell can significantly reduce the life of
the pumps by causing excessive pump cycling and raises the probability of the pumps
overheating and shutting down during critical periods. An oversized wetwell can create
stagnation problems and adds unnecessary cost The wetwell depth depends on the inlet sewer
elevation, pump operating volume, and minimum submergence requirement of the pumps.
The�vetwell floor dimensions depend on pump size and spacing, and operating volume if the
wet�arell depth is constrained.
Wetwells can be supplied in a variety of shapes but most are either circular or rectangular.
Circular wetwells typically consist of vertically installed pre-cast sectional pipe and are usually
more economic for small to mid-size pumps stations with deeper wetwells. Rectangular
wetwells are better suited to larger(>5,000 gpm) pump stations, are more space efficient with
multiple pumping arrangements, and are less prone to sediment settling than circular wetwells.
Smaller rectangular wetwells are typically pre-cast vaults or box culverts for deeper
installations. In areas with high groundwater, counter-buoyancy measures must be provided
and may include base lips and anti-floatation collars. Base lips require over-excavating for the
larger base footprint which may add considerably to the cost of installing the wetwell. Circular
wetwells are often installed��ith a caisson,and combination cutting shoe and tremie base in
deep installations or where high groundwater is present. In shallow installations the��etwell
may be brought to grade. In deeper installations, the wetwell height can be limited to the high
water level plus freeboard,and an access riser installed on top. This arrangement can reduce
construction cost and provides counter buoyancy with the weight of earth over the wetwell
roof. Circular wetwells are usually preferred for small to medium sized pump stations as the}'
tend to have a lower construction and maintenance costs, particularly with deeper wetwell
installations. Common practice is to line the interior and exterior of�vetwell to protect the
structure from corrosive material in the surrounding soil and pumped media.
In certain applications it may be preferable to house the pumping equipment in a separate room
adjacent to the wetwell in a dry pit/wet pit arrangement. This arrangement adds substantially
to the overall cost and is typically only preferred in large pump stations.
�� ��r �.F�t�/� '� /, * �( 700 Northeast Multnomah Street,Suite 900,Portland,Oreqon 97232-4189
�� � ��,..�1 �.s.,l"'ll��l 5d3r8'2-4100 • 503�`87�-4101 Fax � wwtiv.abam.com
For this application a circular wetti�ell installed �n�ith a caisson and tremie base is recommended
given the relatively small size of the pump station, required wet��ell depth, and presence of
high groundwater.
Piping and Valves
Discharge piping will connect the pumps to a pressure sewer forcemain line which in tum will
convey the pumped stormwater to the water quality pond. Each discharge line will have a
check valve and isolation valve installed in a below grade valve vault to prevent backflow into
the wetwell. The pump discharge lines will be manifolded to the forcemain line in the valve
vault. The forcemain will discharge to a manhole near the water quality pond, and then flo�v
via gravity sewer a short distance to the pond. The forcemain discharge invert elevation will be
set at a higher elevation than the maximum water level in the pond to prevent any possibilih�
that the pond could drain back through the pump station and flood the roadway. Forcemain
lines are typically sized to keep velocities high enough to prevent solids and sediment
precipitating out, yet low enough to prevent excessive friction headloss. Typical storm�vater
forcemain design flow velocity range is 2 to 10 feet per second (fps). A 24-inch pipe meets this
criteria for both phase II and III design flows.
Standby Pozver
As mentioned previously, a dedicated onsite standby po�n�er unit w-ill be required for the new
pump station. Standby power units are most commonly diesel fired although gas units are
often preferred where a natural gas or propane supply is available due to quieter and cleaner
operation. Onsite standby power units can be housed��ithin a dedicated building or provided
with a sound-attenuated outdoor enclosure. An outdoor enclosure is more cost effective than a
dedicated building and usually provides sufficient noise reduction for most locations. Noise
ordinances for both Renton and Tukwila suggest that an outdoor enclosure should be sufficient
for this pump station. However,the City of Renton expressed a desire to house the generator in
a building. A building will add substantial cost, and will require extending a water mainline
along Strander Boulevard to provide fire protection in accordance with the City of Tukti�ila
Building Code. As such, the generator building ti�ill be identified as a bid-altemate item.
CofTtrols and Instruments
The most common method of stormwater pump station control is based on fluid level in the
wetwell and cycles the pumps when the fluid level rises or falls to pre-set control levels. The
simplest level control system consists of inercury float switches installed at the pump set point
levels in the wetwell. Mercury floats are the most cost-effective form of level control but are
susceptible to fouling and have to be physically moved in order to change the level settings.
'� 13er erAI3AM ��Northeast Multnomah Street,Suite 900,Portland,Oregon 97232-4189
�� � 503/872-4100 • 503/872-4101 Fax • www.abam.com
Mercur}�floats are common for backup control in most municipal pump stations. Ultra-sonic
and pressure transducers are common for primary control in municipal pump stations. Both
types are accurate, reliable, and can be reset by the level controller at the touch of a button.
Additional controls and instruments include a motor control center(MCC) that allows both
manual and hands-off-automatic(HOA) pump operation with runtime counters and an alarm
system that signals alarm conditions to operators via telemetry and may have audible and
visible alarms at the pump station. Typical alarm settings include overflow,high water level,
low water level,overflo��, pump oil seal failure, and pump overheat.
The City of Renton's preferred primary level control instrument is ultra-sonic. Also,per the
City of Renton's standards, an in-line flow meter will be installed in the forcemain within the
pump station site. A magnetic flow meter is recommended due to its resistance to fouling and
suitability for wasteti�ater applications.
Controls Building
The MCC, telemetry gear, and miscellaneous controls can be housed within a controls building
or frame mounted outside in NEMA 4X weather proof enclosures. A controls building is more
expensive than an outdoor enclosure but provides better protection and is less visually ;
intrusive. Both Tukwila and Renton have expressed preference for a controls building.
However, as mentioned previously,a building will require extending the water mainline to
pro��ide fire protection.
Inlet Protection
Inlet protection in the form of a bar screen or trash rack may be provided where clogging and
ragging are particularly problematic. However, many municipalities have shied away from
providing inlet protection on smaller pump stations such as this given that their maintenance
can be substantially greater than that required to unclog pumps from time to time. As such,
inlet protection is not recommended for this application.
Equalization and Operating Storage
Equalization storage helps to reduce peak runoff to the pump station during high storm events
and can allow for a reduction in the pump sizes,with a corresponding reduction in construction
and operating costs. Upstream equalization storage can also provide pump operating volume
and thus allow the wetwell to be reduced in size. These cost savings have to be balanced
against the added overall cost of pro��iding equalization storage in the form of vaults or upsized
sewer lines. Adding equalization volume to reduce the pump size would not be cost effective
in this application. Preliminary sewer sizing shows that the upstream sewer bet�a�een the last
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catch basin in the sy�stem and pump station has sufficient capacit�� to provide enough operating
storage at the phase III design floti�. Upstream storage volume will need to be added during
phase III to provide sufficient operating��olume fur the greatly increased flo�vs.
Location and Site Layout
The pump station should be located such that the overall depth of the wetwell and distance
from the pump station to the discharge point is minimized. Limiting these factors reduces the
required pump size and hence cost to construct and operate the facility. The site should be
easily accessible to maintenance vehicles, and depending on the owner's preference,placed in a
location that minimizes visual impact. Structures within the site should be laid out so that they
can be easily accessed with lifting gear and other heavy maintenance equipment. Depending on
the owner's preference, security fencing and perimeter landscaping may also be necessary.
An initial location for the pump station was chosen at the south�vest corner of the BNSF right-
of-way and Strander Boulevard. At the meeting with the City of Renton, they stated their
preference to locate the pump station further to the west,between Strander Boulevard and the
future phase III loop road. This location improves access and enables continuous operation
during the phase III expansion. T'he facility would be located entirely within the City of
Tukwila and thus subject to Tukwila's building code and land use requirements, in addition to
the City of Renton's pump station standards.
Pre-Packaged Pum,p Stations
Pump stations can be custom designed and assembled onsite or may be supplied as a
prefabricated(or pre-packaged)unit supplied by a single vendor. Pre-packaged units are
available in a wide variety of configurations and sizes and are often more cost-effective for
small pump stations where the added design and construction costs would not justify a custom
build. Quality assurance and control can be enhanced with a pre-packaged installation as the
unit is factory tested after complete assembly. Choice is generally limited to pump stations w�ith
small (<30 HP) pumps. The main disadvantages of a pre-packaged unit are the limited range of
products and few choices in the larger(10 to 30 HP) size range. Most pre-packaged suppliers
will only provide one or two pump brands and associated equipment. It can often be difficult
to find a pre-packaged pump station that meets the strict requirements of a large municipality.
Pump stations with specific requirements such as unique pumping conditions and site
constraints should be custom designed. A custom design usually allows the facility to be better
tailored to a client's specific needs and preferences. Furthermore, the cost advantage of a pre-
packaged pump station diminishes as the size and complexity of the facility increases. Given
the size of the pump station for this application, and client's preferences, it is recommended that
this pump station be custom designed and tield assembled.
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Preliminar�� Pump Station Sizing
For the purposes of evaluation and comparison, four pump stations were considered for this
preliminary analysis and are described below.
• Pump Station A-This facility would be constructed by the City of Renton during phase
II to serve the phase II area only and would be retired following compleHon of phase III.
• Pump Station B-This facility would be constructed by the City of Tukwila during phase
III to serve the phase III area and would replace Pump Station A.
• Pump Station C-This facility would be constructed during phase II by the City of
Renton to serve the phase II area but will be designed so that it could be expanded to
serve the phase III area upon completion of that project. This pump station would be
identical to Pump Station A except that the controls building, generator, and power feed
would be sized to serve the full phase III area.
• Pump Station D-This facility would be constructed by the City of Tukwila during phase
III to expand Pump Station C so that the combined pump stations would serve the phase
III area. This pump station would be identical to Pump Station C except that it would
have higher capacity upstream operating volume storage and a separate generator and
controls building would not be required. The pump station would be hydraulically
connected to Pump Station C and the pumps controlled by the level controller in Pump
Station C.
Pump station design data are summarized on Table 4 below.
Table 5-Pum Station Desi n Data
Element Pump Station
A B C D
Desi Ca aci 3,270 m 9,380 m 3,270 m 6,110 m
Nominal Pum Size 40 HP 60 HP 40 HP 40 HP
Number of Pum s 2 3 2 2
Wetwell Inside Diameter 10 feet 12 feet 10 feet 10 feet
Wetwell De th 32 feet 34 feet 33 feet 35 feet
Required Upstream Storage 6,500 gallons
Volume 5,000 allons 7,340 allons 5,000 allons
StandbV Po�ver Generator 80 KW 175 KW 175 KW Not Required
�� Ber �ll ]1J1 ]1 V 1 �00 Northeast Multnomah Street,Suite 900,Portland,Oregon 97232-4189
�� � 503I872-4100 • 503l872-4101 Fax • www.abam.com
Estimated Cost of Construction
The estimated construction costs for pump stations A,B, C, and D are summarized on Table 6
below and detailed on Tables 7 through 10.
Table 5- Estimated Construction Cost Summary
Pum Station A-Phase II $820,325
Pum Station B -Phase III $1,234,750
Pum Station C-Phase II Initial $920,150
Pum Station D-Phase III Ex ansion $286,000
Pum Station C+D Total for Phase III $1,206,150
Conclusions and Recommendations
As the estimated cost to initially build a pump station that can be expanded from phase II to
phase III is about the same as a pump station that can serve phase II only, it clearly makes little
sense to construct Pump Station A only to decommission it when Pump Station B is brought
online. Although it may be possible to salvage some equipment from Pump Station A and keep
the wetwell operational to augment the operating volume of Pump Station B, the combined cost
�vould greatly exceed the other options. Thus Pump Station A is sho�vn for comparison only.
Although this memorandum does not provide a life-cycle cost analysis of each pump station it
is expected that Pump Station B may be cheaper to maintain and operate than Pump Stations
C+D over the life of the facilities given that there are fewer pumps, equipment, and sub-grade '
structures that need to be maintained. However, pump stations C +D have the lo�•est total
capital cost and pump station C has the lowest initial cost to the City of Renton, if pump station
A is discounted. Thus it is recommended that pump station C be constructed initially with
phase II.
Pump station system head-capacity curves along with wetwell control levels and buoyancy
calculations for pump station C are included as figure 1 and tables 11 thru 13b.
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Table 7-Estimated Cost of Construction-Pump Station A
Item Number Units $ Each Total$
40 HP Submersible Wastewater Pump 2 EA $50,000 $100,000
Discharge Piping,Valves, and Fittings 1 LS $50,000 $50,000
Wetwell (10' diameter, 32 feet deep) 1 EA $150,000 $150,000
Flow Meter 1 EA $15,000 $15,000
Upstream Sewer(185 LF 24"pipe-23 feet deep) 185 LF $300 $55,500
Forcemain (195 LF 12"Pipe) 195 LF $150 $29,250
60"Dia. SDMH (30' deep) 2 EA $15,000 $30,000
54"Dia. Discharge Manhole(5' deep) 1 EA $3,000 $3,000
80 KW Standby Generator(inc. pad, load bank, &ATS) 1 EA $100,000 $100,000
Controls Building 390 SF $200 $78,000
Motor Control Center, Instrumentation, &Misc. Electrical 1 LS $60,000 $60,000
Site Work(inc. radin , access road, and landsca in ) 1 LS $40,000 $40,000
Sub-Total $710,750
Contractor Mobilization/Demobilization $19,000
Permitting $8,000
QA/QC, Testin $8,000
Sub-Total Construction $745,750
Contin en (10%) $74,575
TOTAL PUMP STATION A $820,325
�� Ber �1� ].1)1 ]j�/1 �a0 Northeast Multnomah Street,Suite 900,Portland,Oregon 97232-4189
`� � 503/872-4100 • 503/872-4101 Fax • wwwabam.com
Table 8-Estimated Cost of Construction-Pump Station B
Item Number Units $ Each Total$
60 HP Submersible Wastewater Pump 3 EA $75,000 $225,000
Discharge Piping, Valves, and Fittings 1 LS $75,000 $75,000
Wetwell (12' diameter, 34 feet deep) 1 EA $200,000 $2�0,000
Flow Meter 1 EA $20,000 $20,000
Upstream Sewer(185 LF 48"pipe-23 feet deep) 185 LF $500 $92,500
Forcemain (195 LF 24"Pipe) 195 LF $200 $39,000
60"Dia. SDMH(30' deep) 2 EA $15,000 $30,000
54" Dia. Discharge Manhole(5' deep) 1 EA $3,000 $3,000
175 KW Standby Generator(inc. pad,load bank, &ATS) 1 EA $175,000 $175,000
Controls Building 390 SF $200 $78,000
Motor Control Center, Instrumentation, &Misc. Electrical 1 LS $90,000 $90,000
Site Work(inc. radin , access road, and landsca in ) 1 LS $40,000 $40,000
Sub-Total $1,067,500
Contractor Mobilization/Demobilization $31,000
Permitting $12,000
QA/QC, Testin $12,000
Sub-Total Construction $1,122,500 '
Contin en (10%) $112,250
TOTAL PUMP STATION B $1,234,750
'� Ber erABAM �00 Northeast Mu�momah Street,Suite 900,Portland,Oregon 97232-4189
�� � 503/872-4100 • 503/872-4101 Fax • www.abam.com
Table 9-Estimated Cost of Construction-Pump Station C
Item Number Units $Each Total$
40 HP Submersible Wastewater Pump 2 EA $50,000 $100,000
Discharge Piping, Valves, and Fittings 1 LS $50,000 $50,000
Wetwell (10' diameter, 32 feet deep) 1 EA $150,000 $150,000
Flow Meter 1 EA $20,000 $20,000
Upstream Sewer(185 LF 24"pipe-23 feet deep) 185 LF $300 $55,500
Forcemain (195 LF 24"Pipe) 195 LF $200 $39,000
60"Dia. SDMH(30' deep) 2 EA $15,000 $30,000
54" Dia. Discharge Manhole(5' deep) 1 EA $3,000 $3,000
175 KW Standby Generator(inc.pad,load bank, & ATS) 1 EA $175,000 $175,OQ0
Controls Building 390 SF $200 $78,000
Motor Control Center, Instrumentation, &Misc. Electrical 1 LS $60,000 $60,000
Site Work (inc. radin , access road, and landsca in ) 1 LS $40,000 $40,000
Sub-Total $800,500
Contractor Mobilization/Demobilization $20,000
Permitting $8,000
QA/QC, Testin $8,000
Sub-Total Construction $836,500
Contin en (10%) $83,650 �
TOTAL PUMP STATION C-PHASE II INITTAL $920,150
'� Ber erAI3AM �00 Northeast Muitnomah Street,Suite 900,Portland,Oregon 97232-4189
`� � 503/872-4100 � 503/872-4101 Fax • www.abam.com
Table 10-Pump Station D
Item Number Units $ Each Total$
40 HP Submersible Wastewater Pump 2 EA $50,000 $100,000
Discharge Piping, Valves, and Fittings 1 LS $10,000 $10,000
Wetwell (8' diameter, 34 feet deep) 1 EA $72,000 $72,000
Storage Vault(50 LF 60"pipe-23 feet deep) 50 LF $400 $20,000
Expand Motor Control Center&Re-Program PLC 1 LS $40,000 $40,000
Site Work (inc. radin and landsca in ) 1 LS $10,000 $10,000
Sub-Total $242,000
Contractor Mobilization/Demobilization $10,000
Permitting $4,000
QA/QC, Testin $4,000
Sub-Total Construction $260,000
Contin en (10%) $26,000
TOTAL PUMP STATTON D -PHASE III EXPANSION �286,000
�� �j��t�����/� � /( 700 Northeast Multnomah Street,Suite 900,Portland,Oregon 97232-4189
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- - _ - - — _ _-- - __ _- -- ---- ---- _ __ _
i
Figure 1. I
Strander Boulevard Extension Phase II
Stormwater Pump Station
I System-Head-Capacity Curves
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Volume Flow Rate,Q(gpm)
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Table 11-Wetwell Operating Volume
t=60/n Where: T=Time Between Pump Cycles (minutes)
V=tQi(Qo-
Q�)/Qo n=Pump Cycles Per Hour at Q
V=Required Wet Well Operating Volume
(gals)
d' _(3.142*D2/4)*7.48 Qo=Target Pump Discharge(gpm)
d�=V/d' Q�=ADWWF at Build-Out(gpm) �,
D =Wet Well Inside Diameter(feet) ''
d' =Wet Well Storage Volume (gallons/foot)
do=Pump Operating Range (feet)
Inputs: D= 10.0 feet
n= 10 cycles per hour
Q�= 1,640 gpm
Qo= 3,280 gpm
Outputs: T= 6 minutes
V= 4,920 gallons
d' = 587.55 gals/foot
d�= 8.37 feet
�� I�er��rAI3AM �00 Northeast Multnomah Street,Suite 900,Portland.Oregon 97232-4189
�/ 503!872-4?00 • 503/872-4101 Fax • www.abam.com
4.. '
Table 12-Wetwell Control Levels
Finished Grade Elevation at Wet
Well= 27.50 Datum
Clearance to Rim= 1 inches
Wet Well Rim Elevation= 27.58 Datum
Influent Sewer Invert/I'umps Off
Elevation= -1.00 Datum
Pump Submergence = 3.50 feet
Wetwell Bottom Elevation= -4.50 Datum
Total Wetwell Depth = 32.08 Feet
Invert Sewer Diameter= 24.00 inches
Lead Pump On Elevation/Invert
Crown= 1.00 Datum
Freeboard = 1.00 feet
Lag Pump On Elevation/High Level
Alarm= 2.00
Freeboard = 1.00 feet
Overflow Alarm = 3.00 feet
�� I3er erl �■ �l 11r1 �40 Northeast Multnomah Street,Suite 900,Portland,Oregon 97232-4189
�� � 503/872-4100 • 503/872-4101 Fax • www.abam.com
Table 13a-Wetwell Buoyancy-Standard Base
Assumed Water Level Elevation= 27.00 Datum
Wetwell Inside Diameter= 10.0 feet
Wet Well Wall Thickness= 11.0 inches
Wet Well Wall OD = 11.83 feet
Bottom Slab Width= 14.0 feet
Bottom Slab Breadth= 14.0 feet
Bottom Slab Thickness= 12.00 inches
Volume of Water Displaced= 3,716 cubic feet
Total Uplift Force = 231,862 lbf
Volume of Concrete = 1,205 cubic feet
Weight of Concrete= 180,714 lbf
Volume of Soil above Slab = 2,752 cubic feet
Weight of Soil above Slab = 302,749 lbs
Total Resistive Force= 483,463 lbs
Safety Factor= 2.09
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Table 13b—Wetwell Buoyancy—Standard Base
Assumed Water Level Elevation= 27.00 Datum
Wetwell Inside Diameter= 10.0 feet
Wet Well Wall Thickness= 11.0 inches
Wet Well Wall OD = 11.83 feet
Tremie Depth= 7.0 feet
cubic
Volume of Water Displaced= 4,290 feet
Total Uplift Force= 267,676 lbf
cubic
Volume of Concrete= 1,779 feet
Weight of Concrete= 266,805 lbf
Total Resistive Force= 266,805 lbs
Safety Factor= 1.00
Hydraulic Report
Strander Boulevard Extension Project
Cities of Renton and Tukwila, Washington
Appendix F - Geotechnical Report
Geotechnicai Report
Strander Boulevard Underpass Phasa 11
RentonlTukwila,Washington
November 22, 201 Q
Submitted To:
Mr.James S. Guarre, P.E., S.E.
