HomeMy WebLinkAboutPLAT OF EAGLE RIDGE <S, �
4205 148th Ave.N.E.Suite 200
CORE Bellevue,Washington 98007
425.885.7877 Fox 425.885.7963
DESIGN
PLAT OF EAGLE RIDGE
RENTON, WASHINGTON
for
PACIFIC HUTS AND CASTLES, INC.
STORM DRAINAGE
CALCULATIONS
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Project No.: 99102 �� =r
Prepared by: Brennan P. Taylor, P.E. y
Approved by: David E. Cayton, P.E. o
Date: October 2000
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ENGINEERING • PLANNING SURVEYING
PLAT OF EAGLE RIDGE
RENTON,WASHINGTON
STORM DRAINAGE
CALCULATIONS
TABLE OF CONTENTS
Section
I. Introduction
II. Offsite Analysis
A. Upstream Drainage
B. On-Site Drainage
C. Downstream Drainage
III. Flow Control and Water Quality Analysis and Design
A. Hydraulic Analysis
B. Detention Routing Calculations
C. Water Quality Calculations
IV. Conveyance System Analysis and Design
V. Erosion Control Calculations
I. Introduction
The Eagle Ridge project is located in the southeast quadrant of the intersection of SE
128'h Street (NE 40'St.) and 148"Avenue SE in Renton, Washington. This parcel is
approximately 4.2 acres and was recently annexed to the City of Renton in the
Maplewood Annexation. An existing asphalt contractor occupies the adjacent property
east of the site. The south adjacent parcel includes the proposed Plat of Maplewood. See
Figure 1 for vicinity map.
The majority of the site is currently young alder saplings, Douglas fir, western hemlock
and other trees. The site generally slopes to the southwest at approximately 5%. No
wetlands exist on-site.
The proposed improvements include the construction of 17 single family dwellings with
related grading, utility, and road construction. Onsite generated storm water runoff will
be directed to a combination wetpond/detention pond in the southwest corner of the site.
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a►. It CORE DESIGN NO. 99102
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H. Offsite Analysis
A. UPSTREAM DRAINAGE
There are no upstream tributary areas draining onto the site. Runoff from SE 128" Street
right-of-way drains to the south roadway ditch and flows west, off-site. This roadside
ditch is drained to the southwest into a separate drainage basin via drainage ditches and
culverts. Runoff from the adjacent asphalt company flows south onto the Maplewood
property. See Figure 2 for Existing Drainage Basin Map.
B. ON-SITE DRAINAGE
Stormwater runoff on-site generally flows in a southwesterly direction over forested
terrain to the 148t'Avenue SE right-of-way. 148'Ave SE is currently under construction
as part of the Maplewood Property project. There are no existing channels on-site all
existing flows are sheet flow to the southwest.
C. DOWNSTREAM DRAINAGE
Runoff from the project drains onto the Maplewood Property site. The Maplewood
Property project will improve 148 h Ave NE on the west side of the site and install a storm
drainage conveyance system which accept runoff from the Eagle Ridge project. A 12"
pipe form the new 148'Ave SE conveyance system will be stubbed to the southwest
corner of the site (Inlet 71A of the Maplewood Property project). As mentioned earlier,
the Maplewood Property is currently under construction.
The storm water runoff from the site is conveyed approximately 3500 feet through the
newly constructed storm drainage system of the Maplewood Property. The Maplewood
storm system discharges to a pair of 24 culverts located immediately south of the
intersection of 148`h Ave SE and SE 136"' St. The twin 24" culverts convey storm water
to a grassy swale which runs southeast and then south for approximately 700
II. Offsite Analysis (cont.)
C. DOWNSTREAM DRAINAGE (cont.)
feet until it reaches a 30" CMP Pipe on the north side of the Plat of Briar Hills. This 30"
CMP pipe directs the flows through the Plat of Briar Hills at varying slopes of 0.6 to
3.8% (see Figure 3 for Downstream Drainage Map). There is one "off-line"detention
pond approximately 4900 feet downstream which is thoroughly grassed and shows no
sign of recent inundation. The 30"inch CMP ultimately drains to another"off-line"
detention pond approximately 5800 feet downstream near the south end of Briar Hills.
This detention pond shows evidence of recently detained flows filling up the bottom 2
feet of the pond (the pond has seven feet of available storage). This pond releases to a
rip-rapped discharge at the top of a natural drainage ravine. The ravine eventually
discharges to the Cedar River approximately one and a half miles downstream of the
subject property.
The downstream flow path has no apparent signs of flooding or extensive erosion.
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III. Flow Control and Water Quality Analysis and Design
A. Hydraulic Analysis
The drainage analysis was modeled using the King County Runoff Time Series software.
The onsite soils are Alderwood, hydrologic group C and KCRTS group Till. See soils
map included in Section 3 Offsite Analysis of this report. The site is located in the Sea-
Tac rainfall region with a location scale factor of 1.0.
Existing Conditions
The site is 4.21 Acres in size. The existing ground cover is till-forest. The following
information was used for generating time series and flow frequencies.
EXISTING CONDITIONS Total Area=4.21 acres
99102ex
GROUND COVER AREA acre
Till-Forest 4.21
Onsite existing conditions flow frequency analysis:
PEAK FLOW RETURN
CFS PERIOD
0.340 100 year
0.315 50 year
0.265 25 year
0.204 10 year
0.196 5 year
0.172 3 year
0.117 2 year
0.072 1.3 year
0.007 1.1 year
/S.E. 128TH ST
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CORE DESIGN NO. 99102
Flow Frequency Analysis
Time Series File:99102ex.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0 .265 2 2/09/01 18:00 0.340 1 100.00 0.990
0.072 7 1/06/02 3 :00 0.265 2 25.00 0.960
0.196 4 2/28/03 3 :00 0.204 3 10.00 0.900
0.007 8 3/24/04 20:00 0.196 4 5 .00 0.800
0.117 6 1/05/05 8:00 0.172 5 3 .00 0.667
0.204 3 1/18/06 21:00 0.117 6 2.00 0.500
0.172 5 11/24/06 4 :00 0.072 7 1.30 0.231
0.340 1 1/09/08 9:00 0.007 8 1.10 0.091
Computed Peaks 0.315 50.00 0.980
SHEET NO. 11
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3.2.2 KCRTS/RUNOFF FILES METHOD--GENERATING TIME SERIES
TABLE 3.2-2.B EQUIVALENCEBETWEEN SCS SOIL TYPES AND KCRTS SOIL TYPES
SCS Soil Type SCS KCRTS Soil Notes
Hydrologic Group
Soil Group
Iderwood A B A C A D C Till
Arents,Alderwood Material (AmB, AmC) C Till
Arents, Everett Material (An) B Outwash 1
Beausite (BeC, BeD, BeF) C Till 2
Bellingham (Bh) D Till 3
Briscot (Br) D Till 3
Buckley (Bu) D Till 4
Earlmont(Ea) D Till 3
Edgewick (Ed) C Till 3
Everett(EvB, EvC, EvD, EwC) A/B Outwash 1
Indianola (InC, InA, InD) A Outwash 1
Kitsap (KpB, KpC, KpD) C Till
Klaus (KsC) C Outwash 1
Neilton (NeC) A Outwash 1
Newberg (Ng) B Till 3
Nooksack (Nk) C Till 3
Norma (No) D Till 3
Orcas (Or) D Wetland
Oridia (Os) D Till 3
Ovall (OvC, OvD, OvF) C Till 2
Pilchuck (Pc) C Till 3
Puget (Pu) D Till 3
Puyallup (Py) B Till 3
Ragnar(RaC, RaD, RaC, RaE) B Outwash 1
Renton (Re) D Till 3
Sala] (Sa) C Till 3
Sammamish (Sh) D Till 3
Seattle (Sk) D Wetland
Shalcar(Sm) D Till 3
Si (Sn) C Till 3
Snohomish (So, Sr) D Till 3
Sultan (Su) C Till 3
Tukwila (Tu) D Till 3
Woodinville (Wo) D Till 3
Notes.
1. Where outwash soils are saturated or underlain at shallow depth (<5 feet) by glacial till, they should
be treated as till soils.
2. These are bedrock soils, but calibration of HSPF by King County DNR shows bedrock soils to have
similar hydrologic response to till soils.
3. These are alluvial soils,some of which are underlain by glacial till or have a seasonally high water
table. In the absence of detailed study,these soils should be treated as till soils.
4. Buckley soils are formed on the low-permeability Osceola mudflow. Hydrologic response is
assumed to be similar to that of till soils.
1998 Surface Water Design Manual 9/1/98
3-25
S,; CTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
KCRTS Land Cover Types
KCRTS supports four land cover types:forest,pasture, grass, and impervious. 77hese cover types shall be
applied as specified in Table 3.2.2.0(below).
TABLE 3.2.2.0 KCRTS COVER GROUPS AND AREAS OF APPLICATION
KCRTS APPLICATION
Cover Group Predevelo ment
P Post-Development
Forest All forest/shrub cover, irrespective of All permanent(e.g., protected by
age. covenant or SAC)designation) onsite
forest/shrub cover, irrespective of age,
planted at densities sufficient to ensure
80%+canopy cover within 5 years.
Pasture All grassland, pasture land, lawns, and Unprotected forest in rural residential
cultivated or cleared areas, except for development may be considered half
lawns in redevelopment areas with pasture, half grass.
predevelopment densities in excess of
4 DU/GA..
Grass Lawns in redevelopment areas with All post-development grassland7andpredevelopment densities in excess of landscaping and all onsite foresnd
4 DU/GA.. not protected by covenant or SASA
designation (except in rural areas as
noted above).
Wetland All delineated wetland areas (except All delineated wetland areas(except
cultivated/drained farmland). cultivated/drained farmland).
Impervious(') All impervious surfaces, including All impervious surfaces, including
heavily compacted gravel and dirt compacted gravel and dirt roads, parking
roads, parking areas, etc., and open areas, etc., and open water bodies,
water bodies (ponds and lakes). including onsite detention and water
7
quality ponds.
c>> Impervious acreage used in KCRTS computations should be the effective impervious area
(EIA). This is the gross impervious area multiplied by the effective impervious fraction (see
Table 3.2.2.E, p. 3-28). Non-effective impervious areas are considered the same as the
surrounding pervious land cover.
The following four factors were considered in specifying the above land cover types to be used in
hydrologic analysis with KCRTS:
• Cover types are applied to anticipate ultimate land use conditions. For example, probable clearing
of woodland after development is nominally complete suggests that the post-development land use be,
specified as grassland(either pasture or grass)unless the forest cover is protected by covenant.
• In areas of redevelopment,there are often significant changes between the predevelopment and post-
development efficiencies of the drainage system. For example,in conversion of low density
residential areas to higher density land use, impervious areas prior to redevelopment may not be
efficiently connected to a drainage system(e.g., downspouts draining to splash blocks, ditched instead
of piped roadway systems). These problems are addressed by defining an"effective impervious
fraction"for existing impervious areas and by generally requiring predevelopment grasslands to be
modeled as pasture land.
9/1/98 3-26 1998 Surface Water Design Manual
.5ECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.2.A RAINFALL REGIONS AND REGIONAL SCALE FACTORS
ST 1.0/
ST 1.1 ST 1.0 LA 0.8 LA 0.9 LA 1.0 LA 1.2
'
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KINO COUNTY
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Rainfall Re
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Regional Scale Factors LA 0.9
u Incorporated Area LA 1.0 LA 1.2
—c:z River/Lake
Major Road
9/l/98 3-22 1998 Surface Water Design Manual
Developed Conditions
The developed site will consist of 17 single family residences with associated roadway
and utilities
The impervious area was calculated using the criteria in the 1998 King County Surface
Water Design Manual page 3-27 which states that 4000sf of impervious per lot should be
assumed. All other impervious surfaces were measured by a planimeter.