BergerABAM!
33301 Ninth Avenue South, Suite 300
Federal Way,Washington 9800�2fi�
By:
� Shannon 8 Wiison, Inc.
404 N 34"'Strest, Suite 100
Seattle,Washington 98103
21-1-21 292-001
SHANNON F�WILSON.INC.
TABLE OF CONTENTS
Page
1.0 INTRODUCTION .................................................................................................................1
2.0 DESIGN GROLJNDWATER LEVEL AND DEWATERING ESTIMATI�N ....................2
2.1 Results of Groundwater Monitoring.........--•..............................................................Z
2.2 Dewatering Goa1 ........................................................................................................2
2.3 Potential ProblemslConcems.....................................................................................3
2.4 Fuhue Investigations................................•--...............................................................4
3.0 SEISMIC DESIGN C(3NSIDERATI�NS.............................................................................4
4.0 LTIDERPASS DESIGN AND CONSTRUCTION CONCEPT............................................5
4.l Alternative 1: Temporary Sheet Pile Shoring and Pile Foundations........................5
4.2 Alternative 2: Secant Pile Wall and Base Ground Improvement..............................6
S.Q AXIAL PILE CAPACII'Y AND PARAMTERS FOR PILE DESIGN................................7
6.0 LATERAL PRESSURES FOR TEMPOR.ARY WALLS DURING EXCAVATION .........8
7.0 LATERAL PRESSURES FOR PERMANENT WALLS DISIGN.......................................9
8.0 SHOO-FLY �R FILL EMBANICIvIENT............................................................................10
9.0 REFERENCES.....................................................................................................................11
TABLES
�
1 Recommended Parameters for Lateral Resistance Analysis Using LPILE
Cansidering Liquefadion
2 Recommended Parameters for Lateral Resistance Analysis Using LPILEP�Us
Without Cansidering Liquefaction
21-I-21292-0O1-Rl f-rev.dncx'wP,�� 21-1-21292-OQ 1
i
TABLE OF CUNTENTS (cont.) SMANNON F�V1IIl.SdN.INC.
FIGiJRES
1 Variation of Groundwater Levels Based on Field�ionitoring
2 Results of Liquefaction Analyses—Boring B-145 VWP (M= 6.63, PGA=0.65)
3 Results of Liquefaction Analyses, Boring B-107 (M=6.b3, PGA=Q.65)
4 Ulrimate Axial Capacity vf 24" Dia. Steel Pipe Pile Driven with Conical Tip—
Static Condition,West of BNSF Section Near B-105 VWP
5 Ultimate�ial Capacity of 24"Dia. Steel Pipe Pile Driven with Conical Tip—
Seismic Candition,West Side of BNSF—Near B-105 VWP
6 tiltimate Axial Capacity of 24" Dia. Steel Pipe Pile Driven with Conical Tip—No
Liquefaction—Near B-105 VWP
7 CJltimate Aacial Capacity of 24" Dia. Steel Pipe Pile Driven with Conical Tip—
Static Condition, East Side of BNSF Near B-107
8 L'ltimate Axial Capacity of 24" Dia. Steel Pipe Pile Driven with Conical Tip—
Seismic Condition, East Side of BNSF Near B-1Q7
9 Ultimate Aacial Capacity of 24" Dia. Steel Pipe Pile Driven with Conical Tip—Na
Liquefaction—Near B-107
10 Lateral Pressures During Canstruciion
11 Live Load Pressure Due to Cooper E80
i 2 Lateral Pressures— Static Post Constructian with Top Strut
13 Lateral Pressures—Static Post Construction without Top Strut
14 Lateral Pressures—Post Construction, Seismic
15 Lateral Pressures—Post Constzuction, Post Seismic
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GEOTECHNICAL REPORT
STRANDER BOULEVARD UNDERPASS PAASE II
RENTON/TUKWILA,WASHINGTON
1.0 INTRODUCTION
This report presents the results of our geotechnical studies for the conceptual design of the
proposed Strander Boulevazd Underpass Phase 1 project. We understand that Phase 1 of the
Strancier Baulevard Underpass project involves the design and construction of BNSF Railway
(BNSF) bridges within the BNSF right-of-way to accommodate the final Strander Boulevard
configuration and the design and construction of a shoofly for temporary track diversion, as
required. This project is expected to be managed by BNSF. The project also involves a
companion project,to be managed by city of Renton, for building a two-lane vehicular underpass
and pedestrian/bicycle tie-ins under the existing BNSF tracks in the northern half of the proposed
Strander Boulevard Undetpass. The underpass section is estimated arvund 500 feet long and
26 feet wide, excluding the pedestrian walk. The bottom of the base slab is estimated at
elevation-1.5 feet 6ased on the originaI conceptual plan. The bottom elevation may vary
depending on the selected design alternatives.
We reviewed the project information provided by BergerABAM and discussions during a
meeting on February 25,2Q10. We also reviewed a previous geotechnical report for conceptual
design of the Strander Boulevard(Shannon& Wilson, 2004). We took two additional sets of ',
groundwater data, on March 19 and aaother one on April 12, 201Q. In addidon, we analyzed the �'
monitored groundwater data co�lected since July 2003. We reviewed the subsurface conditions
and selected reports from previous studies for the Strander Boulevard Project site located in
Renton/Tukwila,Washington.
We performed the geotechnical services based on a subcansultant agreement between
BergerABAM and Shannon&Wilson, Inc. dated February 22, 2010. We made our evaluation
of selected tasks based on your Notice to Proceed of March 9, 2010. These tasks include:
I. Recommend goundwater design level
2. Review seismic design criteria
3. Evaluate underpass canstruction by means of sheet piling and dry excavation
4. Evaluate underpass construction by means of secant pile wall and bottom seal
5. Develop design recommendadons for permanent walls and base slab
6. Develop design recommendations for BNSF bridge foundations
7. Evaluate shoo-fly embankment for temporary relocation of railroads
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This report presents the results of our studies for the specific task geotechnical services for
Phase I of the Strander Boulevarci Underpass Project.
2.0 DESIGN GROUNDWATER LEVEL AND DEWATERING ESTIIVIATION
2.1 Resu�ts of Groundwater Monitori.ng
We performed the latest groundwater monitoring an March 19 and April 12, 2010, and analyzed
the monitoring results that wete collected since Ju1y 2003. An earlier memorandum (Shannon &
Wilson, 2009}documented the locations of manitoring wells and porewater pressure measwing
points, as well as data callected between July 2003 and May 2009. The monitoring results
showing the seasonal variation of groundwater levels since July 2Q(}3 are presented in Figure 1.
We identified two distinct groundwater le��els, one for the upper strata dominated by the fine-
grained sandy to clayey silt layers above around zero elevation,named as the perched water
table, and the other for the fine to medium sand layer and the lower strata, namely deep-seated
groundwater table. Based on the data,the perched water tabie fluctuates with seasons between
elevations 16 and 19 feet in the last three years and is presently at around 19 feet. The deep-
seated groundwater table in the area fluctuates between ele�-ations 12.5 and 14.5 feet in the last
three years and is presently around 13 feet.
For the purpose of this project for which the underpass is to be built in the upper strata,the
recommended groundwater levei for design is at elevation 19 feet for bath temporary and
pennanent works.
2.2 Dewatering Goal
We assume that the bottom of the base slab is at elevation-1.5 feet. The recommended design
groundwater elevation is 19 feet.
Assuming temporary watertight sheet piles will be installed around the excavation area,
dewatering goal in this area is tv drawdown the water table to about 7 feet at the well points
belaw the bottom of excavarion in order to maintain a practical working condition in the
excavation pit. To achieve this goal,well points inside the shored excavation would need to be
installed at below elevation -13.5 feet. With such an installatian and operation,the maximum
drawdown in the area is expected to be about 32.5 feet based on our initial assessment,
depending on whether a relatively impervious cut-aff layer is available at the toe level of sheet
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pile within a practical depth. The drawdown outside the shored area would be much reduced if
an impervious cut-offis present.
2.3 Potential Problems/Concerns
Based on Figure 3 in the Geotechnical Report for Conceptual Design of Strander Boulevard
(Shannon&Wilson,2004},which shows the subsurface profiles along the aligntnent of the
proposed undercrossing, the essendally fined grained sandy to clayey silt(He D) near the top is
underlain by a fine to medium sand (Ha D}that extends from a depth of about 30 to 7Q feet. On
the west end of the BNSF track,boring B-105 VWP encountered an 18-faot low pernieability
clayey silt(He D)immediately beneath the fine to medium sand layer. This low permeability
layer,however, was not present in boring B-107 on the east side of the BNSF tract. There is
uncertainty on how far the estuarine formation(He) extends eastward from boring B-105 VWP
and bvring B-103 fiu�ther west of B-105. The following two scenarios are outlined and further
investigations are needed to better understand the geology and hydrogeotogy of the azea:
1. If the He D layer(clayey silt)was absent between borings B-105 and B-i(}6 in Figure 3
{Sheets 2 and 3),then the Alluvium formation(Ha C and Ha D)would be in direct
contact with Cedaz River Alluvium-Gravel formation{Hag). The Hag formation consists
mainly of sandy gravel and gravelly sand with high hydraulic conductivity. This scenario
would present greater challenge in reaching dewatering goal, as large amount of water
would enter the dewatering zone from Hag formation. In this case,a large drawdown
would be expected outside of the construction area,due to connection of Hag aquifer
undemeath the piles. The railway may be affected due to settlement caused by large
groundwater drawdown in an extended area.
2. If the He layer was continuous eastward and comgetent,groundwater would be more
confined by shoring piles and underlying the He formation. In this case,the drawdown
goal can be reached by well points inside the shored area. A drawdown depth much
smaller than that in scenario 1 can be expected outside of the construction area. T'he
resulting settlement on the adjacent ground would be contrallable in this case.
Quantitative analyses are needed to estimate drawdown impacts outside construdion.
The Green River is apgroximately slightly over 1,000 feet away from the proposed underpass.
The Green River is under tidal influence and is connected to the de.ep-seated groundwater table
and the aquifer in the project area. Water level change due to tide, and associated pressure
change beneath the project,would need to be considered in the design of dewatering approaches.
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2.4 Future Iuvestigations
We recommend the following:
1. Geological exploration consisting of one boring of around I 10 feet deep in between
BNSF track and existing boring 8-106 to verify the continuity of the less pervious clayey
silt He layer.
2. A pumping test to evaluate aquifer hydraulic conductivity, storativity, and connecrions
between different geological units and Green River.
Shannon &Wilson, Inc. would be pleaserl to grepare a proposal for these further explorations if
required.
3.0 SEISMIC DESIGN CONSIDERATIONS
We understand that the railroad bridges will be designed in accordance with the 2007 Manual for
Railway Engineering as outlined in the American Railway engineering and Maintenance-of-Way '
Association(AREMA). We reviewed the code-based seismic ground motion in the project area
for three different levels of earthquakes that correspond to AREMA's grouping based on U.S.
Geological Survey 2(?02 Probabilistic Seismic Hazard Degradation. The results are as fallows:
Perfornaance Average' USGS Mean Pe�k R�ick
Ground Motion Criterii Limit Retur�o Period Retnrn Time Acccler�t�on
I:evel 5tate ears egra Coefficient
1 Serviceabili 50- 100 145 O.15S
2 Ultimate 200—500 475 0.326
3 Survivabilit 1,400—2 400 2,475 0.62b
USGS=U.S.Geological Survey
We understand that the bzidge designs will likely to be based on the maximum 500-year average '
return period that corresponds to Ground Motion Level 2. Based on the subsurface conditions '
encout�tered in the nearby borings,the site would be conservatively classified as AREMA Sail
type 4 with a conesgonding site factor of 2.0. The corresponding amplified peak ground
acceleration appropriate for design consideration is 0.65g.
We performed liquefaction analyses using liquefacdon evaluation soflware developed by
Shannon&Wilson, Ine. and subsurface borings near the BNSF tracks. Results of the analyses at
borings B-105 VWP and B-1071ocations are presented in Figures 2 and 3 for an earthquake with
magnitude 6.63 and an amplified peak ground acceleration of 0.65g.
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Liquefactions are generally considered limited to soft cohesive soils and loose to meditun dense
sand strata. The estimated depths of liquefaction are 70 and 80 feet,respectively, west and east
of the BNSF tracks. A substantial reduction of the shear strength will occur in the liquefied
layers and a reduction may also occur in other mazginally stable layers. These results are used as
a basis for the subsequent evaluation of the axial capacity and L-Pile pazameters recommended
for pile design. For an approximately 10(}-ycar retum earthquake, the depth of liquefaction is
similar to that for a 500-year retum earthquake. A greater depth of liquefaction is expected if an
approximately 2,500-year return eatthquake is considered for survivability situations.
4.0 UNDERPASS DESIGN AND CONSTRUCTI�N CUNCEPT
Two alternatives we.re cansidered for the design and cvnstruction of the Strander Boulevard
Underpass.
4.1 Alternative 1: Temporary Sheet Pile Shoring and Pile Foundations
The first alternative consists af using temporary excavationlshoring techniques, a tremie seal
with tialowns to complete the required excavation,driven steel pipe piles to support bridge
structures, and then constructing peimanent sidewalls. A tremie seal either by itself(gravity-
based}or tied down with tension piles will be necessary to resist uplift pressures. The vertical
loads fram the proposed bridge structures and substructure may be supported by both skin
friction and end bearing on the pipe piles. Driven piles should bear within the underlying non-
liquefiable, dense to very dense,alluvial soil layers encountered from about 1 I S to 14Q feet
below ground surface{bgs).
Steel sheet piles are being considered for this project because of their cost-effectiveness and
because they are commonly used in the Puget Sound area. Shee#piles are cost-effective
primarily because of the feasibility to recover the pile after construction;however, this would
require the construction of a permanent, concrete wall within the excavation. In addition, we
anticipate that either heavy-gauge steel sheet piles or mul6ple level bracing,deadman, or
tiebacks would be necessary to resist the large lateral pressures associated with the saturated
loose and soft soils encountered in the borings. To obtain the necessary toe support,the sheet
piles would likely need to penetrate through the soft/loose soils into the underlying fine to
medium-gained alluvium(HaD}. After sheet pile installation,the underpass could be excavated
in the wet; however, excavarion in the wet is more difficuit. If possible,the underpass area
should be dewatered and excavated in the dry. However, as discussed eazlier, dewatering at the
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project site could present a problem unless the essentially fine-grained clayey silt (He D)is
verified to be continuous for providing an effective cut-off of flow.
Driven steel pipe piles would be a suitable alternative for bridge and permanent sidewall
foundation support and tremie seal tiedowns at this site. The final foundation and tiedown
decision shauld be based on site conditions, economics and capacity needs. Based on the results
of our liquefaction analysis described previously, we recommend that the steel pipe piles be
driven into the underlying non-liquefiable soil. For steel pipe piles used as foundation support,
we recommend that they be driven closed-end to reduce the need for removal of the sails inside
the pipe pile and disposal of the spoils. However, for pipe piles being used as friction-only
members(tremie seal tiedowns)open-end piles can be considered.
Conventional cast-in-place concrete walls generally provide a high tevel of performance with
fow lateral wa11 movements. However, these walls are nat very flexible and cannot tolerate large
differential settlements. Consequently,this type of wall needs to be constructed on competent
foundation soils.
A concrete tremie seal would be installed aftex the temporary excavation shoring walls are in
place and the soil within the excavation is removed. The excavation could be completed in the
wet or dewatered and excavated in the dry. The area would be overexcavated beyond the design
pavement grade to allow the tremied concrete seal to cover the excavation bottom. If the
excavation is completed in the wet, the seal could be constructed by tremied concrete on the
excavation bottom. When the seal is in place and has gained sufficient strength,the inside of the
excavativn would be dewaterezi. The thickness of the concrete tremie seal should be deternuned
based on the uplift resistance needed. We recommend that a groundwater level at elevation
19 feet be considered in the design of the tremie seal. A tremie seal alone would probably be too
thick to be practical; therefore, it would likely be combined with riedowns (tension pile.$). Pipe
pile or other pile type riedowns could be driven to non-liquefiable soil to counteract the uplift
pressures under static or liquefiable s�il conditions.
4.2 Alternative 2: Secant Pite Wall and Base Ground Improvement
The second alternative consists of a ground impmved bottom seal in oonjuncrion with a secant
pile wall excavation support to form a"boat." The ground improvement zone could consist of
cement deep soil mixing(CDSM)or a jet grout bott�m seal. 1fie secant pile wall should be
founded within the gound improvement zone such that the underpass walls and bottom seal
would act as one underground structure. When the bottom seal is used in conjunction with a
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secant pile wall installed prior to excavation, the excavation can be carried out in the dry and no
dewatering in the construction area would be necessary. The wall should have the ability to
support the vertical loads from the praposed bridge struchues, as well as the lateral loads from
the soil and groundwater outside the excavation. The ground improvement bottom seal would
likely be about 30 to 35 feet thick in the deepest section of the underpass and would, therefore,
be"sitting"on top of potentially liquefiable soil. The required thickness of the seal is dependent
upon the cement- soil mix or soilcrete unit weight,permeability, and the hydrostatic pressure at
the battom of the soilcrete layer. After a design-leve� ground motion, the"boaY'would
experience liquefaction-induced ground settlement as discassed previously.
If the bridge structures cannot be designed to sustain the liquefaction-induced settlement, the
bridges foundations would need to be sepazate from the ground improvement bottom seal and the
sidewalls and would bear in the underlying non-liquefiable soi1. The bridge structure foundation
supports could be achieved separately on driven pipe piles. In this case,it would be possible to
use reinforced CDSM as the sidewalls and unreinforced CDSM as the bottom seal.
5.0 AXIAL PILE CAPACITY AND PARAMTERS FOR PILE DESIGN
We evaluated the axial pile capacity for a steel pipe pile of 24-inch-diameter driven closed-end
that may be used for supporting the B�ISF bridges under both static and seismic loading
conditions. Capacity of pipe piles will vary with their type, penetration, size, and the subsurface
conditions. In addirion to static soil conditions,the underpass would likely be exposed to a
temporary loss of skin friction during liquefaction and downdrag{negative skin friction)of
liquefiable soils immediately following a design seismic event.
We evaluate the axial pile capecity based on subsurface condirions encauntered in boring B-105
VWP west of the BNSF tracks and boring B-107 west of the tracks. We assumed a liquefaction
depth of about 70 feet at boring B-105 VWP and about 80 feet at boring B-107 3ocation. Results
of our evaluation are presented in Figures 4 through 9 for static and seismic conditions. Factors
of safety should be applied to these ultimate pile forces in accordance with AREMA. The
estimated downdrag force is on the order of 76 to 114 tons. This downdrag force would present I
as an additional axial load that will add to the applied load from the bridge after the soil liquefy
during a design seismic event. Downdrag forces due to soil liquefaction are post-earthquake
secondary forces. Seismic forces due to ground shaking are secondary forces that occur during
an earthquake. Seismic forces due to ground shaking are not additive to seismically induced
downdrag forces due to soil liyuefaction,
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Based on ow review of the 60 percent design plan prepared by Hanson, we understand that the
BNSF railroad bridge would consist of two abutments and one intermediate pier. Each of the
abutments would be supported by 78 piles ari�anged in 13 rows by 6 columns. The intermediate
pier would consist of 34 piles arranged in 13 rows by 3 columns. The pile spacings would be on
the order of 3 to 3.2 pile diameters. In our opinion,the driving of the piles at this spacing would
result in densification of the medium dense to dense sand layer encountered from 30 to 70 feet in
boring B-105 VWP, and from 23 to 103 feet in boring B-107, especially within the inner I 1 rows
of piles at the two abutments. Due to the densification of tl2is sand layer, we anticipate no
liquefaction would occur. Figures 6 and 9 are recommended for use to estimate the axial
capaeity of the piles within the inner 11 rows at each abutment. I3owndrag force along these
piles would be small and could be neglected. The exterior row and column piles wauld still be
subjected to liquefaction and downdrag, Figures S and 8.
We understand that GROUP or LPILEPLus programs would be used for the analysis of lateral
resistance of piles subjected to lateral loads. Tables 1 and 2 summarize the recommended L-Pile
parameters required in LPILE analysis that we developed based on the results of borings on both
the west side and the east side of the railroad tracks. These parameters include both static
conditions and seisrnic conditions considering potential jiquefaction and strength reduction
during the design earthquake of 500-year return period. Table 1 is recommended for the lateral
analysis of intermediate pier and Table 2 far the two ahutments.