D. Impervious Area Delineation
Onsite road and sidewalk 28,960 sf
Impervious area of lots 4000sf*17 lots 68,000 sf
Total impervious area 96,960 2.22 acres
The input used for the KCRTS analysis is summarized in the table below:
DEVELOPED CONDITIONS Total Area=4.21 acres
99102dev
GROUND COVER AREA acre
Till-Grass (Landscaping) 1.99
Impervious 2.22
Onsite developed conditions flow frequency analysis:
PEAK FLOW RETURN
CFS PERIOD
1.47 100 year
1.27 50 year
0.865 25 year
0.857 10 year
0.758 5 year
0.716 3 year
0.716 2 year
0.590 1.3 year
F-- 0.565 1.1 year
Flow Frequency Analysis
Time Series File:99102dev.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
FlowRate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.716 5 2/09/01 2 :00 1.47 1 100 .00 0.990
0.565 8 1/05/02 16:00 0.865 2 25 .00 0.960
0. 865 2 2/27/03 7:00 0 .857 3 10 .00 0 .900
0.590 7 8/26/04 2 :00 0.758 4 5.00 0 .800
0.716 6 10/28/04 16:00 0.716 5 3 . 00 0.667
0.758 4 1118106 16:00 0.716 6 2 . 00 0.500
0.857 3 10/26/06 0:00 0.590 7 1.30 0.231
1.47 1 1/09/08 6:00 0.565 8 1.10 0.091
Computed Peaks 1.27 50.00 0.980
B. Detention Routing Calculations
The detention/water quality facility will be a combination water quality and detention
pond. Per the hearing examiner's conditions, the facility will be designed according to
the Sept. 1998 KCSWDM instead of the 1990 KCSWDM that is normally required in the
City of Renton. Since the level of protection was not specified by the hearing examiner,
the detention portion of the pond will be sized according to a Level 1 Analysis
(Conveyance Protection)using the KCRTS software. The Level 1 Analysis results in a
276% increase in detention volume from the 1990 KCSWM methods used in the
preliminary storm drainage calculations.
Sizing the pond by the 1998 KCSWDM and KCRTS Computer Software Reference
Manual, the 2 and 10 year flows are matched. Since the KCRTS software is not very user
friendly when custom stage storage relationships are used, the actual stage storage
relationship was approximated with a trapezoidal pond having a similar stage storage
relationship. The attached table shows the relationship of the Actual pond to the KCRTS
trapezoidal pond.
The flows to match for the 2 year and 10 year flow are 0.293 cfs and 0.505 cfs
respectively. The following table summarizes the routing results.
ROUTING RESULTS 2 year storm 10 year storm
Qp allowable release cfs 99102 re 0.12 0.20
Qp into pond cfs 99102dev 0.716 0.857
Qp released from the design pond 0.0.12 0.20
cfs 99102out
Pond live storage required CF 17,445 27,016
The control structure has 2 orifices to meet the detention criteria to match the 2 and 10-
year storm events. The first orifice has a diameter of 1.64 inches. The second orifice is at
a stage of 2.70 feet with a diameter of 1.54 inches.
The primary overflow for the pond is the riser pipe within the control structure. The
KCRTS program calculates the overflow over the riser when routing the hydrographs
through the detention facility. This is evidenced by the fact that the riser stage is 3.7 feet
and the maximum stage of the detention pond 3.86 feet. This translates to a maximum
water surface of 442.86.
The secondary overflow for the pond will be via a jailhouse weir. The overflow elevation
for the 100-year developed flow will be calculated assuming there is a blockage in the
control structure. The jailhouse weir can be analyzed using the standard weir equation:
Q=9.739DH312
where Q =flow (1.47 cfs)
D =riser diameter(4 feet)
H=head above weir (ft)
The head required to drive this flow is 0.11 feet. The CB structure is placed at the
overflow elevation of 442.86. The secondary overflow elevation is therefore 442.86 +
0.11 =442.97.
In addition to the secondary emergency overflow, the City requires an emergency
overflow spillway. The primary overflow elevation is EL 442.86 (shown as design water
surface on the plans). The secondary overflow flow elevation is EL 442.97 (shown as
overflow elevation on the plans) which will also be the top of the rip-rap of the
emergency overflow spillway. The required spillway length is calculated below.
L=(QIOW(3.21H3/2)) - (2.4H)
Qioo= 1.47 cfs (tributary to pond)
Assume H=0.2'(minimum value)
L= (1.47/(3.21(0.2)3/2)) - (2.4(0.2)) =4.64'
The minimum length of overflow spillways is 6 feet.
The emergency overflow elevation of the spillway is EL 442.97 + 0.2' =EL 443.17
POND
VOLUME CALCULATIONS (LIVE STORAGE)
CORE#99102
BUTTAR PROPERTY
ELEVATION- INCREMENTALl TOTAL
VOLUME VOLUME VOL
SF CF CF GCF)
439.0 5080 0 O
5,776
440.0 6472 5,776
l" a 15,232 - ,n. ;
442.0 8760 21,008 20 58Q-
9 400 .