6.0 LATERAL PRESSURES FOR TEMPORARY WALLS DURING EXCAVATION
We understand that sheet pile walls with two levels of tieback anchors are being considered for
dewatering control and support of excavation during the construction of the underpass. We
evaluated the lateral pressures for staric condition using the subsurface conditions represented
primarily by borings B-1 O5 VWP and B-1 Q6 MW and a design groundwater level at elevation
19 fe�et. The earth pressures were developed by assuming an active condition behind the sheet
pile wall and partial mobiliaation of passive resistance of soils for the embedded part behind the
wall and for the wall beneath the bottom of excavaiion.
Results of our evaluation on lateral pressures are summarized in Figure 10. Our
recommendations for accounting the surcharge load due to Cooper E80 aze shown in Figure 11.
Tieback anchors could be installed 20 to 40 degrees fram horizantal. Steeper tieback anchors
could be installed if right-of-way concerns are present. Na-load zvne should be considered from
ground surface to about elevation zero{about 30 feet below ground surface}. We anticipate that
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the anchors will be installed within the medium dense to dense sand layer below elevation zero,
which is about 45 feet thick. Within this layer,we recommend an ultimate bond capacity of 3.5 I
kips per square foot(ksfl for gravity�outing, and S.5 ksf for pressure grouting.
For a 2Q-foot embedment(about elevation-1 6 feet) of the sheet pile wa11,the estimated ultimate
vertical resistatice is about 24 kigs/ft of wall length. For a 30-foot embedment(about etevation
-26 feet},the estimated ultimate vertical resistance wauld be on the order of 34 kips/ft af wall
length.
7A LATERAL PRESSURES F(?R PERMANENT WALLS DISIGN ',
Convenrional cast-in-place concrete walls can be used as cut walls where temgorary cuts are
stable{by the nature of the soil and by nsing temporary shoring support)during wall
construction. This type of wall generally provides a high level of performance with small lateral
wall movements. However,thcse walls are not very flexible and they cannot tolerate large
differential settlements. Consequently, this type of wall needs to be constructed on competent
foundation soils. For this project, it would be necessary to faund the cast-in-place concrete walls
on deep foundations embedded in the strata below the potentially liquefiable zone.
Alternatively,the permanent wall could rest on a stnictural bottom slab,with the wali foundation
integrated with the bottom slab.
We evaluateci the lateral pressures for permanent walls under the static loading condition using
the subsurface conditions represented primarily by bori.ngs B-105 VWP and B-106 MW and a
design groundwater level at elevation 19 fcet. The earth pressures were developed by assuming
at rest condirion or active condition in the soils behind the permanent wall,depending on
whether there is a top strut or not. A paziial mobilizarion of passive resistance of soils was
generally assumed for the embedded part behind the wall and for the wa11 beneath the botkom of
excavation. Figures 12 and l3 present the lateral pressares for the conditions with top strut and
without top strut,respectively. The passive resistance can be mobilized at the base of the
excavation depends on whether the soil is improved or not.
As the permanent wall is likely to experisnce an earthquake, analyses were performed to
evaluate tbe pressures under two different post construction situations: (a)during seismic and
(b) post-seismic conditions. Based on the liquefaction analyses,the subsoils above the depths of
between 70 and 80 bgs may potenrially liquefy.
In the seismic condition, in addition to the static active earth pressure and the hydrostatic water
pressure, there is an earth pressure increment with its magnitude degending on the horizontal
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seismic coefficient. For the post-seismic conditions, we assumed that the subsoils behind the
retaining wall will liquefy,with its friction angle reduced to generally below 10 degrees. In
addition to the hydrostatic water pressure, an active earth pressure corresponding to the reduced
resistance and an excess porewater pressure would act to ihe retaining wall. Figures 14 and 15
present the fateral earth pressures for these two seismic conditions.
8.0 SHOO-FLY OR FILL EMBANKMENT
In order to temporarily relocate the BNSF railroads for the construction of the bridge-underpass
structure, new railroad fill embankments af approximately 2,OQ0 feet long will need to be built.
We understand that the embankments will be constructed to accommodate two railroad tracks at
the crest,range between 8 and 16 feet high, and have 2 Horizontal by 1 Vertical side slopes.
Using soil groperties estimated from the Standard Penetration Test N-values and published
correlations and laboratory consolidation test results, settlement and stability of the proposed
embankment were evaluated earlier(2004) and results were documented in Shannon&Wilson
(2004). That study indicate�that st$ged construction might be required to overcome stability
problem in areas underlain by soft and compressible foundation soils. The same study atso
recommende� a field monitoring program for evaluating the magnitude and rate of settlement, as
well as for stability control of embankment during canstruction,
SHANNON & WILSON, INC.
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Ghada Ellithy, Ph.D.,P.E.
Seniar Principal Engineer �
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9A REFERENCES
Shannon&Wilsan, Inc.,2004,Geotechnical report for conceptual design, Strander
Boulevard/SW 27`� Street irnprovements, Renton and Tukwila, Washington, Eebruary.
Shannon&Wilson, Inc.,2009,Memorandum on groundwater monitoring, Strander Boulevard
extension and UPRR relocation project, Renton and Tukwila, Washington, May.
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stt,atv�uoN a wi�soN,iNc.
r�s�ei
RE('OMMR.NbIL7)PAftAMBTF.RS FOR L.A7ERA1.Ri'SISTAIVCE AIVALYSIS U81NC LPILE���-CONSIDERING LIQIJ�ACTiON ,,
....._� � . .. �
9or�oahl I
Bebw� CAnfoe Frfctle�AaQk Uait Wcl�lt' Modnh�s of Sub�ndt
FkW Gro��d LPQ.E r[a Rnedo� 1 UNfm�te Side Frktba Ultl�au Esd Bei
E:ploratlo� SMrfaa 500 Cydki Sntlel
ket i 9atic C eL Statle L uef. St�tic L ueL Sntk
Aotinga 8-103 a�k1 0•7 Snft C S00 250 - - 100 38 - 0.02
-105VWP 7-10 SoRC S00 400 - - 100 38 - - �•� �sp �73 0 0 I
[0-16 Sad 36 3 1Q0 38 20 2
t6-30 SoR CM 2S0 150 ]00 3S 0.02
30-37 Ssnd 36 l6 120 58 60 21 770 300 GB000 Q
37-60 Send J6 36 120 S8 60 60 770 770 68,000 0
60-70 Smd - - J6 20 120 58 60 30 - '110 �00 69.000 0
70-l08 Stiff C w/o flee water 1.000 800 110 48 I SO l00 0.01 S00 600 10,000 fl 000
108-123 Ssnd 39 39 130 68 130 �30 3,000 3.000 240,000 240000
Boring B-107 0-7 Soft C 600 300 - - 110 48 - 0.01
7.t5 Sud 28 4 110 48 20 3 200 !00 U 0
IS-23 Soft C 250 200 100 38 0.02
43-65 Sud 35 35 l20 38 60 60 930 950 60 000 0
65-78 Saod 33 I2 120 38 60 IS 9S0 300� 60 000 0
78•t03 S�ad 33 33 120 58 60 60 930 950 60 000 60 OOQ ,
I03-I l7 Sand 38 38 130 68 l23 125 2.800 2,l00 200 000 200.000
117-133 Sliff Cl� w!o tSc wrter 4000 4 000 !30 b8 ! 00 1 S00 OAl I S00 1,300 33 000 33 000
133-152 Send 40 40 I3D 68 130 I70 3 S00 3 00 240 000 2�0 000
!vots:
'Groundwria kveb lwve bem me�swed moathly Gom Auq�ut 2003 f o Mnch 2010, Groundwua levek we�e merwed a�ekvotiom 16 ro I9 fM duroC 4te wemnet and f�Necy wota.repcchvely.for the uppc�treta cd I?.5 and 14.5 fat.respeet�vely
Cor the lowa aq�ufQ. As tM wet teawn contioues.grovndw�ta kvek w0l Gkety wmmue to ri�e.wit�p�nundw�ner bveh reufiing nnr�rou�d wrfnte.
AatDmio�tti�t a tfvae�di��c(miomim)cmtv-tosamar p�le spoene would be uxd a luenl efliciacy hctor o(ab�.ru10.7�s rceovuirnded due m pik group eQects.
If appbc�bk.enodificxio�u to the py curvv for abpmg puu�rond'Rion�.�hvuld be deterndnal in socord�nte wIM Ihe LPILE�'11997)manual.
GrowA wr6ce's ar q�proxinney davatioo 26 6ect.
cw'Sa1tf a One-dilf th!Oluinmm yrmc�al�am d�amce
pcf'ppwdt pet cu0ie foot
pri'poimd�per cubic iach
P�f'Dow�PQ aqa��foot
Staic-ftatic care.l.iquef'liquefied we.Cyetic'cyeNc badm�{coe
�i-i�no7nuixis�n+M'-l�n 21-I-71292-0OI
SHANNON 8 WILSOH,INC.
7�Bi.[2
RFCOMMBl�tD�PARAMS'CURS ROiI IJ►TQYAL tE81STANC6 ANALYSIS USQVG LPIL6�'��-W[iHOVE COM4IDPRING I.fQU6FACT10N
DeptY Horfz�W
Bdsw� CoieNoa FrWN�Aaek U�it Wei=N' Mod�Au ot Sr6�nde
Fldd Gro��d IpQ.E can iteacdou UMfm�lt$Mle FrieWa Ultlrb 6�d HnrY
E:plontioa S��La SsY Cye�d Spqd
1br 9ntle C �N. 9htle ad Shtic �L S4tit
rings B-]03 md 0-7 Soft CL S00 250 100 38 0.02
-I03 vWP 7-!0 Gift S00 400 — — 100 3R — — �•� 330 175 0 0
10-16 Saad 26 3 100 18 20 2
t6-]0 Soft C 250 l30 l OQ 38 0.02
30-70 Sud 38 J8 I25 63 120 110 l 00 8S0 66 000 68 000
70-108 Saff C w/a hee w�ttt 1 000 800 110 48 150 t00 0.01 800 b00 10 000 S 000
I08-123 S�od � 39 39 13D 68 I]0 130 3 000 3000 24(I.DO� 2+OOOD
rtng 8-107 D-7 SoR C1� 600 )00 — 110 <8 — — O.Ot
7-15 S�nd — — 28 4 110 48 20 3 — 200 100 0 0
F IS-T) SoR C 230 200 100 38 0.02
23-103 Sud 38 38 125 6) 120 t!0 1 t,000 60000 60000
103-t 17 Saod �8 38 1l0 68 IZS 125 2 B00 2.600 200,000 200,000
117-133 Soff C w/o 6to water 4 000 4 000 130 68 1 500 !S00 0.01 1 S00 1 l 5,000 33 000
f 33-152 Smd 40 �0 130 68 130 130 3 S00 3 S00 240 000 240 000
Nocn:
'Ctro�mdw�er kvds 6rvc bec ronuaed mom6iy!mm Auµw 2063 to Mamh 2010.Croundwem ie�eb wae mamu�ed a ekvetimu 16�019(en du'iej le�a o�mQ�od hR�erly wmta.rapa.aivdy.for Me uppa arx�nM 11.3 rod 14.5 6eai.�pectivaty.
for�he bws pude. Aa�hr Wa uuoe���,;��Qeoimdw�ta Ieva4 w�L Ukdy comtnue ta ri�a with poimdwuer kveb rod�in�nnr�oued wrfaee.
wsaome�tLx��Fnardimurer(minm�um)temaaotenta p8e�would be wed.�Wenl eMkxncy 6�acr of�6un 0.7 i eecomnknded due to D�L�W��� ,
if pptiabk,mo�6e�riom to the p-y nwa Ibr ilopi�jrowd mnditiors fAould be detmnoieA m Kco�ncY wiN the LMLE u'{t99'n mmu�L '.
Gawd wrSce it�t rPOrowmtdY dNNioa 181Eu.
c�—atrm at ox-half d�a owc'tnwa princial�vus dltF�'eace
D�—D��Pa�vbit foot
pp�KOW1�pQ NbIC OCA
�-jlC�d{�lq1���Ot
�pIC�7��Ctll.(JQItl(��ll[60d Cilf.��CYC�IC�O/l�tllj CYC .
:�-ta�Klaoi�utr.a..� 21-t.71292�401
Filename:J:�271�21292-001�21-1-21292-001 Groundwater Levels.dwg Date:11-22-2010 Login:Ir
25
20 -_.__� ____..--
_ _ ._._.____ ._._ ..._._ _ ...._.._._ . _....._.__. __.____ _, „`� ._,____.
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� _.__.__.._._.._. __.________._... _.____._
C
7 ;
� � � ��
� 5 -+-B-101 MW(EL-9.55') t8-304 MW(E1-13.66') -,k-B-104 VWP(EL+6.37')
p t8-105 MW(EL-124.56') -�-B-106 MW(EL�9.71') -�-B-106 VWP(EL-25.18')
T+
� -�8-108 MW(E1-17.01') -----B-108 VWP(ELi1.19') B-110 MW(EL-16.5')
� _. -... � + � ' �
W , � I i I �
i
�
�
�
0
0 10 20 30 40 50 60 70 80 90
Strander Boulevard Underpass
Time Lapsed from July 2003(Months) Phase II
Renton/Tukwila, Washington
VARIATION OF
GROUNDWATER LEVELS
� BASED ON FIELD MONITORING
� November 2010 21-1-21292-001
�
SHANNON& WILSON, �Nc. FIG. 1
Geoledxdcal and Environmsntal Conwllants
SBU_APGA Liquetaction_105 VWP.xtsm 11/21I2010 se
APPAQXIMATE Factor of Safety against liquefaction
SUBSURFACE 0.0 0.7 0.2 0.3 0.4 0.5 0.6 0.7 Q8 0.9 t.Q 7.1 1.2 1.3 1.4 >15
P�OFILE
��___ �
.V'!�y�a#i it�S�7fF � �' � i I ' i �
Sastdy tt�Cda3�ey � i � � � ( �
SiLT � �. i
��;. ~f � I ; �
�� � s� �
� i �
-� �-
�- - --I- __-� -- , -__ __ -- 20
� � g � I '
: �
30` i � I� � � '
; ,
� �
, !
- - � � i , ; � ♦ ;
,
; �
, , , , � �
i , ,
; �- `
_ :.-- - '. , __ ' ao
, , •
�_ _ ( � ; , :
, . I ' �
1 } � d
� � '
,
; � � � �
�
_ �
� � m
. � ; . U
�
f � � - --
t
,----�--_- -- --� - _}-- ;__ i _ — '-- 60 �j
i ; ; a
_ _.,. ' � � i � c
j . , �� �� i i �
70� ` �
� ' � � � ( � � j ; 3
i � o
� � , -
� i ; i m
• f . � f
.
w ' i
I ' L
'-� , �� � � ,- __ � __ -.__ �____ �-__, � 80 y
---- �-fi--- � — _-
: F � �
�� . j �
�;:� ; � �• � � � _ � _
. � � , i � f
� � � ♦ I �
I ; _ i � � _ ,00
� � ' � -- —
._ . _ _ .— +----�
�, � � s r sa, i ' �r 1 � I
;c� i - i ` i `
. , � i
� ,
.__ _ _---- ' ----}- �__ �_ .. _ 120
I
�
�
Bottom ot Boring
at 123A teet _ __ -- __ _ _ _ ____ ._-- -_ _. ;
■Youd et ai(20ot) •Idriss 8 Boulanger(2006} �Seed et aL(2003} �
NOTES Strander Boulevard Underpass
�. See main text tor references. Phase I I I
Renton/Tukwila, WA �
2. The iiquefaction resistance of a soil is based on its densiry and fines �
content. We used the results of the standard penetration testing to estimate RESULTS OF LIGIUEFACTION ANALYSES
the density,and the results of selected laboratory tests to estimate the fines BORING B-105 VWP
content.
3. The esfimated liquefaction induced settlement ranges from 4 to 1d inches at M = 6.63, PGA=0.65
the ground surface. The ground settlement is likely to be less than ihe November 2010 21-121292-Q01
estimated vatues and o�the orcier of 2 to 4 inches when liquefaction occu�s.
SNANNON & WILSON, INC. FIG. 2
C�e�;echnlca�and Envir�nrien�a'�Consu�tanis
SUB APGA Liquefaction B107 xlsm 11+21;201U se
APPROXIMATE Factor of Safety against Liquefaction
SUBSURFACE 0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 1 1 i 2 1.3 1.4 >1 5
PROFILE
0' i , 0
, $ry q ' ! I �r ; . � I � ;
Med.Dense to �
� Dense Fine to ; � ,� � � ;
14 ; � �j � � : I ;.
� , ' � �
' i I
�
._ - � ' _ _+___ ' . _ ; ; 20
22 I � ,
j . � �
- - i ', � i I . _
1
� �
j -- _ : ao
; _ I ; �
; � � � ! ! �
i �
�: . ; , I �
�, � c�
'- I r -- - - --- i 60 y
� �-- v
� : * �, � . �
, o
' � � � � � �° I o
,
� �' : 80 m
--- -- — - _ _ ._ .
__ _
a
0
. _ { t
__ ■ i � ♦ �
-- _._ � , ! � �
� � �
1�,. I
� 100- +- - �_ --+ _
j
� �
1. __ _ i ; I
F 1 i
�
_ � 720
--- -- — • -- . _—,_ , _ .
� i • ,
k
Bori�g Eztends to ----------.— -
_ —-- _—
_I
133A feet ■Youd et al.(2001) •idnss 8 Boulanger(2006) ♦Seed et ai(2003}
NOTES Strander Boulevard Underpass
t. 5ee main text for references. Phase II
2.The liquefaction resistance of a soil is based on its density and fines RentOn/Tukwila, WA
content. We used me results of the standard penetration testing to estimate RESULTS OF LIGIUEFACTION ANALYSES
the density,and the results of selected laboratory tests to estimate the fines BORING 8-107
content.
3. The estlmated liquefaction induced setUement ranges from 4 to t0 inches at M =6.63, PGA = 0.65
the ground surface. The ground settlement is likely to be less than the November 2010 21-121292-001
estimated values and on the order ot 2 to 4 inches when liquefaction occurs.
SHANNON & WILSON, 1NC. FIG. 3
Ge�'echr�,alard E�'nro�meotal�;,nsuCant�
11l2V2010-Cbse-EndPrpe B-?OSVWP SIaUc-xts
PROFILE
Based on Boring ULTIMATE RESISTANCE(tons)
B-105 VWP
0 50 700 150 200 250 300 350 400 450 500 550 600 650 700 750 800
0' r; �
� 4 � I ! , '
I � , Side-Static Condition
Very Soft to SoR Clayey i Tip-Static Condition
SILT � I
��•Total Ultimate Capacity
I
i �
30' � i � � I
ao _ ___.1_ -- --- ---- --�_
1 �
, � ;
Med.Dense to Dense °i � � ' 1
w f � i
Silty SAND "' , � �
2 , I
Q � r I �
�
a � / ' I �
� :� �
�o� � i � ,
a i i, �
Very Soft to Medium !
Stiff Clayey SILT gp - ;-� _ _
! I t i
�� Medium Dense to Oense ` � f �
SAND ! �� I i
94' , i i `
Very loose to Medium ; ; ' � i �
Oe�se Sandy SILT i � � ; ! � � i
� i I ! i
,f� i
108' ' `��
Very Dense Sandy ��'�� ��.�� '
GRAVEL � ! � �
� '
�
Boring Extends to 152A �pp
feet
NOTES:
t. The analyses were perfortned in accordance with the WSDOT Geotechnical Design Manual(GDM)and local expertence. The analyses are
based on a single pile and do not consider group action of closely spaced piles(2.5 diameters or less,center to center). Once final pile
group sizes and spacings are detertnined,the a�dal capacity of the pile group should be reevaluated.
2. Total pile capacity is a summation of its side and t�p resistance Total ultimate capacity shown on plots above should be d�vided by the
appropriate factor of safety.
3. Steel pipe piles driven closed-end w�th a flat bottom plate may not achieve
significant penetration into the glacial soil. If penetration is needed for load Strander Bloulevard Underpass
capacity requirements,a conical point is recommended to facilitate pile PhaSe II
penetration. Rentonlfukwila,Washington
Ultimate Axial Capacity of 24" Dia.Steel Pipe Pile
Drive�with Conical Tip-Static Condition
West of BNSF Section Near B-105 VWP
SHANNON &WILSON, INC.
Geoteci�n�cal ancl Frrvhonmental Consuitants FIG . 4
i 1��� •��-�i�.� e- � i� -V'�� ' S�.isn:.
ASSUMED SUBSURFACE
PROFILE
Based on 8orrng ULTIMATE RESISTANCE(tons)
B-105 VWP 0 50 100 150 200 250 300 350 400 450 500 550 600
0' ,� �
� . side-seismic conation
���. , T�p-Seismlc Cond�6on
Very Soft to Sot Clayey - �Total UNimate Capacrty
SILT
C
� � �
� � 1
30' "'
N
3
�
� .
�
40 - ---' '– – +
J . ._—rt_ ____ '.____
i i
� �
0 I �
Med.Dense to Dense �
Si1tySAND � N � i
a ' � '
w
C
a
� _
�o• w ; �
J i
a
Very SoR to sak Clayeyy j '
SIIT ' t i
80 — - – – –� '
t � I
I �
I
�� Medium Dense to Dense � i � { i i
SAND � : � I I �
94� � ( j :
Very Soft to Soh Clayey � ! �
to Sand SILT � ,
108' �
Very Dense Sandy �� �� �� ��
GRAVEL
Boring Extends to 152.0 120
feet
NOTES:
1 The analyses were performed in accordance with the WSDOT Geotechnical Design Manuai(GDM}and local expenence. The analyses
are based on a single pile and do not consider group action ot closely spaced piles(2.5 diameters or iess,center to center). Once final
ple group sizes and spacings are determined,the a�aal capacity of the pile group shouid be reevaluated.
2. Total pile capacity is a summation of its side and tip resistance. Total ultimate capacity shown on plots above shouid be divided by the
appropriate factor of satety.
3 Steel pipe piles driven closed-end with a flat botlom plate may not achieve
s�gnificant pe�etration into the glaciai sdt. If penetration is needed for load Strander Bloulevard Underpass
capacity requiraments,a conical point is recommended to facilitate pile Phase I I
penetration. RentonlTukwila,Washington
4 The estimated downdrag load in the zone ot liquefaction is 76 tons.This Ultimate Axial Capacity of 24" Die.Steel Pipe Pile I
downdrag load should be applied under post-seismic loading conditions.
Driven with Conical Tip-Seismic Condition
West Side of BNSF-Nea�B-105 VWP I
November 2010 21-1-21292-001
SHANNON &WILSON, INC. FIG . 5
Geetec:tuucai and Enwronmernai Consultants
77;21r2010-Close-Erx7Plpe 8�105VWP Nohouefaction.xlS
PROFILE
8ased on Boring ULTIMATE RESISTANCE(tons)
8-105 VWP
0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 75Q 800
0' �
� 1 i
I i Side-Static Condition �
Very Soft to Soft Clayey Tip-Static Condition '
SILT i ' _
� �Total Ultimate Capacity
� i
` � } �
30' i � i f � i
40 - + I I - --�--- -__ . _
I t i I � ,
Med.Dense to Dense � ', ( �I
Silty SAND " ' I 1 ! �
F , �� ' I
a � �, � �
W
O ;'
a i � � � (
�o�
� ' ' ' t� !
a I �I � I I
Very Soft to Medium �
Stiff Ciayey SILT 80 ---= _; ;' _ -- ---- � - -
' ' ; ` , i
�� Medium Dense to Dense � ;
SAND �; I
94' ' � �
� i �i i j
Very Loose to Medium � �Tt � i �
Dense Sandy SILT ' (� i i ` I
� I
108' ��+ *��� � '
�
Very Dense Sandy : , "r�r�j��
GRAVEI � ' I ! ' �
, �
Boring Extends to 152.0 120
feet
NOTES:
t. The analyses were pertormed m accordance with the WSDOT Geotechnical Design Manual(GDM)and local expenence. The analyses are
based on a single pile and do not consider group actlon of closely spaced piles(2.5 diameters or less,center to cerner). Once final pile
group sizes and spacings are determined,the a�dal capacity ot the pile group should be reevaluated.
2. Total pile capacity is a summation of its s�de and tip resistance. Total ult�mate capacity shown on plots above shoutd be divided by the
appropriate factor of safety.
3. Steel pipe piles driven Gosed-end with a flat bottom plate may not ach�eve
s�gnificant penetration into the glacial saf. If penetration is needed for load Strander BlOulevard Underpass
capacity requirements,a conical point is recommended to facilitate pile PhaSe I)
penetration. Renion/Tukwila.Washington
Ultimate Axial Capacity of 24" Dia.Steel Pipe Pile
Driven with Conical Tip-No Liquefaction
West of BNSF Section Near B-105 VWP
SHANNON & WILSON, INC.
Geolechrvcal and Enwrwrnental Cons�itarns FIG . s
t�;7t2�tG-Ciuse-Fr•tlr,pe g."_;,' � .
ASSUMED SUBSURFACE
PROFILE
Based on Bonng UITIMATE FlESISTANCE(tons)
8-107
0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 750 860
0' � �
Soft to Medium Stiff �, , ,
CiayeySlLT � �
7� � { Side-Static Conditlon
Very toose to loose '
Silty SAND j Tip-Stauc Condition
15` ; I ��Tota�Uibmate Capacity '
very Soft to Medium ; �
Siiff Clayey SILT i , , ,
23 i � �
� 1 '•. � ; � i ` '
{ ` �
i � il
�� � � ;
� j � � � i � i �
Medium Oense ta Dense 40 __--; --�--r----+ � --�� ----+—
SAND j � ; ' � ! i J
� i f {
m ' � ! � 1 � 1 I
� , �
w � � f I ! i i
S � � I � ? � �
W � �* I . � � i� � � � � I
58' O � ' ` ' ` � I
i I i I i
a i � I I
~ � � � � ' � � � � I
Medium DenSe SAND J ' � � t � � j
a # f � i I � � ! I
; � ; I � �
i � i�— i
� _ 1 �
�s• ' , i � ! I
80 . _ _ -�—_� �-– - ---}_ _
j ` � , ,
f � I � , � � I ; � �'
' I
Medium Dense to Dense i , I i ;
SAND , � � € I I �
1 ;` ( t !
: 1 � � ' i
l03 ' ,�'"'�+•..{..�„ ;
I , ' i ��
Dense to Very Dense i ; i � > � I
Sandy GRAVEL � j � i � '� ;
� i I i , , �` '
Boring continues below �2q
117A feet
NOTES:
1. The analyses were performed in accordance with the WSDOT Geotechnical Design Manual(GDM)and local ezperience. The analyses
are based on a single pile and do not consider group actron oi ciosely spaced pifes(2.5 diameters or less,center to center). Once f�nal piie
group sizes and spacings are detefmined,the axial capacity of tfie pile group should be reevaluated.
2. Total pile capacity is a summation of its side and tip resistance. Total ultimate capacity shown ort plots above should be divided by the
appropriate factor of safery.
3. Steel pipe piles driven closed-e�d with a flat bottom plate may not achieve
significant penetration into the glacial soil. If penetratian is needed for load Strander Boulevard Underpass
capacity requirements,a conical point is recommended to facililate pile Phase II
penetration. Renton/Tukwita,Washington
Ultimate Axial Capacity of 24" Dia.Steet Pipe Pile
Driven with Co�ical Tip-5tatic Conditio�
East Side of BNSF Near B-107
November 2010 21-1-21292-0a1
SHANNON &WILSON, lNC. FIG . 7
('�eotechrnu�and Enwronmental Consullants
11/22120'(i-CIoSE-F��i?ipe H-t0I Se�sm�r zlc
ASSUMED SUBSURFACE
PROFILE
Based on Bonng
8-10T ULTIMATE RESISTANCE(tons)
0 50 100 150 200 250 300 350 400 450 500 550 600
0' p
Soft to Medium Stiff `,,;'
Clayey SILT
� ' Side-Seism�c Condition
Very Loose to Loose , "`
Silty SAN D �
�. Tlp-Seismic Condit�on
15' I
Very Soft tD Medium ----Tolal Ullimate Capacih�
Stiff Clayey SILT
23'
c
o � I i j
w� � � ! �
'
Medium Dense to Dense 40 • � �
+ — --- i---__+- . __
SANO � i I
� �
F O i � i
S � I � � :
C �
a N ; i
o � { �
58' F I
W � j
J i �
Medium Dense SANO a ;
I ! � j
I �
�8' 60 - ' ; ;
--- ___- -- --- --- .
-�--
f i '
� � i
�, i �
Medium Dense to Dense �
SAND , ,
� , � ;
.
� � �
� ,� ,
io3' � '
���;
Dense to Very Dense � '
Sandy GRAVEI � ', � �
�`
1
Boring continues below 120
117.0 feet
NOTES:
i. The analyses were pertormed in accordance with the WSOOT Geotechnlcal Qesign Manuai(GDM)and local experience. The analyses
are based on a single pile and do rwt consider group action of closely spaced pilas(2.5 diameters or less,center to center). Once final
pile group sizes and spacings are determined,the a�dal capacity of the pile group should be reevaluated.
2. Tota)pile capacity is a summation of its sfde and tip resistance Total ultimate capacity shown on plots above should be divided by the
appropriate factor of safery.
3 Steel ppe piles driven closed•end with a tlat bottom plate may not achieve
significant penetration into the glacial soil. If penetration is needed ior load Strander Boulevard Underpass
capacity requirements,a conical point is recommended to tacilitate pile Phase II
penetration. Renton/Tukwila,Washington
4 The estimated downdrag load in the zone of liquetaction is 114 tons.This Ultimate Axial Cepacity of 24" Dia.Steel Pipe Pile
downdrag load shoutd be applied under post-seismic loading conditions.
Driven with Conical Tip-Seismic Condition
East Side oi BNSF Near B-107
November 2010 21-1-21292-001 '�i
SHANNON & WILSON, INC. F�G 8 I
Geetechn�cal and En�nronmental Consultants
i tl21!2010�CIose-Fnd Pipe_8-t07 no Ilque!aclion.xls
ASSUMED SUBSURFACE
PROFILE
Based on Boring ULTIMATE RESISTANCE(tons)
8-107
0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 750 800
0' �
Soh to Medium Stiff
Clayey SILT , i ' '
T .,.,.
Very loase to Loose j ---�—Side-Static Condibon
Siity SAND i Tip-Static Condd�on
15' � � � ���Total Ul6mate Capacdy
Very Soh to Medium ( �
Stiff Ciayey SILT � + `
23' I �
i � 1 i ,
i I �I � � i
, � � � �
,
� � �
Medium Dense to Dense 40 — ` �
SAND ' , , ! — ----� , ___
� I ;
m � ! � i
� i �
i �
2 ' , i f i
�
W � = f j
sa' a � �� � ! �
I �
� � '
� � � (
W i , ' � � ,
Medium Dense SAND a � � `
� �� �
� � , � � ( i
! � � ,, , i
�a� : ; l�_
ao T— —- t- , —
i i ♦ '
!
i � � i ♦� j '
i
Medium Dense to Oense { � I
SAND i � t I i
' � ♦
� ` , ,,
ios' �� �I��F.� � � '
� i i� '
Denseto Very Dense ; I I � � : �� '
Sandy GRAVEI I ` '
� i �'
Boring continues below 120
117.Ofeet
NOTES:
t. The analyses were performed in accordance with the WSDOT Geotechnica!Design Manual(GDMj and local euperience. The analyses
are based on a smgle pile and do not consider group action ot closely spaced piles(2.5 diameters or Iess,center to center). Once final pile
group sizes and spacings are determined,the a�tiel capacity of the pile group should be reevaluated.
2. Totaf pile capacity is a summation of its side and tip resistance. Total ultimate capacity shown on plots above should be d�vided by the
apprapriate factor of safety
3. Steel pipe piles driven closed-erxi with a flat bottom plate may not achieve
significant penetration into the glacial sal. If penetration is needed tor load Strander Boulevard Underpass
capacity requirements,a conical point is recommended to facilitate pile Phase II
penetration. Renton/Tukwila,Washington
Ultimate Axial Capacity of 24" Dia.Steel Pipe Pile
Driven with Conical Tip-No Liquefaction
East Side of BNSF Near B-107
November 2010 21-1-21292-001
SHANNON & WILSON, INC. FIG . 9
Geo�echrncal and EnhrormierAal Consultants
Ground Surface Elevation Varies Temporary Wall �Ground Surface Elevation Varies
i/i ��� 1 1 i// i�� �
43 or a a 175
He
-28H 20,
EI.+19
EI. +19 � �- EI. +19 1 � EI. +19
- 1 �- 1 - � -
14H - h
1 ' '
1 I i
�
22 v W H I � 53
10' He b b
Qr - See Note 12 Bottom of Excavation ; Excavation
43a+22b -� ---
+ � + See Note 9 - �(Varies) + �(Varies)
- 100 psf 1 1 1 '
Bottom of hw i � � .\�i\� hW Bottom of
He Layer �240 psf y ' � 79(d-c) = 1 � He Layer
Bottom � � 1.5 � - 175a+53b
of He ;
Layer (105a+42.6b)0.31 � � 42.6(d-c�.62 � (105a+42.6b)4.62
Bottom � 1.5 _ - 1.5
of He '
12H- I Layer �
18 ' d + he 142
Ha c c -
- 1 1_ _I 1 �I _ �_
� � � � � h '42.6(d-c)4.62+243c �,� � "�w h B � �Y�y hyr � (105a+42.6b)4.62+243c
Q � - 105a+42.6b 0.31+18c w w � �' 1.5 � -
' 1.5
o Earth Pressure Earth Pressure Construction Water Pressure Earth Pressure for Water Water Pressure Passive Resistance of
� (Multiple Brace) (Cantilever or Single Brace) Surcharge Pressure Unimproved Soil Pressure Unimproved Soil
N - -- - Active Pressures - -- - - � - - - --Passive Pressures - - -
�
�
0
NOTES LEGEND
� 1. The lateral pressures shown are applicable dunng construction on walls with two or more levels of 10. Based on groundwater conditions(saturated soil)observed in the soil borings, Y W = Unit Weight of Water.pounds per cubic foot(pc�=62.4 pcf
o bracing or cantileverlsingle braced walls. Both conditions should be checked for wall design. groundwater outside the excavation is assumed to be at elevation 19 feet. Groundwater
� measurements are on�oing. The groundwater levels may change due to seasonal hw = Height of Water Outside Excavation,Feet
�, 2. These pressures are applicable where no top strut is installed resulting in active earth pressures. fluctuations.
� Active earth pressures shown are applicable when the wall moves more than 0.001 x h. h6 = Height of Water Below Inside of Excavation, Feet
o, 11. Both the muRiple brace and the cantilever/single brace active eaRh pressure should be
; 3. The lateral pressure values above assume a horizontal ground surface. analyzed. The active pressure should be the sum of the appropriate earth pressure, h = Depth of Excavation
� water pressure,surcharge pressure,and applicable train traffic impact loading pressures.
° 4. The weighted average of the actual earth pressures(above the bottom of He layer)is presented on H _ Distance from the Top of the Wall to Bottom of He Layer or
� this figure. 12. The passive resistance down to 2 feet below bottom of excavation should be ignored to Point of Zero Deflection whichever is Deeper,Feet
a (typical). The unimproved soil passive pressure beneath the excavation should be used.
�0 5. Pressure expressions are in pounds per square foot(ps�. The passive pressures outside the excavation are for unimproved soil. � = Groundwater Level
a� —
R
J 6. A factor of safety of 1.5 is inGuded in the passive eaRh 13. The recommended pressure diagrams are based on a continuous wall system.If soldier Strander Boulevard Underpass
o pressures presented above. piles with lagging are used.apply active pressures over the width of the soldier piles Phase II
N below the bottom of the excavation and apply passive resistance over twice the width of
N 7. The required depth of wall embedment should also satisfy vertical loading considerations. the piles or the spacing of the piles.whichever is smaller. Wall embedment should Renton/Tukwila, Washington
consider kickout resistance. Embedment should be determined by satisiying horizontal
� 8. The construction surcharge pressure shown is based on a 600 psf surcharge acting over a static equilibrium about the bottom of the pilelshaft. Use 80 percent of the above LATERAL PRESSURES
o semi-infinite area adjacent to the excavation. Other surcharge pressures should be added as pressures for computing moment in piles/shaft. For temporary lagging design.use 70
N required; see Figure 9 for additional details. Lateral pressures due to impact loads from train traffic percent of the above design pressures. DURING CONSTRUCTION
N should also be considered.
`% 14. In addition to the lateral pressures shown above,uplift pressures due to groundwater November 2010 21-1-21292-001
N 9. Groundwater levels inside the excavation should be maintained at least 2 feet and 5 feet below should be taken into account for bottom seal/tremie seal design.
� bottom of excavation for light and heavy weight construction equipment,respectively. SHANNON& WILSON, INC.
� Gededmical and Erni►arnental Consultarns F I G. 7 0
u.
Ground Surface Elevation Varies Wall Ground Surface Elevation Varies
i/i i\� � i�i i��
, StfUt
Hf '
60 0� a a 175
"e I �
—33H i
� EI. +19 � I � EI.+19 1 � EI.+19
EI.+19 - — � � � — —
', ' ' ' �
' h I '
�
� i
16H —. H
I
�'—^' �W 53
27 I �I
He b Bottom of ' I' b
' Excavation ' ,�
- See Note 11 (Varies) + �Excavation
�r 60a+27b � + See Note 9 — � , i r (Varies)
' 1
Bottom of hW � — � 1 \�i\� — hw � Bottom of ' Bottom of
Bottom He Layer� ', I , -�- 79 5c � ' He Layer �� _ �75a+53b�He Layer
of He � � i
Layer (105a+42.6b)0.47 I ' , 42.6{d-c�4.62 � I (105a+42.6b)4.62
` Bottom�of �� � 1.5 � 1.5
�i He Layer � I �
14H— i ha 142
d + c
25 �I Ha c j
� t r t � f
3 -- ,
a (105a+42.6b)0.47 _ ' � 42.6(d-c)4.62+243c ' _ ' � (105a+42.6b�.62+243c _
��— f ywhW-- 1.5 I` �I 'fyv h a,f y YWh6 f �y,„hW — 1.5
� +27C '
N Earth Pressure Earth Pressure Water Pressure Earth Pressure for Water Water Water Pressure Passive Resistance of
N (Multiple Brace) (Cantilever or Single Brace) Unimproved Soil Pressure Pressure Unimproved Soil
o I� - - - At-Rest Pressures - - � �li - — Passive Pressures
3 NOTES
�
° 1. The lateral pressures shown are applicable to static conditions for post-construction walls 10. Based on groundwater conditions(saturated soil)observed in the soil borings,
i with two or more levels of bracing or cantilver/single braced walls.Both conditions should groundwater levels outside the excavation are assumed to be at elevation 19
� be checked for wall design. feet. Groundvuater measurements are on-going. The groundwater levels LEGEND
c°� may change due to seasonal fluctuations.
� 2. These pressures are applicable where is a top strut is installed resulting in at-rest earth Cement Deep Soil Mixing
„ pressures. At-rest earth pressures shown are applicable when the wall moves less than 11. The passive resistance down to 2 feet below bottom of excavation should be CDSM = (assumed ground improvement method
N 0.�01 x h. ignored(typical). Either the unimproved soil or improved soil(CDSM for this figure)
� assumed)passive pressure beneath the excavation should be used. The
� 3. The lateral values above assume a horizontal ground surface. passive pressures outside the exca�ation are for unimproved soil. v W _ Unit Weight of Water,pounds per cubic
� foot(pc�=62.4 pcf
�
"' 4. The weighted average of the actual earth pressures(above the bottom of the He layer)is 12. Both the multiple brace and the cantilevedsingle brace at-rest earth pressure
apresented on this figure. should be analyzed. The at-rest pressure should be the sum of the hw = Height of Water Outside Excavation,Feet
� appropriate earth pressure,water pressure, and applicable surcharge and Strander Boulevard Underpass
o5. Pressure expressions are in pounds per square foot(psfl. train impact loading pressures. he _ Height of Water Below Inside of PhaS2 II
N Excavation,Feet Renton/Tukwila, Washington
N 6. The required depth of wall embedment should also satisfy�ertical loading considerations. 13. The recommended pressure diagrams are based on a continuous wall i
� system. Wall embedment should consider kickout resistance.Embedment h = Depth of Excavation LATE�I�►L PRESSURES
7. Surcharge pressures should be added as required:see Figure 9 for additional details. should be detertnined by satisfying horizontal static equilibrium about the
� Lateral pressures due to impact loads from train traffic should also be considered. bottom of the pilelshafts. Use 80 percent of the above pressures for Distance from the Top of the Wall to STATIC POST CONSTRUCTION !,
o computing moment in piles/shafts. H = Bottom of He Layer or to Point of Zero WITH TOP STRUT '
N 8. A factor or safety of 1.5 is included in the passive earth pressures presented abo�e. Deflection whichever is Deeper,Feet !i
N 14. In addition to the lateral pressures shown above, uplift pressures due to �
9. Groundwater levels inside excavation should be maintained at the bottom of the groundwater should be taken into account for bottom seaUtremie seal design. � = Groundwater Level November 2010 21-1-21292-001 i
' proposed underpass final grade. SHANNON& WILSON, INC. .1�l �,
�; Geotechnical and Environmenlal Conwttants F I G. 1 L �
i� �
Ground Surface Elevation Varies Wall
Ground Surface Elevation Varies
i/� �\� 1 � i/i i\�
Hf ,
43 or a a 175
He i
' I
� EI.+19 ; , � E1.+19 � � EI.+19
E1.+19- - � -
h
H
22 "N '' 'H!I 53
- � —
He b Bottom of i b
Excavation , '
�See Note 11 (Varies) , �I ' Excavation
60a+22b -
"� See Note 9 -- �, , + �(Varies)
i Bottom of '
Bottom of hW Bottom of � - � �\��\ _ I� hW He Layer ' Bottom of
He layer He Layer � - 79 d-c `, He Layer
� � 1 1.5 � � i __ 175a+53b
(105a+42.6b)0.47 - '�— - � 42.6(d-c)4.62 -
— 1.5 �, � (105a+42.6b?4.62
i
1.5
'i I
d + hB '' � 142
18 , Ha c I c
, ' �, i
� , �
' � I
� _1_ _�_ _I 1 1 �
a (105a++28.6b)0.47 � r ,�whW yll � 42.6(d-c?4.62+243c � , �W h6� -� yWhB f f ywhW y{ --- � (105a+42.6b)4.62+243c y
0 1.5 1.5
o Earth Pressure Water Pressure Earth Pressure for Water Water Water Pressure Passive Resistance of
� (Cantilever or Single Brace) Unimproved Soil Pressure Pressure Unimproved Soil
N
� �-- - - - Active Pressures ' -- -- Passive Pressures ---- - - --
�
o NOTES
�, 1. The lateral pressures shown are applicable to static conditions 10. Based on groundwater conditions(saturated soil)observed in
-o for post-construction to cantileverlsingle braced walls. the soil borings,groundwater levels outside the excavation are
o assumed to be at elevation 19 feet. Groundwater measurements
; 2. These pressures are applicable where no top strut is installed are on-going. The groundwater levels may change due to
� resulting in acti�e earth pressures. Acti�e earth pressures seasonal fluctuations.