443.0 10040 30,408
Is
444.0 11420,; R 41,138
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Retention/Detention Facility
Type of Facility: Detention Pond
Side Slope: 3 .60 H:1V
Pond Bottom Length: 85.09 ft
Pond Bottom Width: 60.34 ft
Pond Bottom Area: 5134. sq. ft
Top Area at 1 ft. FB: 11201. sq. ft
0.257 acres
Effective Storage Depth: 3 .70 ft
Stage 0 Elevation: 439.00 ft
Storage Volume: 27040. cu. ft
0.621 ac-ft
Riser Head: 3 .70 ft
Riser Diameter: 18.00 inches
Number of orifices: 2
Full Head Pipe
Orifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
1 0.00 1.64 0.140
2 2.70 1.54 0.064 4.0
Top Notch Weir: None
Outflow Rating Curve: None
Stage Elevation Storage Discharge Percolation Surf Area
(ft) (ft) (cu. ft) (ac-ft) (cfs) (cfs) (sq. ft)
0.00 439.00 0. 0.000 0.000 0.00 5134.
0.02 439.02 103 . 0.002 0.010 0.00 5155.
0.03 439.03 155. 0.004 0.013 0.00 5166.
0.05 439.05 258. 0.006 0.016 0.00 5187.
0.07 439.07 362. 0.008 0.019 0.00 5208.
0.09 439.09 466. 0.011 0.021 0.00 5229.
0.10 439.10 519. 0.012 0.023 0.00 5240.
0.12 439.12 624. 0.014 0.025 0.00 5261.
0.14 439.14 729. 0.017 0.027 0.00 5282.
0.15 439.15 782. 0.018 0.029 0.00 5293.
0.25 439.25 1317. 0.030 0.037 0.00 5399.
0.35 439.35 1862 . 0.043 0.043 0.00 5507.
0.45 439.45 2418. 0.056 0.049 0.00 5616.
0.55 439.55 2985. 0.069 0.054 0.00 5726.
0.65 439.65 3563 . 0.082 0.059 0. 00 5837.
0.75 439.75 4153 . 0.095 0.063 0.00 5949.
0.85 439.85 4753 . 0.109 0.067 0.00 6062 .
0.95 439.95 5365. 0.123 0.071 0.00 6176.
1.05 440.05 5988. 0.137 0.075 0.00 6291.
1.15 440.15 6623 . 0.152 0.078 0.00 6407.
1.25 440.25 7270. 0.167 0.081 0.00 6524.
1.35 440.35 7928. 0.182 0.085 0.00 6643 .
1.45 440.45 8598. 0.197 0.088 0.00 6762.
1.55 440.55 9281. 0 .213 0.091 0.00 6882 .
1.65 440.65 9975. 0.229 0.094 0.00 7003.
1.75 440.75 10681. 0.245 0.096 0.00 7126.
1.85 440.85 11400. 0.262 0.099 0.00 7249.
1.95 440.95 12131. 0.278 0.102 0.00 7373.
2.05 441.05 12875. 0.296 0.104 0.00 7499.
2.15 441.15 13631. 0.313 0.107 0.00 7625.
2 .25 441.25 14400. 0.331 0.109 0.00 7753 .
2.35 441.35 15182. 0.349 0.112 0.00 7881.
2.45 441.45 15976. 0.367 0.114 0.00 8011.
2 .55 441.55 16784. 0.385 0.116 0.00 8142.
2 .65 441.65 17605. 0.404 0.119 0.00 8273 .
2 .70 441.70 18020. 0.414 0.120 0.00 8340.
2 .72 441.72 18187. 0.418 0.120 0.00 8366.
2 .73 441.73 18271. 0.419 0.122 0 .00 8379.
2 .75 441.75 18438. 0.423 0.125 0.00 8406.
2 .76 441.76 18523 . 0.425 0.129 0.00 8419.
2 .78 441.78 18691. 0.429 0.133 0.00 8446.
2 .80 441.80 18860. 0.433 0.139 0.00 8473 .
2 .81 441.81 18945. 0.435 0.144 0.00 8486.
2 .83 441.83 19115. 0.439 0.145 0.00 8513.
2 .84 441.84 19200. 0.441 0. 147 0.00 8526.
2.94 441.94 20060. 0.461 0.157 0.00 8661.
3.04 442 .04 20933 . 0.481 0.165 0.00 8797.
3.14 442 .14 21819. 0.501 0.172 0.00 8933.
3 .24 442 .24 22719. 0.522 0.178 0 .00 9071.
3 .34 442 .34 23633 . 0.543 0.185 0.00 9210.
3 .44 442.44 24561. 0.564 0.190 0.00 9350.
3 .54 442 .54 25503 . 0.585 0.196 0.00 9491.
3 .64 442.64 26460. 0.607 0.201 0.00 9633 .
3.70 442 .70 27040. 0.621 0.204 0.00 9718.
3 .80 442 .80 28019. 0.643 0.671 0.00 9862 .
3 .90 442 .90 29013 . 0.666 1.520 0.00 10007.
4.00 443.00 30021. 0.689 2 .620 0.00 10152.
4.10 443 .10 31043 . 0.713 3 .920 0.00 10299.
4.20 443 .20 32080. 0.736 5.390 0.00 10447.
4 .30 443 .30 33133. 0.761 6.820 0.00 10596.
4.40 443 .40 34200. 0.785 7.360 0.00 10745.
4.50 443 .50 35282 . 0.810 7.850 0.00 10896.
4.60 443 .60 36379. 0.835 8.320 0.00 11048.
4.70 443 .70 37491. 0.861 8.760 0.00 11201.
4.80 443 .80 38619. 0.887 9.180 0.00 11355.
4.90 443.90 39762 . 0.913 9.580 0.00 11510.
5.00 444.00 40921. 0.939 9.960 0.00 11666.
5.10 444 .10 42096. 0.966 10.330 0.00 11823 .
5.20 444.20 43286. 0.994 10.690 0.00 11981.
5.30 444.30 44492 . 1.021 11.030 0.00 12140.
5.40 444.40 45714. 1.049 11.370 0.00 12300.
5.50 444.50 46952. 1.078 11.690 0.00 12462 .
5.60 444 .60 48206. 1.107 12.010 0.00 12624.