� shown are applicable when the wall moves more than O.OQ1 x h. LEGEND
�, 11. The passive resistance down to 2 feet below bottom of
a 3. The lateral values above assume a horizontal ground surface. excavation should be ignored(typicalj. Either the unimproved Cement Deep Soil Mixing
; soil or improved soil(CDSM assumed)passive pressure beneath CDSM = (assumed ground improvement method
� 4. The weighted average of the actual earth pressures(above the the excavation should be used. The passive pressures outside for this figure)
a bottom of the He layer)is presented on this figure. the excavation are for unimproved soil.
r � _ Unit Weight of Water,pounds per cubic
w 5. Pressure expressions are in pounds per square foot(ps�. 12. The active pressure should be the sum of the earth pressure, w foot(pc�=62.4 pcf
�° water pressure,and applicable surcharge and train impact
J 6. The required depth of wall embedment should also satisiy loading pressures. hw = Height of Water Outside Excavation,Feet Strander Boulevard Underpass
vertical loading considerations. PhaS2 II
N13. The recommended pressure diagrams are based on a hB _ Height of Water Below Inside of Renton/Tukwila, Washin tOfi
N 7. Surcharge pressures should be added as required;see Figure 9 continuous wall system. Wall embedment should consider Excavation,Feet g
N for additional details. Lateral pressures due to impact loads from kickout resistance.Embedment should be determined by
train traffic should also be considered. satisfying horizontal static equilibrium about the bottom of the h = Depth of Excavation LATERAL PRESSURES
� pile/shafts. Use 80 percent of the above pressures for STATIC POST CONSTRUCTION
g 8. A factor or safety of 1.5 is inGuded in the passive earth computing moment in piles/shafts. Distance from the Top of the Wall to
m pressures presented above. H = Bottom of He Layer or to Point of Zero WITHOUT TOP STRUT
� 14. In addition to the lateral pressures shown above, uplift pressures Deflection whichever is Deeper,Feet
N 9. Groundwater levels inside excavation should be maintained at due to groundwater should be taken into account for bottom November 2010 21-1-21292-001
N the bottom of the proposed underpass final grade. seal/tremie seal design. � = Groundwater Level
SHANNON& WILSON, INC.
= GeotechnicalandEnvironmenlalConsuttants FIG. �3
i�
0.8 F(H) Ground Surface Elevation Varies Wall Ground Surface Elevation Varies
i/i i\` iii i\` 1
He ,
43 �� a ' d
Ha ' '
EI.+19 � EI. +19 �
� E1.+19
— j j — } Xd, —
j
He h
or b '
Ha ' i H
�
22 �w 1 - I �w
1 —I
Bottom of
�, + Excavation
100 yr F=14 —See Note 10 (Varies) ;I 100 yr X=132 Y=58
475 yr F=39 60a+22b -- He c See Note 8 — 'I + 475 yr X=121 Y=53
2475 yr F=110 ry� � � d2 2475 yr X=110 Y=48
Bottom of ——� •\�i\� —
He Layer � � , I, �
_ 1 �
(105a+42.6b)0.47 --- � �1
Bottom of ' '
He Layer ' + h6
18 e
Ha d ;
o 1' lI
3 � � 1 I 1 �
¢ — —
---! (105a+42.6b)0.47 � _ � �Whw _ ' ; h ' '
� +18c � Sg(e+2) .� � ;w e i— -- �/.�he — ,�-•fWhW� ,f Xd�+Yd2 �
0 0.2F(H)
N Earth Pressure Earth Pressure for Water Water Water Pressure Passive Resistance of
N (Cantilever or Single Brace) Unimproved Soil Pressure Pressure Unimproved Soil
� Seismic Increment Hydrostatic
� Water Pressure
�
0
(A) (B) (C)
3
�
o NOTES
U
� 1. The lateral pressures shown are applicable to seismic conditions for 9. Based on groundwater conditions�saturated soil)observed in the soil borings, LEGEND
o post-construction walls. groundwater levels outside the excavation are assumed to be at elevation 19 feet.
� Groundwater measurements are on�oing. The groundwater levels may change due Cement Deep Soil Mixing
a 2. The lateral values above assume a horizontal ground surface. to seasonal fluctuations. CDSM = (assumed ground improvement method
� for this figure)
N 3. The weighted average of the actual earth pressures(above the 14. The passive resistance down to 2 feet below bottom of excavation should be ignored
� bottom of the He layer)is presented on this figure. (typicaq. Either the unimproved soil or improved soil(CDSM assumed)passive Layers b and c are liquefied soil
L pressure beneath the excavation should be used. The passive pressures outside the
w4. Pressure expressions are in pounds per square foot(ps�. excavation are for unimproved soil. y W _ Unit Weight of Water,pounds per cubic
� foot(pc�=62.4 pcf
� 5. The required depth of wall embedment should also satisiy vertical 11. The recommended pressure diagrams are based on a continuous wall system. Wali Strander Boulevard Under 8SS
� loading considerations. embedment should consider kickout resistance.Embedment should be determined by hw = Height of Water Outside Excavation,Feet P
g satisfying horizontal static equilibrium about the bottom of the pilelshafts. Use 80 Phase II
rn 6. Surcharge pressures considering dynamic effects should be added percent of the above pressures for computing moment in pileslshafts. h6 _ Height of Water Below Inside of Renton/Tukwila, Washington
� as required:see Figure 9 for additional details. Lateral pressures due Excavation, Feet
� to impact loads from train traffic should also be considered. 12. In addition to the lateral pressures shown above,uplift pressures due to groundwater LATERAL PRESSURES
� should be taken into account for bottom sealltremie seal design. h - Depth of Excavation
� 7. Passive earth pressures provided are ultimate values. An POST CONSTRUCTION
� appropriate factor of safety is recommended to be applied to these 13. For 105-year EQ(Servicability) K H=0.16 Distance from the Top of the Wall to SEISMIC
°' values if used for design. For 475-year EQ(Ultimate) K H=0.33. H = Bottom of He Layer or to Point of Zero
N For 2475-year EQ(Survivability) K H=0.50(max). Deflection whichever is Deeper,Feet
8. Groundwater levels inside excavation should be maintained at the November 2010 21-1-21292-001
� bottom of the proposed underpass final grade. 14. Passive rexixtance is based on 1-inch of wall movement. � = Groundwater Level SHANNON 8� WILSON, INC.
� Geotedmical and Environrt�enlal Consultants F I G. 14
ii
Ground Surface Elevation Varies Wall Ground Surface Elevation Varies
i/i i\� � i/i i��
He , �
43 '
°f a I � d� a
Ha �
� ' I
I I, i
- 99a - EI. +19 � � � 99a �
E1.+19 � � ! � EI+1g _1 1
8a - 1 � ' } � 132d, 4
He I h I�, ,
or b
Ha H �
8a+4b - �
99a+43b ';w 1 I � 99a+43b
33a+14b 47a+20b - 1 ' , 33a+14b
i b
�Bottom of
Bottom of �� Bottom of
Excavation ' - See Note 10 Excavation , �
(Varies) + He c See Note 8 � (Varies) + ' Excavation
1_
i (Varies)
\�i\� h'^� _ � �\��� _ hW dz //�//,
1 �
47a+20b+20c — __ � 1 '
1 . 1
�----� (105a+42.6b)0.47 - � � i ',I . 1 I y
33a+14b+14c(h-a-b) � Bottom of � i ' 33a+14b+14c(h-a-b)
He Layer I + hB
18 e ;
- Ha d c
0
¢ � � � � � �—
(105a+42.6b)0.47 I y 58 e+2 �� he t � � ,-
� +18c ,- � �YWh++y � ) 'i- - w � y«I� ',�- �132di+ 58dz -
0
N Net Excess Modified Earth Pressure Hydrostatic Earth Pressure for Water Water Passive Resistance of Net Excess
N
N Porewater (Partial Liquefaction in Water Unimproved Soil Pressure Pressure Unimproved Soil Porewater
� Pressure Soil Layers b and c) Pressure Pressure
a�
�
� (A1 (g1 (�)
3
�
o NOTES
U
� 1. The lateral pressures shown are applicable to seismic conditions for 9. Based on groundwater conditions(saturated soil)observed in the soil LEGEND
o post-construction walls. borings,groundwater levels outside the excavation are assumed to be at
" elevation 19 feet. Groundwater measurements are on-going. The Cement Deep Soil Mixing
� 2. The lateral values above assume a horizontal ground surface. groundwater le�els may change due to seasonal fluctuations. CDSM = (assumed ground improvement method
�, for this figure)
�, 3. The weighted average of the actual eaRh pressures(above the 10. The passive resistance down to 2 feet below bottom of excavation should be
° bottom of the He layer)is presented on this figure. ignored(typical). Either the unimproved soil or impro�ed soil(CDSM Layers b and c are liquefied soil
r assumed)passive pressure beneath the excavation should be used. The
W4. Pressure expressions are in pounds per square foot(ps�. passive pressures outside the excavation are for unimproved soil. v W _ Unit Weight of Water,pounds per cubic
� foot(pc�=62.4 pcf
� 5. The required depth of wall embedment should also satisfy vertical 11. The recommended pressure diagrams are based on a continuous wall
� loading considerations. system. Wall embedment should consider kickout resistance.Embedment hw = Height of Water Outside Excavation,Feet Strander Boulevard Underpass
g should be determined by satisfying horizontal static equilibrium about the Phase II
N 6. Surcharge pressures considering dynamic effects should be added bottom of the pile/shafts. Use 80 percent of the above pressures for h _ Height of Water Below Inside of Renton/Tukwila, Washington
� as required;see Figure 9 for additional details. Lateral pressures due computing moment in piles/shafts. B Excavation,Feet
� to impact loads from train traffic should also be considered.
� 12. In addition to the lateral pressures shown above.upiift pressures due to h = Depth of Excavation LATERAL PRESSURES
0 7. Passive earth pressures provided are ultimate values. An groundwater should be taken into account for bottom seal/tremie seal design. POST CONSTRUCTION
� appropriate factor of safety is recommended to be applied to these Distance from the Top of the Wall to POST-SEISMIC
N values if used for design. 13. Post-seismic earth pressures assume a horizontal acceleration coefficient, H = Bottom of He Layer or to Point of Zero
N K,,,equal to 0. Deflection whichever is Deeper.Feet
`� 8. Groundwater levels inside excavation should be maintained at the Novembe�2010 21-1-21292-001
� bottom of the proposed underpass final grade. 14. Passive resistance is based on1-inch of wall movement. � = Groundwater Level SHANNON 8� WILSON, INC.
°' Geoledttncal and Envi�menlal ConwltaMs F I G. 15
�
Strander Boulevard Underpass Phase II
Revised Dewatering Evaluation
May 6, 2011
Submitted To:
Mr. Jim Guarre, Senior Vice President
BergerABAM Engineers, Inc.
33301 9th Avenue South, Suite 300
Federal Way, Washington 98003-2600
BY:
Shannon &Wilson, Inc.
400 N 34`h Street, Suite 100
Seattle, Washington 98103
21-1-21292-003
�= ��� SHANNON �WILSON, iNC.
�� � _
May 6, 2011
Mr. Jim Guarre, Senior Vice President
BergerABAM Engineers, Inc. �
33301 9`h Avenue South, Suite 300
Federal Way, WA 98003-2600
RE: STRANDER BOULEVARD UNDERPASS, PHASE II,
REVISED DEWATERING EVALUATION
Dear Mr. Guarre: !
This letter presents our results from T'ask 2 and Task 3b (Prepare Dewatering Memorandum and
Refine Dewatering Analysis Based on Pumping Test) of the "Proposal for Dewatering
Evaluation, Underpass Section, and Engineering Support During Bid, City of Renton Strander
Boulevard/SW 27`�' Street Improvements, Renton and Tukwila, Washington," (the project) dated
December 15, 2010. Excavation of Strander Boulevard, Phase II project, will require that work
be performed belo«� the groundwater table to install a roadway, storm drain catch basins, and an
underdrain system.
Our proposed scope of serviccs for the dewatering evaluation (Task 2 and 3b) includes:
1. Describe project dewatering requirements.
?. Develop conceptual dewatering model.
3. Evaluate different deulatering systems configurations.
4. Identify dewatering issues.
5. Identify appropriate dewatering technologies for dewatering system configurations.
6. Refine de«�atering parameters.
7. Refine estimate of dewatering and recharge flows.
8. Develop de«�atering specifications.
���ork��-as authorized by you on February 24, 2011. This letter updates our previously submitted
'�Draft Strander Boulevard Underpass, Phase Il. Preliminary De���atering Evaluation,"dated
March 9, 2011, with dewatering recommendations based on the later-performed pumping test
(Shannon & �'�'ilson, 201 la, b).
._. .. :�- ., �����n�� �- _ . � ,�,�:�
"O CiOX 3003G3
SFATTLE WA 98103
:06-632-8020 FAX 206-695-6777 '
Tf3D: 1-800-II33-6388
����v✓��shannom.vilson corri 21-1-21292-003
Mr. Jim Guarre, Seniar Vice President S��ANNONFy�Ii(ILSON.INC.
BergerABAM Engineers, Inc.
May 6, 2011
Page 2 of 17
This letter presents our preliminary evaluations for items 1 through 7, above. Dewatering
specifications (item 8, above)has been submitted separately.
SITE AND PROJECT DESCRIPTION
The project is located near the City of Tukwila and City of Renton boundary, at Strander
Boulevard. The site map is shown in Figures 1 and 2. Our dewatering evaluation is based on the
'`Strander Boulevard Extension Phase II, 100% Design" prepared by BergerABAM on March 11,
2011.
Figure 2 shows a 36-foot-wide roadway and side���alk, sloping at up to a 10 percent grade to an
underpass below the BNSF Railway Company(BNSF) railway. The roadway for the Phase II
work ranges between Stations 14+71 and 25+19. The project is divided into two stages, Stage 1
is between approximately Stations 18+20 and 20+35, while Stage 2 is between Stations 16+02
and 18+20. The roadway has 3 Horizontal to 1 Vertical cut slopes on the sidewalls, which will
have gravel drains to collect���eeping groundwater and direct it to an underdrain system below
the roadway. The roadway design plans show a storm catch basin which��Iill extend below the ',
underdrain system along the south side of the road«ray. At its lowest point, the storm catch basin
will be at elevation -1 foot at approximately Station 17+32, as shown in Figure 3. Between
approximately Stations 17+80 and 18+65, a foundation slab will be placed to an elevation
-1 foot. The dewatering system will be designed to lower groundwater below the excavation
depths of the roadway slab,underdrain, and catch basins, down to a maximum depth of elevation
-4 feet, 3 feet below subgrade. The focus of this dewatering report is dewatering the bridge ,
underpass under the BNSF railway and ramping down the excavation to the bridge underpass.
The���ork will be performed in nvo stages; the eastern side of the bridge is Stage 1, the western ,
side of the bridge is Stage 2.
SITE GEOLOGY AND H�'DROGEOLOGY
Site Geolog��
The Strander Boulevard alignment is located in a relatively flat alluvial valley. The site geology
is characterized by the follov�ring stratigraphy(Shannon & Wilson, 2004):
■ Holocene Fill (fill)—The site has discontinuous human-placed till soils of varying
thickness at ground surface; the fill soils encompass a range of soil types and
hydraulic properties.
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Mr. Jim Guarre, Senior Vice President SI'{ANNON F�WILSON,INC.
BergerABAM Engineers, Inc.
May 6, 2011
Page 3 of 17
■ Holocene Estuarine/Overbank Deposits(estuary/overbank)—The Green/Duwamish
and Cedar Rivers deposited this fine-grained floodplain and deltaic unit. This unit
has not been ovemdden by glacial ice. It consists of very soft to medium stiff,
slightly fine sandy, clayey silt to silty clay with scattered organics and discrete peat
lenses and layers. This unit has relatively low permeability and is found throughout
the alignment. Duwamish estuarine/overbank deposits are generally located between
ground surface and -5 feet in elevation and are interbedded with peat and sands, with
deeper estuary,�overbank soils found in the�vest side of the alignment between
approximately elevations -50 and -75 feet.
■ Holocene Peat (peat)—Peaty layers of organic, fine-grained soils located between
approximately elevations 10 and 0 feet. Peat layers are generally between 1 and 3
feet thick and interbedded in estuary/overbank fine-grained deposits.
■ Holocene Alluvium—Duwamish/Green River—This fine- to medium-grained alluvial
unit was deposited in the channels of the Green/Duwamish River and is not glacially
overridden. The unit consists of inedium dense to very dense, clean to silty, fine and
fine to medium sand, with scattered organic materials. Its range of hydraulic
conductivity is low to high, depending on the fines content of the soil. Fine-grained
(silty fine sand to fine sandy silt) alluvium soils are generally found interbedded with
estuary/overbank soils between ground surface and elevation -5 feet. Between
elevations 0 and -50 to -90 feet, thickening to the east, the sandy alluvium soils
generally become clean to slightly silty, fine to medium sands. This lower soil unit
(clean to slightly silty, fine to medium sand) is referred to in this report as sandy
alluvium and is the aquifer material addressed in the following analyses.
Additional deep soil units are found on site; however, they have little impact on our de���atering
evaluation and will not be discussed. See Shannon & Wilson, 2004, for more information about
deep soil units. Soil data above was confirmed by 2011 borings, discussed in Shannon &
Wilson, 2011b.
Site Hydrogeology
The water table in the shallow estuary%overbank soils has a seasonal high groundwater of up to
elevation 19 feet (measured in May 2009). The deeper, sandy alluvium has groundwater
readings up to elevation 1� feet. Seasonal ground���ater fluctuations�;�ere observed up to about
6 feet, with the highest ground���ater levels generally recorded in March through May.
Groundwater in the shallow overbank and sandy alluvium is in hydraulic contact with the Green
River, so elevations ��ary depending on the river stage of the nearby Green River. Groundwater
elevations may rise higher than observed during high water or flood stages of the Green River.
Soils are considered saturated below elevation 19 feet.
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Mr. Jim Guarre, Senior Vice President SNi4NNUN F�WII+SON,INC.
BergerABAM Engineers, Inc.
May 6, 2011
Page 4 of 17
In March 2011, Shannon &Wilson performed aquifer testing at the site using well PW-1 as the
pumped well and five monitoring wells(MW-1, MW-3, MW-4, B-104, and B-106) (Shannon &
Wilson, 2011b). The constant rate test im�olved pumping well PW-1 for 24 hours at a rate of
208 gallons per minute(gpm), followed by a recovery period of 24 hours. The analysis of the
test data indicated that the alluvium unit has a transinissivity between 2,540 and 6,000 ft`/d, an
average hydraulic conductivity of 50 to 110 feet per day(fUd) and a storativity betvveen 6.9x I 0-�
and 7.7x 10-`�. The analysis also indicated that the nearby Green River acts as a recharge source
to the alluvium aquifer.
Discontinuous fill is located above the water table and not included in our dewatering evaluation.