5.70 444 .70 49477. 1.136 12 .320 0.00 12787.
Hyd Inflow Outflow Peak Storage
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 1.47 ******* 1.18 3 .86 442 .86 28616. 0.657
2 0.72 ******* 0.54 3 .77 442.77 27734. 0.637
3 0.72 0.20 0.20 3 .70 442.70 27016. 0.620
4 0.76 ******* 0. 19 3 .46 442 .46 24768 . 0.569
5 0.86 ******* 0. 19 3 .40 442.40 24195. 0.555
6 0.45 0.12 0.12 2 .63 441.63 17445. 0.400
7 0.56 ******* 0.10 1.87 440.87 11553 . 0.265
8 0.59 ******* 0.08 1.30 440.30 7589. 0.174
----------------------------------
Route Time Series through Facility
Inflow Time Series File:99102dev.tsf
Outflow Time Series File:rdout
Inflow/Outflow Analysis
Peak Inflow Discharge: 1.47 CFS at 6:00 on Jan 9 in Year 8
Peak Outflow Discharge: 1.18 CFS at 9:00 on Jan 9 in Year 8
Peak Reservoir Stage: 3 .86 Ft
Peak Reservoir Elev: 442 .86 Ft
Peak Reservoir Storage: 28616. Cu-Ft
0.657 Ac-Ft
Flow Frequency Analysis
Time Series File:rdout.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
FlowRate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
0.535 2 2/09/01 15:00 1.18 3 .86 1 100.00 0.990
0.100 7 12/28/01 17:00 0.535 3 .77 2 25.00 0.960
0.188 5 2/28/03 7:00 0.204 3 .70 3 10.00 0.900
0.083 8 8/26/04 6:00 0.191 3.46 4 5.00 0.800
0.118 6 1/05/05 16:00 0.188 3 .40 5 3 .00 0.667
0.191 4 1/18/06 23 :00 0.118 2 .63 6 2 .00 0.500
0.204 3 11/24/06 8 :00 0.100 1.87 7 1.30 0.231
1.18 1 1109108 9:00 0.083 1.30 8 1.10 0.091
Computed Peaks 0.965 3 .83 50.00 0.980
C. Water Quality Volume Calculations
Based on the location of the site, "Basic Water Quality Treatment' is required for sizing
the wetpond. The required volume of dead storage will be designed per KCSWDM
Section 6.4.1.1. The following variables were used in the calculation:
Volume Factor(f) = 3
Rainfall =0.039 feet or 0.47 inches
Where A;= area of impervious surface=2.22 Acres =96703.2 sf
Atg= area of till soil covered with grass= 1.99 Acres = 86684.4 sf.
Vr=[0.9A;+ 0.25Atg] x(R/12)
Vr=[(0.9)(96703.2) + (0.25)(86684.4)]0.039 =4239.5 CF
Vb =f*Vr=3(4239.5) = 12,718 CF
The volume provided is 13,270 cubic feet. See the volume calculation sheet on the next
page.
4
POND
VOLUME CALCULATIONS (DEAD STORAGE)
CORE# 99102
BUTTAR PROPERTY
ELEVATION AREA INCREMENTAL TOTAL
CELL1&2) VOLUME VOLUME
SF CF CF
434.0 516 0
13,270
439.0 4792 13,270
IV. Conveyance Calculations
The proposed conveyance system performance was analyzed using the rational method.
The system was modelled using the 25 year and 100 year design storm events. The
subbasins used to calculate the runoff contributing to each structure are shown on the
attached map. Runoff coefficient values for each subbasin were selected based on the
developed characteristics of each individual area, impervious pavement (C=0.90) or lot
areas (C=0.60).
The attached Storm Conveyance System Design spreadsheets compute tributary flows
using the rational method as discussed previously and present a summary of pipe capacity
flows. The tributary flows were inserted into the attached Backwater Calculations
spreadsheets to calculated the headwater elevation at each structure. The last column in
the spreadsheets (untitled)reflects the difference between each structure rim elevation
and the calculated headwater elevation at that structure. Per attached spreadsheets, all
pipe segments have sufficient capacity to convey and contain the 25 year and 100 year
storm events, per Core Requirements#4, 1998 KCSWDM.
NW 1/4, NW 1/4, SEC. 14, 1 W t'• L3 N., Muc. a c., rr.m.
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li 1 . I• ,1 1 1\ CONVEYANCE SYSTEM
4 1 I 1``t BASIN MAP 74
EAGLE RIDGE
CORE DESIGN NO. 99102 l
--
Z
�`liii.a.�' �xx:.��'i�;..TT�i77��i..EE',(��':..i(�'� �i`���.aa�i�.�ji'`{.���i i[�.s�i..�: iii '.'i '..! i:''�1:�.,Tiii`iE'iEE'E'i`i`i
;.... ....... l.l.•1•.1'� (3v ::f3.i. .���Il\:::: ::..... LOCATION: KING COUNTY 24-HR RAINFALL: 3.46 INCHES
JOB NAME: EAGLE RIDGE JOB NUMBER: 99102 PREPARED BY: DEC DESIGN STORM: 25 YEAR •
. ........ . .
TRi$1tTARY:::E:i.i:iipd;:;i`;::ii.isFiPIE;.:....::i:P.IAE.:::.:iiiYtPE:::i:;�!G`4i7•�-:::::'f11AVE#,.....:.:.:. i8 i.' i�a!ss5
:.:.:::.:::.:.:.:.:.:.:.:..:.:.:.:.:.:.:.:.:.:.:.:.::.:.:::.:.:.:.:.:.:.:.:..:.:.:.:.:.:.:..:.:.:.:.:.:.:.:.:.::.:.:.:.:.:.:.......:.:.....:.:.::.:............................:.:.:.......................