CONCEPTUAL DEWATERING MODEL
Excavation below the water table will likely result in unstable side slopes and basal instability of
the road«�ay, drainage layer, and stormwater catch basins. Therefore, we believe that
groundwater control is necessary to complete the associated excavations. Construction
dewatering will be needed between approximately Stations 16+00 and 20+50 (4501inear feet),
«-here the stormwater basins, piping and foundation slabs extend below the groundwater table,
see Figures 2 and 3. Between approximately Stations 16+25 and 20+10, dewatering will also
include the cut slopes and road���ay subgrade which will extend below the groundwater table.
The width of the roadway dewatered varies from 36 feet (roadway and sidewalks only—no cut
slope or cut slope above the water table) to 130 feet (roadway, plus BNSF bridge construction
excavation). Dewatering���ells should not be placed on the upper edge of the cut slope, but
should be located on the slope where the grade will reach elevation 20 feet so the wells are
placed as close to the roadway(deepest part of the excavation) as possible.
Depending on seasonal groundwater highs, groundwater may be encountered during the
construction of two stormwater catch basins located outside of the recommended dewatering
area, at Station 21+50 (catch basin to an elevation of 17 feet) and Station 23+50 (catch basin to
an elevation of 18 feet). These t���o stormwater catch basins are not included in the dewatering
analysis below and any localized construction dewatering could likely be controlled���ith sumps
and pumps.
We estimated soil hydraulic parameters based on the 2011 pumping test, our review of the I
exploration logs and reports near the project, and our experience in similar soil and groundwater
conditions, listed above. We recommend that construction de���atering lower the ground�vater
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Mr. Jim Guarre, Senior Vice President �'�������N�C�.
BergerABAM Engineers, Inc.
May 6, 2011
Page 5 of 17
table 3 feet below excavation of the stormwater catch basins and roadway slab. The amount of
drawdown required far dewatering varies across the alignment and ranges from approximately
0 to 23 feet of drawdown. For our hydrogeologic evaluation, we also assumed a starting
groundwater elevation of 15 feet for the sandy alluvial aquifer and a saturated thickness of
94 feet. Parameters include:
■ A storage value of 0.0005 �vas used for the sandy alluvium based on pumping test
results,
■ A hydraulic conductivity value of 0.22 ft/day(7x10-5 centimeters per second
[cm/sec]) for estuary/overbank and peat soils, and 95 ft/day(0.033 cm/sec) far the
sandy alluvium at the site.
' Khorizontal t0 K�.ert;�a�—ratio of 10:1 for both units.
Construction dewatering is needed to drain the shallow estuary/overbank soils bedded with fine-
grained alluvium soils and depressurize the underlying alluvium sands. We performed a
dewatering evaluation to determine potential groundwater discharge rates and well
configurations for the project. The dewatering evaluation includes updating the hypothetical
groundwater flow model we developed in 2010 (see Shannon& Wilson, 2010) to incorporate the
pumping test analysis results and the revised current construction plans.
DEWATERING ANALYSIS
Analysis Approach
We performed the dewatering analysis using a numerical, three-dimensional groundwater flow
model of the Strander Boulevard area. The model uses the U.S. Geological Survey(USGS)
computer program MODFLOW-2000(USGS, 2000) to simulate groundwater flow conditions in
the upper 105 feet of the hydrogeologic system. We used the graphical user interface program
Groundwater Vistas (version 5; Rumbaugh and Rumbaugh, 2007)to construct, calibrate, and
operate the MODFLOW model. I
The model domain occupied an area 2,000 by 1,000 feet in plan view. The model represented
the hydrostratigraphy defined by the exploration program using five discrete layers as follo«�s:
■ Layer 1 Overbank (HeD) 30 feet thick 27 to -3 feet elevation
■ Layers 2 through 5 Allu��ium (HaD) 72 fe�et thick total -3 to -75 feet ele���ation
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Mr. Jim Guarre, Senior Vice President SFIAMNON�WILSON.INC,
BergerABAM Engineers, Inc.
May 6, 2011
Page 6 of 17
The static ground«�ater level was benveen 15 and 16 feet elevation. Therefore, layer 1 was
defined as unconfined and layers 2 through 5 were defined as confined.
VVe assigned initial hydraulic properties for the alluvium unit (model layers 2 through 5) based
on the results of the constant rate pumping test analysis (Shannon & Wilson, 2011 b). These
were 95 ft/day(horizontal conductivity) and 5 x 10-� (storativity). As the pumping test did not
provide estimates far the overbank unit, we assigned initial horizontal conductivity and specific
yield values of 0.22 ft/day and 0.05 (5 percent), respectively.
The model's boundaries consisted of the following:
■ East—an up-gradient constant head (elevation 15.5 feet in all layers);
■ West—a do���n-gradient constant head (elevation 15.0 feet in layers 1 through 3) to
represent the Green River; and
■ North and South—no flow conditions in all layers.
l��iodel Calibration
We calibrated the model using the 24-hour constant rate pumping test (dra«Jdown and recovery
data). This consisted of assigning a pumping flux of 210 gpm to PW-1 for a period of 24 hours,
and calculating the change in ground���ater levels(drawdown) in the monitoring wells MW-1,
MW-3 and MW-4. The observed and simulated drawdowns were compared, and a sum of
squares residual for each well calculated. To improve the match between the observed and
�nodeled drawdowns, we iterati��ely varied several key parameters within the conceptual range
(see above). Figure 5 shows the final match for wells MW-3 and MW-4, and Table 1
suminarizes the final pai•ameter values.
TABLE 1
FINAL GROL;ND��1'ATER FLO�'� 1���ODEL PARAI�IETER5
Khorizontal Krertical
Unit(La��ers) (ft/d) (ft/d) T (sf/d) S�(-) S (-)
Overbank(1) 0.22 0.022 4''' 0.0� -"'
Alluvium(2-5) 95 9.5 6,840 0.05'" 5 x 10-`'
�v�,r�s:
`'�` Property not im-oked in modeling.
''' Based on a static water table elevation of I S feet.
ti d=feet per day
�f�1=�quare feet rer day
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Mr. Jim Guarre. Senior Vice President SHANNON F�V`/IIaS�N,INC.
BergerABAM Engineers, Inc.
May 6, 2011
Page 7 of 17
Dewatering Simulations
Following completion of calibration, we used the model to simulate dewatering. We divided the
de���atering approach to correlate with Stage 1 and Stage 2 construction goals. Stage 1 is
between approximately Stations 18+20 and 20+35, which encompass the eastern side of the
BNSF underpass, and Stage 2 is between Stations 16+02 and 18+20, which encompass the
western side of the BNSF underpass. The potential groundwater discharge rates will be used in
support of discharge permits, to design w�ater treatment systems, if needed, and achieve a dry to
near-dry subgrade during construction.
The modeled dewatering facilities consisted of the following:
■ A sheet pile wall, for Stage 1 on three sides(north, west, and south), for Stage 2 on
two sides (north and south), from ground surface(elevation 27 feet) to an elevation of
-20 feet (or the base of model layer 2). The model used MODFLOW's Baf•i�ier�
boundary condition to simulate this feature; and
■ Six dewatering���ells, located inside the sheet pile area and east (Stage 1), and six
dewatering��rells located within the sheet pile area and west (Stage 2), each well
completed to a nominal depth of 60 feet (screened in the upper part of the alluvium
unit, model layers 2 and 3). The wells were simulated using MODFLOW's Gerrer-al
Heud boundary condition with an assigned head of-22 feet elevation.
Target modeled drawdown is up to -4 feet in elevation in Stages 1 and 2; the target dra��•do�vn's
are achieved after 14 days, see Figures 6 and 7. Each stage model was run for 368 days.
The model-predicted Stage 1 total discharge rates (for the six wells) to achieve the necessary
piezometric levels in the alluvium range betu-een 700 and 1,000 gpm. Howe��er, the Stage 1 rate
could initially be as high as 1,200 gpm if the entire Stage 1 dewatering system starts at the same time.
The model predicted Stage 2 total discharge rate (six ��ells) ranges between 800 and 1,100 gpm
after 14 days, but could initially be as high as 1,400 gpm if the entire Stage 2 dewatering system
starts at the same time. Stage 2 model results assume: (1) full groundwater recovery after
Stage 1, and (2) use of three de���atering wells installed as part of Stage 1 construction.
Discharge rates will decrease w�ith time as the saturated thickness of the aquifer is progressively
reduced by the de���atering effort. Ho��-ever, the pumping test showed that the aquifer would
receive recharge by the nearby Green River under pumped conditions, thereby limiting the
amount that pumping���ill decrease over time.
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Mr. Jim Guai7-e, Senior Vice President ������������-`���°�' �-
BergerABAM Engineers, Inc.
May 6, 2011
Page 8 of 17
The model estimated that the radius of influence of the dewatering may extend greater than
2,Q00 feet from the dewatered roadway excavation at 100 days. An increased length of pumping
may result in a greater radius of influence.
De�;-atering System Configurations
For Stage 1 construction, cutoff walls are on the north, west, and south sides of the BNSF bridge
excavation. For Stage 2 construction, cutoff walls will be on the north and south sides of the
BNSF bridge excavation but will be removed for slab construction on the east side under the
railroad tracks. Sheet piles were modeled down to a depth of elevation -20 feet. Increasing the
depth of the sheet piles can result in reduction of drav��down outside the sheet piles and reduce
the groundwater discharge rates. Additional cutoff walls along the north side of the excavation
grading ramps, outside of the BNSF bridge excavation, were examined in the preliminary
dewatering analysis, however, those walls did not seem to justify the expense of installation
«-hen compared to the small reduction in settlement the walls were designed to assist��ith
(Shannon& Wilson, 2011 a}. The additional sheet piles outside of the BNSF bridge excavation
were omitted from this analysis, in accordance with discussion with BergerABAM April 11,
201 1.
The ground���ater model assigned large-diameter pumping���ells inside the BNSF Bridge
excavation. The pumping test demonstrated that the area of influence for a well is extcnsive in
the site soils, so that all dewatering well installations can be placed in the BNSF bridge
excavation and the soils ramping down to the BNSF bridge will be dewatered in conjunction.
Depending on the Contractor's means and methods, additional dev�ratering wells outside of the
BNSF bridge excavation may or may not be needed. Dewatering wells were placed on 50-foot
spacing inside the BNSF bridge excavation. If the Contractor places the dewatering wells
outside of the BNSF bridge excavationlsheetpiles, it is likely that deeper andlor additional
dewatering wells���ill be needed to reach the dewatering goal. Typical dewatering well design is
sho«-n in Figure 4 and our groundwater model well design and drawdown contours are shown in
Figures 6 and 7. Additional dewatering wells may be needed by Stations 17+32 and 19+00 to
achieve adequate drawdown for the lowest stormw�ater catch basins. Dewatering wells may
extend as much as approximately 25 feet below the drawdown goal, depending on the location
and well efficiency. The groundwater model also assumes trenches/sumps will be used in the
fine-grained estuaryioverbank soils between approximately elevations 19 and 0 feet. The
groundwater model achieved dewatering goals at Stage 1 with six wells and Stage 2 with six
���ells (using three «-ells from Stagc 1). The exact number of���ells will depend on the
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Mr. Jim Guarre, Senior Vice President ���QH����N•t�
BergerABAM Engineers, Inc.
May 6, 2011
Page 9 of 17
Contractar's means, methods, sequencing, and scheduling; the number of dewatering wells could
increase or decrease.
DEVVATERING ISSUES
UNlities/Settlement
Dewatering can cause settlement by increasing the effective stress in a soil profile. Several
utilities cross beneath the BNSF embankment about 100 feet north of the proposed Strander
Underpass and BNSF bridge. We evaluated the dewatering settlement at the utility crossing and
beneath the BNSF railroad embankment. The dewatering analyses for this project estimated
about 13 feet of groundwater drawdown at the utilities locarion.
To analyze the settlement, we:
■ Developed a representative soil profile based on nearby borings,
■ Estimated elastic or consolidation parameters for each soil layer based on published
correlations and laboratory consolidation test data, and
■ Estimated settlement based on elastic and consolidation theory.
We estimated:
■ Bet��een 1 and 3 inches of settlement at the utility pipe inverts at the embankment
crossing, and
■ Betvveen 1 and 2 inches of settlement for the railroad embankment.
We anticipate that the settlement would be relatively uniform; differential settlement per 100 feet
of utility pipe/embankment���ould be on the order of'/2 inch. Settlement would occur as
dewatering operations progress and would be substantially complete when dewatering achieves a
steady-state condition.
Potential Groundwater Contaminants
Shannon & Wilson previously preformed a review� of em-ironmental hazards near the proposed
Sound Transit station adjacent to the north of the proposed project. In-house environmental files
were reviewed(Shannon&Wilson, 1999); however, a complete environmental assessment of I,
the Strander Boulevard site was not performed and environmental concerns that may have arisen I
after the report date of 1999 were not considered. Furthermore, the sites reviewed may have
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Mr. Jim Guarre, Senior Vice President �'������������•
BergerABAM Engineers, Inc.
May 6, 201 I
Page 10 of 17
been remediated and no longer pose a hazard. The previously identified sites that potentially
pose a threat to groundv��ater quality within approximately 0.25 mile of the site include:
■ LUST—Leaking Underground Storage Tank sites
■ TOXICS—Washington State Registered Sites for cleanup of hazardous waste under
the Model Toxic Control Act (MTCA)
■ UST—Registered Underground Storage Tank sites
A Phase II environmental assessment was performed by Shannon &Wilson(1999) on the
northwestern property adjacent to Strander Boulevard; the findings indicated one shallo��v
groundwater sample had naturally occumng arsenic above MTCA cleanup levels.
A Union 76 gas station exists on West Valley Highway, observed approximately 500 feet
north«rest of the site. The gas station appears to have been built after the 1999 report of
environmental concerns in the area; information about potential USTs at the gas station is
unknown. The proposed Strander Boulevard is adjacent to the Union Pacific and BNSF
railways. No environmental assessments of these railways were performed specifically for this
project. Ho�vever, in general, railroads are associated with potential surficial contamination of
hydrocarbons, metals, creosote, pesticides, and herbicides.
Construction dewatering at the Strander site has the potential to mobilize contaminants from
nearby properties. The upper 30 feet of soil at the Strander Boulevard site is generally fine-
grained and has a relatively low hydraulic conductivity, which slo��s.�retards the migration of
contaminants in the soil unit. Therefore, the identified sites pose a low risk of contaminant
mobilization. The contaminant migration rate in the lower alluvium sands is potentially higher
due to the higher hydraulic conductivity. However, the alluvial sands are partially protected
from contaminant migration by the lower hydraulic conductivity soils above them. Identified
and potential sources of contamination in the Strander Boulevard area are likely near surface,
which have lower potential for infiltration into, or migration in, the groundwater.
During the pumping test, groundwater samples were taken to test for volatile organic
compounds, hydrocarbons,phosphate,total, and dissolved priority pollutant metals. The
analytical results indicate that the goundwater discharge during the pumping test was clear of
contaminants (Shannon& Wilson, 2011b).
Contaminants have a low probability of being mobilized by construction de���atering at this site.
Construction dewatering should include periodic analytical testing of monitoring wells and/or
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Mr. Jim Guai7-e, Senior Vice President ������''`�����`�-_-��`��'`.�'�`� �
BergerABAM Engineers, Inc.
May 6, 2011
Page 1 I of 17
dewatering effluent to ensure that mobilization of contaminants does not occur. If contaminant
mobilization is detected, cutoff barriers(cutoff walls, recharge wells, etc.) between the
contaminant plume and the de���atering system or effluent treatment systems will mitigate the
impact of mobilized contaminants. Based on groundwater samples taken at the adjacent northern
property, naturally occurring arsenic in the shallow groundwater may be an issue for dewatering
effluent disposal.
Discharge Options
Discharge of dewatering effluent will depend on water quality, permitting, and the final disposal
location of the discharge. If the Contractor employs extensive sump pumping, sand filters and
settlement tanks should be used.
Based on our understanding of the project, the preferred dewatering effluent discharge location is
the City of Renton wetlands, located south of the project. Due to the relatively low permeability
of the near-surface soils, we believe that infiltration at the City of Renton wetlands will have a
minimal effect on de���atering efforts at the site.
Additional dewatering effluent discharge options include storm or sanitary sewers. Groundwater
quality testing will be needed to obtain permits for dewatering effluent disposal in sewers. If
encountered,contaminated groundwater may require additional treatment specific to the
contaminants. Some of the dewatering effluent could also be disposed of as sprinkler water for
landscaping on nearby City of Renton or City of Tuk���ila property.
Dewatering of Strander Boulevard may involve routing dewatering effluent to an east or west
discharge point over or under the BNSF railroad tracks. Dewatering effluent piping can be
elevated above the BNSF tracks with proper pump sizing and lift capacity. If the Contractor
chooses piping the dewatering discharge over obstructions, either higher head dewatering pumps
or booster pumps will be required to accommodate the necessary lift. Coordination with BNSF
«-ill be needed to obtain consent to construct the temporary piping over their tracks. Another
option to route effluent from east to west including using a culvert located under the BNSF
railroad track to the south of the project location. The Contractor should route discharge piping
to match construction activities. When pipe routing encounters path obstructions, the Contractor
should bury or raiup over the pipe.
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Mr. Jim Guarre, Senior Vice President SNANNON�W1t�S�N,INC.
BergerABAM Engineers, Inc.
May 6, 2011
Page 12 of 17
FINISHED ROAD DRAINAGE ROCK ANALYSIS
We evaluated the proposed side slope drainage layer and did not recognize any fatal flaws in the
design. Incorrect installation of materials for the groundwater collection pipes or filter fabrics
could lead to future clogging or other maintenance issues.
We were requested to estimate the potential volume of groundwater collected by the finished
construction drainage rock side slopes and base layer. The drainage layer may convey
approximately 10 to 30 gpm during high groundwater periods. These estimated discharge rates
do not account for additional runoff flow due to rainfall.
APPROPRIATE DEWATERING TECHNOLOGIES
FOR DE�'�'ATERING SYSTEM CONFIGURATIONS
Numerous factors influence the type of dewatering approach employed, including soils, aquifer
thickness, the relationship of subgrade to the base of the aquifer, drawdown requirements,
shoring and excavation approaches, the amount of dewatering flow anticipated, and, most
importantly, the Contractor's experience working in dewatered and wet soils. Regardless of the �I
approach employed for short-term dewatering anticipated for the project, soil heterogeneity and !
stratification will likely result in perched pockets of undrained water and the Contractar should
anticipate sump pumping and working���ith«-et soils.
Sumps and/or Trenches i
Sump and/ar trenches generally provide the least costly ground��ater control and are the most
common de�;�atering method. Sumps consist of excavations immediately adjacent to or in an
excavation with the purpose of collecting groundwater. Sump pumping should be limited to no ��
more than 2 or 3 feet of drawdown. Sumps work well in either fine- or coarse-grained soils,
which typically provide low or high(respectively) volumes of dewatering flow. Sumps and
trenches generally pump finer formation material which can undermine excavations. Sump
pumping requires considerable treatment or settlement of fines in the dewatering discharge prior
to disposal.
Pumped Wells
Pumped wells typically consist of large-diameter holes(24- to 36-inch diameter) and large-
diameter casings/screens (i.e., 8-to 16-inch diameter). Pumped wells, often called deep wells,
are relatively deep compared to sumps and vacuum �;�ellpoints. Each pumped well employs an
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Mr. Jim Guarre, Senior Vice President SHANNON F��VILSON.INC.
BergerABAM Engineers, Inc.
May 6, 2011
Page 13 of 17
individual pump, which typically discharges to a common manifold. Pumped wells work best
(most efficiently) in relatively coarse-grained(high permeability} formations(silty sand, sand,
and gravel) that allow wide spacing of«�ells (typically 25 to 250 feet) due to a large radius of
influence. Pumped wells typically yield volumes of water in the range of 25 to 250+gpm per
well.
Vacuum Wellpoints
Vacuum ��rellpoints connect to a common vacuum header and typically operate using a single
pump for the whole system. Vacuum wellpoints are suitable for both fine- and coarse-grained
soils. They are generally 15 to 25 feet deep and constrained by the limits of the vacuum to lift
water out of the ground (lift capacity is typically 15 to 20 feet at sea level). The wellpoints
typically have a 3-foot length of slotted well screen at the bottom and are spaced 2 to 10 feet
apart with the closer spacing for finer-grained soils (i.e., silt and clay). For coarser soils and
wider spacings, pumped���ells typically prove more efficient and less costly than vacuum
wellpoints.
Eductors/Ejectors
Typically, closely spaced educators are rarely used except in fine-grained soils, due to their cost.
Eductors employ pressurized flow not limited by vacuum constraints, ���hich allows them to
achieve greater drawdowns than vacuum wellpoints. Educators require little maintenance
compared to pumped wells or vacuum wellpoints and are particularly suited for excavations
needing great drawdowns over a long period of time (months or years).
Cutoff Walls
Cutoff�;�alls can include sheet piles, slurry walls,�trenches, soiligrout walls, secant piles, and an
assortment of other low permeability barriers to hinder the flow of groundwater. Cutoffs do not
necessarily eliminate the need for dewatering pumping. However, they can significantly reduce
the volume of water that needs to be extracted and mitigatelreduce/eliminate drawdown impacts
related to potential settlement or contaminant mobilization.
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Mr. Jim Guarre, Senior L'ice Pi•esident ��'�'`'��'��������-�����'��r
BergerABAM En`ineers, Inc.
May 6, 2011
Page 14 of 17
DE«'ATERING RECOnin1E1�DATIONS A:VD CONCLUSIONS
Dewatering System
For the soil types encountered and the depth of excavation, large-diameter pumped wells in
conjunction with trenches/sumps appear the most efficient approach to dewatering the Str•ander
excavation. The large-diameter dewatering wells will be used to relieve the pressures and basal
instabilities that may be encountered at depths. Because the near-surface soils are fine-grained,
unless an extended period of dewatering(at least one month) occurs before construction starts,
the fine-grained soils will drain slo���ly and the Contractor should be prepared to encounter
residual groundwater and•'or���et soils, «�hich should be drained ���ith sumps, trenches, and
pumps.
T�pical �'�'ell Design
Pumped wells can be placed on a�0-foot spacing in the BNSF bridge excavation and generally
extend 20 feet below the elevation dewatering goal, a minimum of approximately 70 feet belo��
ground surface (bgs). The dewatering���ells are placed «�ithin the BNSF bridge construction
(within the sheet piles)to achieve adeyuate depressurization of the alluvial sands. If dewatering
wells are placed outside the sheetpiles,the Contractor will likely need wells to be deeper in depth
and capable of pumping higher volumes of water, and additional wells may be needed. Figure 4
shows a typical dewatering well schematic. Figures 6 and 7 shows a schematic hypothetical well
layout used in our groundwater model for Stages 1 and 2, respectively. Dewatering wells will
likely be 12-inch-diameter casings and screens placed in a 24- to 36-inch-diameter borehole.
Our analyses assumed highly efficient wells(approximately 80 percent efficient). Lower
efficiency wells will require increased depths andlor additional wells.
Preliminarv Filter Pack and W'ell Screen
The Contractor should design the dewatering�-e11 filter pack material to industry standards in
order to prevent the pumping of fines from the formation while maximizing the well yield. The
Contractar should desib the well screens to retain the filter pack material. Failure to design a
filter pack which is appropriate to the formation grain size and the well screen based on the filter
pack grain size increases the risk of pumping sediment-laden water to the discharge point and
undermine structures by creating voids due to formation piping processes. Our preliminary
desian indicates that a 20- or 30-slot ���ell screen may be appropriate; ho���ever, «�ell slot size
�i-i-'>>��_-�u,;.i i d;��.,,i,;i� '1-1-_'1�9?-003
Mr. Jim Guarre, Senior Vice President
���-��.����`� ��_�'���_����,1��
BergerABAM Engineers, Inc.
May 6, 2011
Page 15 of 17
needs to be tailored to the Contractor's means, methods, and dewaterin, desi�n, particularlv the
filter pack the Contractor decides to use.
Friction Loss and Pump Sizing Evaluation
Friction loss refers to that portion of pressure lost by fluids while moving through a pipe, hose,
or other limited space. Estimating that the dewatering effluent discharge piping is made of
12-inch-diameter pol}n-�inyl chloride, friction losses account for a small percentage of total
dynamic head losses. Dewatering wells need to be capable of pumping a minimum of 200 gpm
per well with a lift capacity of 70 feet. Based on the groundwater model results, the dewatering
pumps should have a minimum of 15 to 20 horsepower to overcome friction losses and
adequately power the dewatering system. If fewer large-diameter pumped wells are installed on
site or the wells are deeper that 70 feet bgs, the pumps may need increased horsepower and
capacity.
Pump Operation
Pumps should consist of typical submersible dewatering pumps capable of running dry without
burning up. Dewatering specifications should require oil cooled pump systems, or pump systems
that cycle off when the groundwater is lowered below pump elevation, so that the pumps do not
overheat and burn up. The Contractor should be responsible for the maintenance of the pumps
and dewatering system.
Power Supply
The Contractor should have backup generators on hand in the event that power is lost at the site.
Dewatering System Maintenance
The Contractor should be responsible for the maintenance of the dewatering system for the
duration of the project. Pumping test water quality testing results indicate a high probability of
slime-forming and iron-related bacteria growth, a moderate probability of sulfate-reducing
bacteria growth, and a low probability of nitrifying bacteria growth in the groundwater
(Shannon&Wilson, 2011b).
Contractors should be aware that the presence of iron-reducing bacteria and slime bacteria could
i•equire periodic well rehabilitation to maintain dewatering system performance, and that water in
settling tanks may become turbid and colored from bacteria growth in the water and require treatment.
�i-i-�i���-o�:��-u.d��K�w�p��i� 21-1-2129�-003
Mr. Jim Guarre, Senior Vice President �iF�1NNON€�WILS{�N.(NC.
BergerABAM Engineers, Inc.
May 6, 2011
Page 16 of 17
Dewatering Specifications
A tailored dewatering specification should reflect the project schedule, excavation approach, and
identified issues (i.e., settlement, etc.). The project team should determine the specification
approach prior to completion of the contract documents. We have provided specifications that
include performance criteria(i.e., minimum drawdown below excavation and numerical values
that limit drawdown outside the excavations). Dewatering specification assistance has been
submitted separately to BergerABAM.
Existing groundwater observation/monitoring wells in the project vicinity should be maintained
and used to monitor performance of the Contractor's dewatering system. Depending on the
Contractor's dewatering approach and design, additional observation �vells may be��-arranted.
Groundwater levels should be monitored prior to and during excavation and dewatering
activities, to evaluate natural groundwater level fluctuations and the performance of the
dewatering system.
We recommend that the Contractor retain a Washington State-licensed hydrogeologist or
engineer experienced in construction dewatering to design a system consistent with the selected
roadway excavation system and the Contractor's means and methods.
LIMITATIONS
This letter was prepared for BergerABAM and the Cities of Renton and Tukwila for specific
application to the site defined in this letter. This study has been prepared in accordance with
generally accepted hydrogeologic methods. No other warranty, express or implied, is made.
Shannon & V1�ilson, Inc. has prepared the enclosure, "Important Information About Your
Geotechnical/Environmental Report."to assist }ou and others in understandina the use and
limitations of our reports.
The geologic and hydrogeologic data obtained indicate subsurface conditions only at the specific
locations and times when the observations were made and only to the depths penetrated. They
do not necessarily reflect strata variations that may exist between such locations. The validity of j
the dewatering estimates is based in part on assumptions about the stratigraphy and hydraulic
conductivities made by our staff. If subsurface conditions different from those described ar•e
encountered during future explorations or excavations, findings in this letter may require
re-evaluation. Actual permeabilities or hydraulic conductivities significantly lower or hi�her
than those assumed in our e�,�aluations���ill result in significantly lo���er or higher flows
21-I-_'1242-Uf,�;-L Ldocx�ti�p clp �1-1-�1�9�-UQ i
Mr. Jim Guarre, Senior Vice President ��������Q���
BergerABAM Engineers, Inc.
May 4, 20] 1
Page 17 of 17
and drawdown impacts. More refined or accurate estimates of flow would require additional
subsurface explorations, and pumping tests.
Sincerely,
SH,ANNON & WILSON, INC.
�
Kate E. Stalker, L.G.
�-Iydrogeologist
-bot aah!
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LAWRrtdCE M. V��::7
Larry West, L.H.G., C.E.G.
Vice President
KES:STD:JNB:LMW/kes
Enc: References
Figure 1 —Vicinity Map
Figure 2—Site Plan(2 sheets)
Figure 3 —Generalized Suhsurface Profile A-A' (4 sheets)
Figure 4—Typical Pumped Well �,
Figure 5 —Groundwater Model vs Pumping Test Data Calibration Curves '
Figure 6—Dewatering Groundwater Elevation Contours, Stage l, 14 Days of Pumping I
Figure 7 —Dewatering Groundwater Elevation Contours, Stage 2, 14 Days of Pumping
Important Information About Your Geotechnical/Environmental Report
21-1-2 t 292-OOJ-L].docw'wp/clp 21-1-21292-003
SHANNON F�WILSON.INC.
REFERENCES
Rumbaugh, J.O., and Rumbaugh, D.B., 2007, Groundwater vistas, version 5.0: Herndon,Va.,
Environmental Simulations, Inc.
Shannon&Wilson, Inc., 1999, Phase I Environmental Site Assessment, Boeing/Longacres
property, Tukwila Station,Tukwila,Washington, June, project number T-6003-21: Prepared
for Sound Transit, Seattle,Wash.,by Shannon&Wilson, Inc., Seattle,Wash., 16 p.
Shannon&Wilson, Inc., 2004, Geotechnical report for conceptual design, Strander
Boulevard/SW 27`f' Street improvements, Renton and Tukwila, Washington, February.
Shannon &Wilson, Inc., 2010, Groundwater de�vatering memorandum, Strander Boulevard
Underpass Phase I, Renton,Washington—BergerABAM project no. fapwt-09-175, Job
number 21-1-21292-001: Prepared for BergerABAM, Federal Way,Wash., by Shannon &
Wilson, Seattle,Wash., May.
Shannon& Wilson, Inc., 2011a, Updated Draft Strander Boulevard Underpass, Phase II,
Preliminary Dewatering Evaluation, Job number 21-1-21292-002: Prepared for
BergerABAM, Federal Way,Wash., by Shannon &Wilson, Seattle,Wash., March 9.
Shannon &Wilson, Inc., 2011b, Draft pumping Test Analysis Report, Strander Boulevard Phase
II, Renton and Tukwila,Washington, Job number 21-1-21292-003: Prepared for
BergerABAM, Federal Way,Wash., by Shannon &Wilson, Seattle, Wash.,Apri129.
U.S. Geological Survey, 200Q, MODFLOW-2000 v. 1.19.01: Available:
http://water.usgs.go�-�/nrp/gwsoft���are/modflow2000/modflow2000.html.
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� 02-11-11. SHANNON& WILSON, �Nc. FIG. 3
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� 02-11-11. SHANNON 8�WILSON, �Nc. FIG. 3
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� 02-11-11. SHANNON 8 WILSON, �Nc. FIG. 3
� Geo6edinlwl and EnvirorrnerMel Oonsuttents Sheet 4 of 4
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_
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0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1
Time(Days)
Strander Boulevard Phase II
Renton and Tukwila, Washington
GROUNDWATER MODEL VS
PUMPING TEST DATA
�+ CALIBRATION CURVES
�
c May 2011 21-1-21292-003
�
m SHANNON &WILSON, INC.
�+ FIG.5
Geotechnical and Environmental Consultants
�� Hypothetical �
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Notes: Strander Boulevard Extension
Plan View Phase II
Renton,Washington
Contours show groundwater elevation after 14 days of dewatering.
Typical dewatering well distribution, actual well placement depends on contractor means, methods DEWATERING GROUNDWWATER
schedule and dewatering design. ELEVATION CONTOURS
STAG E 1
14 DAYS OF PUMPING
May 2011 21-1-21292-003
SHANNON S WILSON, INC FIG. G
Geotechnical and Environmental Consultants
i
1' Hypothetical �Z~ �� \,
Dewatering wells `` `�' ,
� �" �
�r �} I f � p � �
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,J ' t �� ��—
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� ..,.. � ^ 't r� `�� '•�� It- � .. -�� C)~J4'-- bV .
�-- ~ � � � � i�' f � ,d 'V 1
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y-� '-�'� -��:=,,,,___Z -, _ _... � `,�. �` � �
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Notes: Strander Boulevard Extension
Plan View Phase II
Renton,Washington
Contours show groundwater elevation after 14 days of dewatering.
Typical dewatering well distribution, actual well placement depends on contractor means, methods DEWATERING GROUNDWATER
schedule and dewatering design. ELEVATION CONTOURS
STAGE 2
14 DAYS OF PUMPiNG
May 2011 21-1-21292-003
SHANNON S WILSON, INC F�G. �
Geotechnical and Environmental Consullants
_ SHANNON 8�WILSON, INC. .Attachment to and part of Report 21-1-21292-003
- Geotechnical and Environmental Consultants
Date: A1av 6,201 I
- To: A1r.Jim Guarre
BergerABAM Engineers,lnc.
IMPORTANT INFORMATION ABOUT YOUR GEOTECHNICAL/ENVIRONMENTAL
REPORT
CONSULTING SERVICES ARE PERFORMED FOR SPECIFIC PURPOSES AND FOR SPECIFIC CLIENTS.
Consultants prepare reports to meet the specific needs of specific individuals. A report prepared for a civil engineer may not be
adequate for a construction contractor or even another civil engineer. Unless indicated othenvise,your consultant prepared your report
expressly for you and expressly for the purposes you indicated. No one other than you should apply this report for its intended
purpose �i�ithout first conferring with the consultant. No party should apply this report for any purpose other than that originally
contemplated���ithout first conferring��ith the consultant.
THE CONSULTANT'S REPORT IS BASED ON PROJECT-SPECIFIC FACTORS.
A geotechnical�'environmental repon is based on a subsurface exploration plan designed to consider a unique set of project-specific
factors. Depending on the project, these may include: the general nature of the structure and property involved; its size and
configuration; its historical use and practice; the location of the structure on the site and its orientation; other improvements such as
access roads, parking lots, and underground utilities; and the additional risk created by scope-of-service limitations imposed by the
client. To help avoid costly problems, ask the consultant to evaluate ho�a�any factors that change subsequent to the date of the report
may affect the recommendations. Unless your consultant indicates othenyise, your report should not be used: (1) when the nature of
the proposed project is changed (for example. if an office building will be erected instead of a parking garage, or if a refrigerated
warehouse�vill be built instead of an unrefrigerated one, or chemicals are discovered on or near the site); (2)���hen the size, elevation,
or configuration of the proposed project is altered; (3)when the location or orientation of the proposed project is modified; (4) when
there is a change of o��mership; or(5) for application to an adjacent site. Consultants cannot accept responsibility for problems that
may occur if they are not consulted after factars�vhich were considered in the development of the report have changed.
SUBSURFACE CONDITIONS CAN CHANGE.
Subsurface conditions may be affected as a result of natural processes or human activity. Because a geotechnical/em�ironmental report
is based on conditions that existed at the time of subsurface exploration, construction decisions should not be based on a report whose
adequacy may have been affected by time. Ask the consultant to advise if additional tests are desirable before construction starts; for
ezample,groundwater conditions commonly vary seasonally.
Construction operations at or adjacent to the site and natural events such as floods,earthquakes,or groundwater fluctuations may also
aftect subsurface conditions and,thus,the continuing adequacy of a geotechnical!environmental report. The consultant shoul d be kept
apprised of an�-such events,and should be consulted to determine if additional tests are necessary.
MOST RECOMMENDATIONS ARE PROFESSIONAL JUDGMENTS.
Site exploration and testing identifies actual surface and subsurface conditions only at those points�vhere samples are taken. The data
��ere ehtrapolated by your consultant,who then applied judgment to render an opinion about overall subsurface conditions. The actual
interface bet���een materials may be far more gradual or abrupt than your report indicates. Actual conditions in areas not sampled may
differ from those predicted in your report. ���hile nothing can be done to prevent such situations, you and your consultant can work
together to help reduce their impacts. Retaining }rour consultant to observe subsurface construction operations can be particularly
beneficial in this re�pect.
Pagc 1 uf 2 I 201 I
A REPORT'S CONCLUSIONS ARE PRELIMINARY.
The conclusions contained in your consultant's report are pr�liminary because they must be based on the assumption that conditions
revealed through selective exploratory sampling are indicative of actual conditions throughout a site. Actual subsurface conditions can
be discerned only during earthwork; therefore, you should retain your consultant to observe actual conditions and to provide
conclusions. Only the consultant who prepared the report is fully familiar with the background information needed to determine
whether or not the report's recommendations based on those conclusions are valid and w�hether or not the contractor is abiding by
applicable recommendations. The consultant who developed your report cannot assume responsibility or liabilit�- f'or the adequacv of
the report's recommendations if another party is retained to observe construction.
THE CONSULTANT'S REPORT IS SUBJECT TO MISINTERPRETATION.
Costly problems can occur when other design professionals de�elop their plans based on misinterpretation of a
geotechnical/environmental report. To help avoid these problems,the consultant should be retained to work with other project desi��n
professionals to explain relevant geotechnical,geolovical. hydrogeolo�ical,and environmental findin�s.and to re�ie�� the adequac� of
their plans and specifications relative to these issues.
BORING LOGS AND/OR MONITORING WELL DATA SHOULD NOT BE SEPARATED FROM THE REPORT.
Final boring logs developed by the consultant are based upon interpretation of field logs (assembled by site personnel), field te�t
results,and laboratory and/or office evaluation of field samples and data. Only final boring logs and data are customarily included in
geotechnical/environmental reports. These final logs should not,under any circumstances, be redra���n for inclusion in architect�n•al or
other design dra�vings,because drafters may commit errors or omissions in the transfer proce;�.
To reduce the likelihood of boring log or monitoring well misinterpretation, contractors should be gi�en read� acce,;to the complete
geotechnical engineering/environmental report prepared or authorized for their use. If access is provided only to the report prepared
for you, you should ad��ise contractors of the report's limitations, assuming that a contractor was not one of the specific persons fur
whom the report was prepared, and that developing construction cost estimates was not one of the specific purposes for which it ��a�
prepared. While a contractor may gain important kno���ledge from a report prepared for another party, the contractor should discuss
the report with your consultant and perform the additional or altemative �vork believed necessary to obtain the data specifically'
appropriate for construction cost estimating purposes. Some clients hold the mistaken impression that simply disclaiming
responsibility for the accuracy of subsurface information always insulates them from attendant liability. Providing the best available
information to contractors helps prevent costly construction problems and the adversarial attitudes that aggravate them to a
disproportionate scale.
READ RESPONSIBILITY CLAUSES CLOSELY.
Because geotechnical/environmental engineering is based extensively on judgment and opinion. it is far less exact than other design
disciplines. This situation has resulted in«�holly unwarranted claims being lodged against consultants. To help prevent this problem.
consultants have developed a number of clauses for use in their contracts, reports and other documents. These responsibility clauses
are not exculpatory clauses designed to transfer the consultant's liabilities to other parties; rather, they are definitive clauses that
identify where the consultant's responsibilities begin and end. Their use helps all parties im�olved recognize their individua]
responsibilities and take appropriate action. Some of these definitive clauses are likely to appear in your report, and yrou are
encouraeed to read them closel�. Your consultant�vill be pleased to gi��e full and frank ans«ers to your question;.
The preceding paragraphs are based on infonnation provided by the
ASFEr'Association of Engineering Firms Practicin��in the Geosciences. Sil��er Spring. 1��laryland
Pa«��?�d�� I 2111 I
----�
���s� � - SHANNON F�WILSON, INC. , �-F:::
� . � , ck:,��:
` rLCR�.D.:
I�NESOTA
115SC_=1
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.. 1.y•..(�I:.'.
June 22, ?Ol 1
Mr. Jim Guan-e, Senior Vice President
BergerABAM Engineers, Inc.
33301 9tn Avenue South, Suite 300 ��.,
Federal Way, WA 98003-2600 �� ; ``�
r, ,\ ` .
RE: STRANDER BOULEVARD UNDERPA�SS, I��E II, I�EWATERING
EVALUATION ADDENDUM � ''�;,�,�,, �'��,
�.
<; � � .,���,� ,
Dear Mr. Guarre: --_ �
�- •�
- � \ � .� ,,
This letter is an addendum to our Shannon R �Wilsbn�VlayY� 20�11,r�ort. "Strander Boulevard
Underpass, Phase II, Revised Dewaterin�v�a}�u�bq�" �e based'�our�current analyses on
updated plans for the exc�vatio�..�ro�dec�by,-Berge(,rA�AIC�I on J�ne 13, 2011. The June plans ,
show a slightly differe�t grading pla�,,ga�ng ir�,and o�t of the�xcavation, and have changed the
southern sheet pile vvalls to �fru�al retairl�ng��*�lls, e�ding to an elevation of 2.5 feet (see
Figures 1 and 2). `� ��� `��� `�,
., , ..
. �, ,, �., ,:
Based on the ne��� proposed co�figurat�dn, de1��atering discharge rate estimates increase from the
previous May 2011 analysis becac�,se the pre�ious model featured deeper sheet piles to the south,
which have been replaced with shal�b�ver etaining walls. Shallower walls allow more
groundwater to flow underneath, increasing discharge rates.
It is our understanding that the excavation staging and depths below the BNSF Railway
Company(BNSF) railroad will remain similar to the previous design plans; however, we will not
consider the stormwater catch basin conveyance system dewatering at this time, since it is not
longer included in the construction plans of Phase II construction. Between approximately
Stations 17+80 and 18+65, a foundation slab will be placed to an elevation -1 foot. Under our
conceptual dewatering approach,the dewatering system will lower groundwater below the
excavation depths of the roadway slab down to a maximum depth of elevation -4 feet, 3 feet
below subgrade. The focus of this dewatering report is dewatering the bridge underpass under
the BNSF railroad and ramping down the excavation to the bridge underpass. The work will be
performed in two stages; the eastern side of the bridge is Stage 1, the western side of the bridge
is Stage 2.