.ii�:�1!E SE��IN��N7!'ii:iiiiiiii°��•�°'i i ii:::':OirkFtC���N��::�:: "�° �i�i' ::.:�:;o:"E?:.:?;`:':' i.:.:`':':''.''.':i :::::,: :;::: ::: ,:::i:5:::: °`°�'i ::::i:fii:i:iii`;i
........ .;:SLOPE:
.FR. M..: .;. .......:.:C c3t3:SY.ii:;:`•.:::: ...:•..... .;.;.:E4.C)... E`(R11NUT�Sjpi.iii�+1/BR)i`E: E iiiiYC33•S)....i;°i.;:.;:a::::::;....tIiYCBESkE (PERCENT).i:fiFEEF} ;:(ETdEC). :fMgvtf77CS)i (CFS}i (BTI&CC:} (pEHCENTI i
10 9 0.48 0.60 0.29 0.29 10.00 2.06 0.59 0.012 12 7.0 39 6.57 1 0.10 10.21 13.00 5.8%
9 6 0.08 0.90 0.07 0.36 10.10 2.05 0.74 0.012 12 2.0 28 4.62 0.10 5.46 6.95 13.5%
8 7 1.06 0.60 0.64 0.64 10.00 2.06 1.31 0.012 12 0.5 55 3.44 0.27 2.73 3.47 48.0%
7 6 0.87 0.60 0.52 1.161 10.27 2.03 2.35 0.012 12 5.4 88 9.59 0.15 8.971 11.42 26.2%
6 5 0.46 0.60 0.28 1.79 10.42 2.01 3.60 0.012 12 0.5 52 3.47 0.25 2.73 3.47 131.9%
5 5A 0.12 0.90 0.11 1.90 10.67 1.98 3.76 0.012 12 9.0 58 13.05 0.07 11.58 14.74 32.5
4A 4 0.08 0.90 0.07 0.07 10.00 2.06 0.15 0.012 12 2.0 28 2.64 0.18 5.46 6.95 2.7%
4 4B 0.081 0.90 0.07 0.14 10.18 2.04 0.29 0.012 1 12 1 2.0 72 3.51 0.34 5.46 6.95 5.4%
11/10/00 CORE DESIGN,INC. PAGE 1
J...............�lu�;. .,..fJ.,... l l ............ LOCATION: KING COUNTY 24-HRRAINFALL: 3.95 INCHES
JOB NAME: EAGLE RIDGE JOB NUMBER: 99102 PREPARED BY: DEC DESIGN STORM: 100 YEAR
s c}F i'::IinliuFaGc':
.
j�K;!iY�.?1,...,.?t►,...,.,.,.��J...............:...............................................................................T....... Y...•.............•..........R)�E,...,..,.,.p!hl.,.,...Nt E. .�C trnf.......'f .v£v......•... �.
.. ........ ..
e............x.............. ...............#'l'.... Gi1:B�tMIY.:.:.:
tE'.? iiiAilLAiiiiii5i ll ......'
g.. I. N ii o CI N3.ii iiiiiii'AR�iI::;:;5 ;. 'i' `.':'''ii' .i iiiiiii°�"''.Gi;i;i °' :; ```i``'```?ii:i'i`'`'`:`'``?caNC.....iNtr Ns11i.....F..P....�..G......�'..•:::.:.:.:.:.:.:.:.:.:.::::.:G...:......:.:..:.::.:.:.:.:.:::::::.:u:.:Q:.::.:.:.:.:.;.:.;.;....:.:.:.:.:.:.:.:.:..:......�.nW.;.;..:M?4?gNtNC�S;..binnfETE#;;:SLOY�:::::4�NG7N::�'�QC!tk..;.:.;l7ME:.:.:..;. EF�fii,LJ:::w. .:.::;�4 nGT
FROM::::::::T41::::::::::::1:AC3L1cS}::::::::::::::.:.:...:.:.:.:.:..:.:.:.:E.....:.:.:.::.:(A:.: ):.::.1 !NIfT65):..:.:(FN/SRj...........t3'S::::::::::::::;��q�,;::::::::: t�iC9E ERCENT: •.....
............................ ....... ........ ...........,.,.,,.,.,.. ,3..... X?.........5}'. (Y.,......,) :.L:FEET}., ..(F.TSkC) ..4!11M37i';5):.:':(CFS):.'; Y1!'TI&ff;}
10 9 0.48 0.60 0.29 0.29 10.00 2.42 0.70 0.012 12 7.0 39 7.02 0.09 10.21 13.00 6.8%
9 6 0.08 0.90 0.07 0.36 10.09 2.40 0.87 0.012 12 2.0 28 4.83 0.10 5.46 6.95 15.8%
8 7 1.06 0.60 0.64 0.64 10.00 2.42 1.54 0.012 12 0.5 55 3.58 0.26 2.73 3.47 56.3%
7 6 0.871 0.60 0.52 1.161 10.26 2.38 2.75 0.012 12 5.4 88 9.94 0.15 8.971 11.42 30.7%
6 5 0.46 0.60 0.28 1.79 10.40 2.36 4.23 0,012 12 0.5 52 3.47 0.25 2.73 3.47 155.0%
5 5A 0.12 0.90 0.11 1.90 10.65 2.32 4.42 0.012 12 9.0 58 13.71 0.07 11.58 14.74 38.1%
4A 4 0.08 0.90 0.07 0.07 10.00 2.42 0.17 0.012 12 2.0 28 2.99 0.16 5.46 6.951 3.2%
4 4B 0.08 0.9 0071 0.141 10.16 2.39 0.34 0.012 12 2.0 72 3.75 0.32 5.461 6.95 6.3%
11/10/00 CORE DESIGN, INC. PAGE 1
............... .......
JOB NAME: EAGLE RIDGE PREPARED BY: DE CAYTON
JOB NUMBER: 99102 DESIGN STORM: 25YEAR
ENTRANCE ENTRANCE HEAD
OUTLET INLET
N JAPPROACH BEND JUNCTION
PIPE PIPE NIANNING'S�.LOUTL�'T INLET PIP FLOW VELOC41AIL-ATEJ FRICTION HGL IIEAD 'AD CONTROL C-N��ERTOL VELOCITY HE. HEAD lEADWATER
FV 'A EL,
FROM� TO FLOW LENGTH DIA. n T14LE All PIPE
VELOCITY H: AT.. LOSS ELEVATION LOSS LOSS ELIVATIO�ELEVATIOJ HEAD LOSS LOSS ELEVATION
CB ca (CFS) (FEET) (IN) VALUE (FEET) (S (F] (FEET) (FEE FEE EE EE FEET) (FEET) (FEET) (FEET) (FEV-n RIM EL
4B 4 0,29 72 12 0.012 438.03 439047 0.79 0,37 0.00 442.77 0.00 442.77 0000 000 442.78 439.47 0.00 0,00 0.00 442.78 443.03 0.25
442 7'
4 4A 0.1 28 12 0.012 439.47 440.03 0.79 019 0.00 442.78 0.00 442.78 0.00 0,00 442.79 440.03 0.00 0.00 000 442.78 443.03 0.25
5A 5 3,76 58 12 0,012 438.00 443.22 0.79 4.79 0.36 442,77 0.54 444,22 0.18 0.18 444.58 444.67 0.33 0.11 0.00 444.45 447.02 157
5 6 3.60 52 12 0.012 443.22 443.48 0.79 4.58 0.33 444.45 0.45 444.90 0.16 0.16 445.22 444.93 0.14 0.00 0,49 445.58 447.41 1.83
6 7 2,35 88 12 0.012 443.48 448.23 079 2,99 0.14 445.58 0.32 449,23 0.07 0.07 449.37 9
- 44938 0.04 0.19 0.0o 449.53 451.70 2.17
7 8 1,31 55 12 0.012 448.23 448.50 0.79 L67 0.04 449.53 0.06 449.59 0.02 0.02 449.64 449.20 0.00 0.00 0.00 l44964 452.00 2.36
6 1 9 0.74 28 12 0.012 443.48 1 444.04 1 079 0.94 0.01 445.58 0.01 445.59 1 0.01 0.01 445,60 1 444.04 0.01 0,02 0.00 44561 447.41 1.802
9 1 10 0.59 39 12 0.012 444.04 1 446.77 1 0.79 0.75 0.01 445.61 0.01 447.77 1 0.00 0,00 447.78 1 446.77 0.00 0.00 0,00 447.78 450.27 149
11/10/00 DODDS ENGINEERS,INC. PAGE 1
.............
.............
JOB NAME: EAGLE RIDGE PREPARED BY: DE CAYTON
JOB NUMBER: 99102 DESIGN STORM; 100 YEAR
ENTRANCEIENTRANCE OUTLET
INLET APPROACH REND JUNCTION
CONTROL
TLET U
H EXIT 0 1 �IEADWA.ER
PIPE PIPE MANNING'S�,OUTLET INLET PIPE FLOW VELOCI AILWATE FRICTION I GL HEAD HEAD CONTROL CONTROL VELOCITY HEAD HEAD
0 LOSS
[LO S
FROM TO FLOW!LENGTH: DIA. n LEVATION ELEVATION AREA VELOCITY ELEVATIOD ELEVATION LOSS SS ELEVATIOJELEVATIO HEAD LOSS LOSS ELEVATION
VALUE (FEET) (FEET) (SO FT) (FT/qvcl M (FEET) r S F IRDIEI
CB CB (CFS) (FEET) (IN) I �:E, EFTI (FEET) r)
4B 4 0.34 72 1 12 0.012 438,03 439.47 0.79 0.43 0.00 442.86 0.01 442.87 0.00 0.00 442,87 439A7-- 0.00 0.00 0,00 442.87 443.03 0.16
4 4A 0,17 28 1 12 0.012 4397 440.03 0.79 022 0.00 442.87 0.00 442.87 0,00 OM 442.97 440.03 0.00 OM 0.00 442.97 443.03 0.16
5A 5 4,42 58 12 0.012 438.00 443.22 0.79 563 0.49 442.86 0,75 444.22 0.25 015 444.71 444.67 0.45 0.15 OM 444.41 447.02 2.61
5 6 4,23 52 12 0.012 44122 443.48 0.79 539 0.45 444,41 0,62 445,03 0.23 0.23 445.48 444.93 0.19 0+00 0068 445+96 447.41 1.45
6 7 2.75 88 12 0,012 44148 44823 0,79 150 0,19-- 4596 0.44 449.23 0.10 0.10 449.42 44938 0,06 0.27 0.00 449.63 451.70 2.07
7 8 1.54 55 12 0,012 448.23 448.50 0+79 L96 0.06 449,63 0.09 449,71 0.03 0.03 449077 44920 0,00 0.00 0.00 449.77 452,00 123
17 29 12 0.012 443,48 444,04 0.79 0 1 0.02 1 445,96 1 0.01 1 445M 0,01 0.01 446.00 444.04 1 0.01 0.03 1 0.00 1 446.01 44T41 IAO
IP9 IF,o�111,70 39 12 0.012 444�04 446.77 0.79 0,89 0.01 1 446.01 1 0.01 1 447.77 0,01 _0.01 44T78 446.77 1 0.00 0.00 1 0.00 1 447.78 450.27 2.49
11/10/00 DODDS ENGINEERS,INC. PAGE 1
SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.1.0 25-YEAR 24-HOUR ISOPLUVIALS
2L� g�_- SN XO�ISN COUNTY
KING COUNTY
2� REF r�'� �� ✓-
2,y m ►
dIV
h'
2z-sr'as`.#
-
5.0
t
ko Ysfi
s S
3 ,M4 �� I
r
y '
M ' !Pv
• ij�Cb
wa
CID! 06
11.* PIERCE COUNTY
WESTERN i7
KING COUNTY s.5
N � $,0
25-Year 24-Hour 4.5
h
1
Precipitation
in Inches CO
"""� �� ` ���`'
9/1/98 1998 Surface Water Design Manual
3-16
3.2.1 RATIONAL METHOD
FIGURE 3.2.1.1) 100-YEAR 24-HOUR ISOPLUVIALS
_"M- — --- --- --
�� yr — ——— -- — COUNTY
N COUNTY
tna ✓ �
A
ff �
JW
UZ
�a ,�- � •a sae: '..,i ✓ `...,ti .t
E
� 4. t,}}.x. .. ; _ :S / 1 •.ails, ..+^''��
s .