100 NORI H 34TH Sl REE7. SUII E 100
G O. BOX 300303
�FATTLE,WASHINGTON 98103
�06-632-8020 FAX 206-695-6777
'LiD 1-800-833-6388
�.v.�w shannor.wi!son ccm 21-1-?1?92-003
Mr. Jim Guarre, Senior Vice President ������� '��- u�������°-�`���°°���
BergerABAM Engineers, Inc.
June 23. 201 1
Page 2 of 6
DE��'ATERING 190DEL
Exca�-�ation below the water table will likely result in unstable side slopes and basal instability of
the roadway. Therefore, we believe that groundwater control is necessary to complete the
associated excavations. Construction dewatering will be needed between approximately Stations
15+50 and19+80 (4301inear feet), where the grading and�oundation slabs extend below the
groundwater table, see Figure 2. The width of the��c�w�y de�at�ed varies from 36 feet
(roadway and sidewalks only—no cut slope or cut��op�abeve the�6ater table) to 130 feet
(roadway,plus BNSF bridge construction excavatio�. `� �'`� �
1 <'y .�`� �`-r`���
We estimated soil hydraulic parameters based o�U��-,,pump�ng f�t, our r�view of the
exploration logs and reports near the project, and ou.t'expexie�e im�imi ar�oil and groundwater
� �.
conditions, listed above. We recommen�t�.con�r ction d�w�ring;.lower the goundwater
table 3 feet below excavation of the ro,� ' ay`�1� �e/ariAountbf di-awdown required for
�' �;
dewatering varies acros�-�the ahg�n��and r�nges �rom��rc�xi3Yiately 0 to 23 feet of drawdo«n.
For our hydrogeolog�ic�evaluat�e.n groi.tr�d�;�terparameters,pxease refer to Shannon R Wilson,
2011.� `'�
` ._`� .,\�1 �\`.
Dewatering Simulations \ �� � �
.,�
Following completion of calibrati�p of the g,�ound����ater model, we used the model to simulate
� �
dewatering. We divided the de���ateii�;ajiproach to correlate with Stage 1 and Stage 2
construction goals. Stage 1 is between approximately Stations 18+20 and 19+80, which
encompass the eastern side of the BNSF underpass, and Stage 2 is between Stations 15+�0 and
18+20, which encompass the western side of the BNSF underpass. The potential groundwater
discharge rates will be used in support of discharge permits, to design water treatment systems, if
needed, and achieve a dry to near-dry subgrade during construction.
The modeled de��ater•ing facilities consisted of the follo��-ing:
� Shannon&Wilson, Ine.,2011,Strander Boule�ard underpass. Phase I1. re��ised dewatering e��aluation. project
number�1-1-21292-003: Prepared for Bergei:ABA1�4 Engineers. Inc. of Federal �Vay. Washington. by Shannon R
Wilson,Inc.of Seattle,Washington,May 6.
2 i a-z i z9?-ooa-�z.a«x-Wpnkn 21-1-21292-003
Mr. Jim Guarre, Senior Vice President ` ���_ � ` � �� �� �
BergerABAM Engineers, Inc.
June 23. 201 l
Pa�e 3 of 6
■ St�eet pile ��-alls for Stage 1 on tti��o sides (north and ��est) and a retaining ���all on the
south side. For Stage 2, a sheet pile«�all on the north side and a retaining«�all on the
south side.
■ Sheet pile walls extend from ground surface (elevation 27 feet) to an elevation of-20 feet
(the base of model layer 2). Retaining walls extend from ground surface(elevation 27
feet)to an elevation of 0 foot(the base of model l�ye� 1).
■ Six dewatering wells, located inside the ea�t'e�`se�,of wall�.(Stage 1), and six dewaterin��
wells located within western set of walls (�tage�),_�ach we�i'completed to a nominal
depth of 60 feet(screened in the upper part�the a1li�ui,�an u�it, model layers 2 and 3).
�� % � �'��. r.
Target modeled drawdown is up to-4 feet in eleva�`�lStage� 1 anti 2; the�rget dra�vdo���ns
/ `- � -�,
are achieved after 14 days, see Figures 3 and 4;' Each sYa�e�i�odel��was r�_f�368 days.
; � / '.,� ` �'..
The model-predicted Stage 1 total dischafge�r�te�'fqY the,six�,el�s,�t�'achieve the necessaiy
,•.:, � . � , ,_ �
piezometric levels in the�tr��n rar�ge�etv�een 7d0 a�d �,100 gallons per minute (gpm).
. .. , , � , 1.�,
However, the Stage 1 r�te could initiall'�;be as�,high a,s 1,3�0 �pm if the entire Stage 1 de���atering
system starts at the sa�ne tim�.~ ��•� ` -- -��
, ., \� \ � '�����''•
The model predicted Stag�,� tota�.disc�arge`rate�si�%'vvells) ranges bett��een 800 and 1,200 gpm
after 14 days, but could initial�,y be�s,�gh as'��1,400 gpm if the entire Stage 2 dewatering system
starts at the same time. Stage 2 i�del resul�assume: (1) full groundwater recovery after
Stage 1, and(2) use of three dewate�n�vv�lls installed as part of Stage 1 construction.
Dewatering discharge rates have increased from the previous May 2011 analysis because the
previous model featured deeper sheet piles to the south, which have been replaced with
shallower retaining walls in the updated plans. Shallower«�alls allo«� more ground���ater to flow
underneath, increasing discharge rates.
Discharge rates will decrease with time as the saturated thickness of the aquifer is progressively
reduced by the dewatering effort. However, the pumping test showed that the aquifer would
receive recharge from the nearby Green River under pumping conditions; thereby limiting the
amount that pumping will decrease over time.
The model estimated that the radius of influence of the de«-atering may extend greater than
2,000 feet from the dewatered roadway excavation at 100 days. An increased length of pumpin`�
mav result in a «t-eater radius of influence.
_i-i-�i-"�_��-�:_i,_d,�:��,�.F,iF.� �1-1-�1�9�-UO?
a� �:F�- � p �F �`{' _�l,r-..
Mr. Jiin Guan-e, Senior Vice President `' ����''�`������' ` �""���` �'`��"�
BergerABAM Engineers. Inc.
June 23. 2011
Page 4 of 6
' De��atering S��stem Configurations
For Stage 1 construction around the BVSF bridge excavation, sheet pile cutoff walls are on the
north and west sides; the south side features a shallower retaining wall cutoff wall. For Stage ?
construction, cutoff walls in the form of sheet pile walls will be on the north side of the BNSF
r,
bridge excavation and a shallower retaining wall at the sout�side of the excavation. Stage 2
construction will include removing the sheet pile wail o�t�e ea�t'side under the railroad tracks
for slab construction. Sheet piles were modeled to,a de�th.`f eleva�fon -20 feet, retaining walls
to a depth of 0 foot. Increasing the depth of the she�-��piles o`x,� in i�g,wall may result in a
reduction of dra«�down outside the walls and reduce�e grouf�dwa�diseli�e rates.
.--��J,� � �� �
For the groundwater model, we assigned larga�diam�ter�um�ng v�.�lls in �de the BNSF bridge
excavation. The pumping test demonstra�t�at the�(rea of'i�fli�nce�or a well is extensive in
� � �r. -. ., .
the site soils, so that all dewatering wel��sta`�la�n,� can b�p1a�dY the BNSF bridge
excavation and the soils,.�amping dczwn,to th��BNS�bri�lge`w��lL�ie dewatered in conjunction.
Depending on the CQritractor;s�eans��a�d�net�iods, a itio�l dewatering wells outside of the
BNSF bridge excavati�ma}��r m��not`�ie�'rieede�, Dewatering wells were placed on 50-foot
spacing inside the BNSF`b�idge�e�cav�ion�,If�e�ntractor places the dewatering wells
outside of the BNSF bridge e�ava�Qn/�heetp;iles,it is likely that deeper and/or additional
dewatering wells will be needed`t�reach the�ewatering goal. Our groundwater model �vell
�
design and drawdown contours are�s`�own�,�fn Figures 3 and 4. Dewatering wells may extend as
much as approximately 25 feet below t�ie drawdown goal, depending on the location and well
efficiency. The groundwater model also assumes trenches/sumps will be used in the fine-grained
estuary/overbank soils between approximately elevations 19 and 0 feet. The groundwater model
achieved dewatering goals at Stage 1 ��-ith six wells and Stage 2 with six wells(using three ��ells
from Stage 1). The eaact number of wells w�ill depend on the Contractor's means, methc�ds.
sequencing, and scheduling; the number of dewatering wells could increase or decrease.
DEWATERING RECOMMENDATIONS AND CONCLUSIONS
Our dewatering recommendations remain the same as in the May 2011 Shannon & Wilson
report.
,i-i-,i��iz-���,�_i�a,��.��i,i�„ 21-1-2129?-003
Mr. Jim Guarre, Senior Vice President Sf1�WNON��IVILSON,INC.
BergerABAM Engineers, Inc.
June 23, 2011
Page 5 of 6
Dewatering System
For the soil types encountered and the depth of excavation, large-diameter pumped wells in
conjunction with trenches/sumps appear the most efficient approach to dewaterin�the Strander
excavation. The large-diameter dewatering wells will be used to relieve the pressures and basal
r,
instabilities that may be encountered at depths. Because t e,t�ear-surface soils are fine-grained,
unless an extended period of dewatering(at least o�mp h) o�curs before construction starts,
the fine-grained soils will drain slowly and the Co`�tract�or s�iould b�prepared to encounter
residual groundwater and/or wet soils, which shoula�be draii��ith�s�mps, trenches, and
> > � �
pumps. < : �.\ �..f��
% � � ��
Tv ical Well Desi n /" \\ �
�P g .
�, �
�, �/� �• �, '�.
Pumped wells can be placed on a 50-fo9�sp�in�/�the�NSF�j�ri�xcavation and generally
extend 20 feet below the�kevatiezi d�atering'goal�.a m.ini�n�m o�approximately 70 feet below
ground surface. Our q�odeling placed:d�.�;�ate��g w�11s withi�the BNSF bridge construction
(within the sheet pile��;to ac�i e�dequa,te'�c�epr`�suriz�i�n of the alluvial sands. If dewatering
wells are placed outside�e sh�tpile�the�oi�t,�-actdc will likely need wells to be deeper in depth
and capable of pumping hig�er vo�me�,of vv�ter;`aiid additional wells may be needed. Figures 3 '
and 4 shows a schematic hypoth�ticaT��iell layout used in our groundwater model for Stages 1
and 2, respectively. Dewatering w�ls wil�ely be 12-inch-diameter casings and screens placed
in a 24- to 36-inch-diameter borehole`��ixr analyses assumed highly efficient wells ,
(approximately 80 percent efficient). Lower efficiency wells will require increased depths
and,�or additional wells. �
LI�iITATIONS
This letter was prepared for BergerABAM and the Cities of Renton and Tukwila for specific
application to the site defined in this letter. This study has been prepared in accordance with
generally accepted hydrogeologic methods. No other warranty, express or implied, is made.
Shannon & VVilson, Inc. has prepared the enclosure, "Important Information About Your
GeotechnicaUEnvironmental Report,"to assist ��ou and others in understanding the use and
limitations of our reports.
The geologic and hydrogeologic data obtained indicate subsurface conditions only at the specific
locations and times when the observations were made and only to the depths penetrated. They
�i-i-z i�e�-oo�_i.�.d���ti��ik� �1-1-21?92-003
Mr. Jim Guarre, Senior Vice President SF{ANNC�N F�WiL.SON,iNC.
BergerABAM Engineers, Inc.
June 23, 2011
Page 6 of 6
do not necessarily reflect strata variations that may exist between such locations. The validity of
the dewatering estimates is based in part on assumptions about the stratigraphy and hydraulic
conductivities made by our staff. If subsurface conditions different from those described are
encountered during future explorations or excavations, findings in this letter may require
re-evaluation. Actual permeabilities or hydraulic conductjyities significantly lower or higher
than those assumed in our evaluations will result in s�nif�cai�tly,.lower or higher flows and
� � = �,
drawdown impacts. More refined or accurate estir�'iatespflQow woi�d require additional
subsurface explorations, and pumping tests. `�,/•��� ��,�
Sincerely, � \�`�
� �/
SHANNON & WILSON, INC. �
/^``�
_,� � � \
� �`
Kate E. Stalker, L.G�, \ � �' _ . �
Hydrogeologist \ �
,,.
.
J J=�
. �
,
Larry West, L.H.G., C.E.G. ��� ;' �I
Vice President ��'
KES:JNB:LMW/kes
Enc: Figure l —Vicinity Map
Figure 2 —Site Plan
Figure 3 —Dewatering Groundwater Elevation Contours, Stage 1, 14 Days of Pumping
Figure 4—Dewatering Groundwater Elevation Contours, Stage 2, 14 Days of Pumping
Important Infonnation About Your Geotechnical!Em-ironmental Report
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� LEGEND NOTE Renton and Tukwila,Washington
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� provided by BergerABAM via FTP,
� Scale in Feet received Cr13-2011. SITE PLAN
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June 2011 21-1-21292-003
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a SGeotecnnicel�andEnvironlmentelCons�taMs FIG. 2
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Notes:
Plan View
Contours show groundwater elevation after 14 days of dewatering. Strander Boulevard Extension
Typical dewatering well distribution, actual well placement depends on contractor means, methods Phase II
schedule and dewatering design. Renton and Tukwila,Washington
DEWATERING GROUNDWWATER
ELEVATION CONTOURS
STAGE 1
14 DAYS OF PUMPING
June 2011 21-1-21292-003
SHANNON 8 WILSON, INC FIG. 3
Geotechnical and Environmental Consultants
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Notes:
Plan View Strander Boulevard Extension �
Contours show groundwater elevation after 14 days of dewatering. Phase II ��
Typical dewatering well distribution,actual well placement depends on contractor means, methods Renton and Tukwila,Washington I
schedule and dewatering design. DEWATERING GROUNDWATER I
ELEVATION CONTOURS I
STAGE 2 '
14 DAYS OF PUMPING
June 2011 21-1-21292-003
SHANNON 8�WILSON, INC FIG. 4
Geotechnical and Environmental Consultants
_ SHANNON 8�WILSON, INC. ,attachment to and part ofReport 21-1-21292-003
_ Geotechnical and Environmental Consultants
Date: June 22,201 1
� To: Mr.Jim Guarre
BergerABA'�1 Eneine�rs,]nc.
IMPORTANT INFORMATION ABOUT YOUR GEOTECHNICALIENVIRONMENTAL
REPORT
CONSULTING SERVICES ARE PERFORMED FOR SPECIFIC PURPOSES AND FOR SPECIFIC CLIENTS.
Consultants prepare reports to meet the specific needs of specific individuals. A report prepared for a ci��il engineer may not be
adequate for a construction contractor or even another civil engineer. Unless indicated otherwise,your consultant prepared your report
expressly for you and expressly for the purposes you indicated. No one other than you should apply this report for its intended
purpose without first conferring ���ith the consultant. No party should apply this report for any purpose other than that originally
contemplated without first conferring�vith the consultant.
THE CONSULTANT'S REPORT IS BASED ON PROJECT-SPECIFIC FACTORS.
.a geotechnicalienvironmental report is based on a subsurface exploration plan designed to consider a unique set of project-specific
factors. Depending on the project, these may include: the general nature of the structure and property involved; its size and
configuration; its historical use and practice; the location of the structure on the site and its orientation; other improvements such as
access roads, parking lots, and underground utilities; and the additional risk created by scope-of-service limitations imposed by the
client. To help avoid costly problems, ask the consultant to evaluate how any factors that change subsequent to the date of the report
may affect the recommendations. Unless your consultant indicates otherwise, your report should not be used: (1) �vhen the nature of
the proposed project is changed (for example, if an of�'ice building will be erected instead of a parking garage, or if a refrigerated
�rarehouse will be built instead of an unrefrigerated one, or chemicals are discovered on or near the site);(2)when the size, elevation.
or configuration of the proposed project is altered; (3)when the location or orientation of the proposed project is modified; (4) when
there is a change of ownership; or(5) for application to an adjacent site. Consultants cannot accept responsibility for problems that
may occur if they are not consulted after factors which were considered in the development of the report have changed.
SUBSURFACE CONDITIONS CAN CHANGE.
Subsurface conditions may be affected as a result of natural processes or human activity. Because a geotechnicaUenvironmental report
i, based on conditions that existed at the time of subsurface exploration, construction decisions should not be based on a report���hose
adequacy may have been affected by time. Ask the consultant to advise if additional tests are desirable before construction starts; for
e�ample,groundwater conditions commonly vary seasonally.
Construction operations at or adjacent to the site and natural events such as floods,earthquakes,or groundwater fluctuations may also
affect subsurface conditions and,thus,the continuing adequacy of a geotechnical/environmental report. The consultant should be kept
apprised of any such events,and should be consulted to determine if additional tests are necessary.
MOST RECOMMENDATIONS ARE PROFESSIONAL JUDGMENTS.
Site exploration and testing identifies actual surface and subsurface conditions only at those points«�here samples are taken. The data
«ere extrapolated by your consultant,who then applied judgment to render an opinion about overall subsurface conditions. The actual
interface between materials may be far more gradual or abrupt than your report indicates. Actual conditions in areas not sampled may
differ from those predicted in your report. While nothing can be done to prevent such situations, you and your consultant can work
together to help reduce their impacts. Retaining your consultant to observe subsurface construction operations can be particularly
beneficial in thi,respect.
Pa��c I ��f? I ?�11 1
A REPORT'S CONCLUSIONS ARE PRELIMINARY.
The conclusions contained in your consultant's report are preliminary because they must be based on the assumption that conditions
revealed through selective exploratorv sampling are indicative of actual conditions throughout a site. Actual subsurface conditions can
be discerned only during earthwork; therefore, you should retain your consultant to observe actual conditions and to provide
conclusions. Only the consultant who prepared the report is full}� familiar �rith the background information needed to determine
whether or not the report's recommendations based on those conclusions are valid and whether or not the contractor is abiding by
applicable recommendations. The consultant who developed your report cannot assume responsibility or liability for the adequacy of
the report's recommendations if another party is retained to observe construction.
THE CONSULTANT'S REPORT IS SUBJECT TO MISINTERPRETATION.
Costly problems can occur when other design professionals develop their plans based on misinterpretation of a
geotechnicaUenvironmental report. To help avoid these problems,the consultant should be retained to work��-ith other project design
professionals to explain relevant geotechnical,geological, hydrogeological,and environmental findings,and to revie�v the adeyuacy of
their plans and specifications relative to these issues.
BORING LOGS ANDIOR MONITORING WELL DATA SHOULD NOT BE SEPARATED FROM THE REPORT.
Final boring logs developed by the consultant are based upon interpretation of field logs (assembled by site personnel), field test
results, and laboratory and/or office evaluation of field samples and data. Only final boring logs and data are customarily included in
geotechnical/environmental reports. These final logs should not,under any circumstances,be redrawn for inclusion in architectural or
other design dra���ings,because drafters may commit errors or omissions in the transfer process.
To reduce the likelihood of boring log or monitoring well misinterpretation,contractors should be given ready access to the complete
geotechnical engineering/environmental report prepared or authorized for their use. If access is provided only to the report prepared
for you, you should advise contractors of the report's ]imitations, assuming that a contractor was not one of the specific persons for
whom the report was prepared, and that developing construction cost estimates�vas not one of the specific purposes for which it ��•as
prepared. R�hile a contractor may gain important knowledge from a report prepared for another party, the contractor should di scuss
the report with your consultant and perform the additional or alternative work believed necessary to obtain the data specifically
appropriate for construction cost estimating purposes. Some clients hold the mistaken impression that simply disclaiming
responsibility for the accuracy of subsurface information always insulates them from attendant liability. Providing the best available
information to contractors helps prevent costly construction problems and the adversarial attitudes that aggravate them to a
disproportionate scale.
READ RESPONSIBILITY CLAUSES CLOSELY.
Because geotechnical,�environmental engineering is based extensiveh�on judgment and opinion, it is far less exact than other design
disciplines. This situation has resulted in wfiolly unwarranted claims being lodged against consultants. To help prevent this problem,
consultants have developed a number of clauses for use in their contracts, reports and other documents. These responsibility clauses
are not exculpatory clauses designed to transfer the consultant's liabilities to other parties; rather, they are definitive clauses that
identify where the consultant's responsibilities begin and end. Their use helps all parties invoh-ed recognize their individual
responsibilities and take appropriate action. Some of these definitive clauses are likely to appear in your report, and you are
encouraged to read them closely. Your consultant�1 ill be pleased to�ive full and frank ans���ers to your questions.
The preceding paragraphs are based oi� infonnatio��provided by the
ASFEi�Association of Enaineering Firms Practicing in the Geosciences, Silcer Spring. Maryland
Page?of 2 I�201 1