a
e
4 s `ta •a f.6x8 A e � .� ``�
a
r�t��Yh
1-1 C[COUNTY ,
t
WESTERN
KING COUNTY o�o �,, s.s
H 5.5
100-Year 24-Hour
Precipitation
in Inches 0 2 MBes h�
h�
1998 Surface Water Design Manual 9/1/98
3-17
A �
V. Erosion Control Calculations
The intent of this erosion and sedimentation control plan is to minimize erosion and the
transport of construction related sediments off-site. This design will utilize interceptor
swales and ditches to route all runoff originating from disturbed areas of the site to the
permanent drainage facility, modified with the necessary erosion control measures. The
sedimentation control facilities were designed using the methodology as presented in
Chapter 5 of the KCSWDM.
This plan will also include constructing temporary filter fabric fencing along the south
and east property lines and the placing of mulch, straw, chips or hydroseeding on all
disturbed areas which will be exposed during the wet season as required, see plan sheet
C2.31, note 7.
Sediment Pond Calculations
• Tributary area=4.2 acres
• Design flow, Q2=0.94 cfs (see attached basin summary)
• SA=2 x Q2/0.00096 = 1,958 sf(required at top of riser)
• Side slopes=3:1
• Depth of dead storage= 5.0'
• Depth of live storage=4.5'
• Surface area at top of riser= 9,900 sf
• Riser:
Design flow, Q10 = 1.77 cfs (see attached basin summary)
18" diameter riser with 1 foot of head� 8.5 cfs (see attached Fig. 4.4.7J)
• Emergency Overflow Spillway:
Design flow, Q100=2.71 cfs (see attached basin summary)
Overflow to be provided by the permanent structure, max. flow>>2.00cfs
• Dewatering Orifice:
Orifice area=As(2h)0-5/(10.6)(3600)Tgos
_ (9,900)(2)(4.5)0-5/(10.6)(3600)(24)(32.2)0s
= 0.0081 sf
Orifice diameter=24(orifice area/7r)o.s
=24(0.0081/Tc)o.s
= 1.22 inch. USE 1 inch min.
1 y
11/14/00 6 : 51 : 16 am Dodds Engineers, Incorporated page 1
EAGLE RIDGE
CORE JOB # : 99102
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BASIN SUMMARY
BASIN ID : SPOND002 NAME: SEDIMENT CONTROL POND, 2 YR
SBUH METHODOLOGY
TOTAL AREA. . . . . . . : 4 . 20 Acres BASEFLOWS : 0 . 00 cfs
RAINFALL TYPE . . . . : TYPElA PERV IMP
PRECIPITATION. . . . : 2 . 00 inches AREA. . : 4 . 20 Acres 0 . 00 Acres
TIME INTERVAL. . . . : 10 . 00 min CN. . . . : 89 . 00 0 . 00
TC. . . . . 5 . 00 min 0 . 00 min
ABSTRACTION COEFF: 0 .20
PEAK RATE : 0 . 94 cfs VOL: 0 . 36 Ac-ft TIME : 480 min
BASIN ID: SPOND010 NAME : SEDIMENT CONTROL POND, 10 YR
SBUH METHODOLOGY
TOTAL AREA. . . . . . . : 4 . 20 Acres BASEFLOWS : 0 . 00 cfs
RAINFALL TYPE. . . . : TYPElA PERV IMP
PRECIPITATION. . . . : 2 . 94 inches AREA. . : 4 . 20 Acres 0 . 00 Acres
TIME INTERVAL. . . . : 10 . 00 min CN. . . . : 89 . 00 0 . 00
TC. . . . . 5 . 00 min 0 . 00 min
ABSTRACTION COEFF: 0 . 20
PEAK RATE : 1 . 77 cfs VOL: 0 . 65 Ac-ft TIME: 480 min
BASIN ID: SPOND100 NAME: SEDIMENT CONTROL POND, 100 YR
SBUH METHODOLOGY
TOTAL AREA. . . . . . . : 4 .20 Acres BASEFLOWS : 0 . 00 cfs
RAINFALL TYPE. . . . : TYPEIA PERV IMP
PRECIPITATION. . . . : 3 . 95 inches AREA. . : 4 . 20 Acres 0 . 00 Acres
TIME INTERVAL. . . . : 10 . 00 min CN. . . . : 89 . 00 0 . 00
TC. . . . . 5 . 00 min 0 . 00 min
ABSTRACTION COEFF: 0 . 20
PEAK RATE: 2 . 71 cfs VOL: 0 . 97 Ac-ft TIME : 480 min
` 4111110KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
FIGURE 4.4.7J RISER INFLOW CURVES
Weir Flow
Orifice Flow
100 . 36
33
30
27
24
a
21
d �
U 18
7
U
a 15
a
12
10 or
ElE
1
0.1 1.0
10.0
HEAD IN FEET (measured from crest of riser)
SOURCE: USDA-SCS
QWIER = 9.739 DH=
aORIFICE =3.782 D2H1rz
0 in cfs, D and H in feet
4.4.7-10 1/90