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HomeMy WebLinkAbout03372 - Technical Information Report - Addendum � 1ZEEDS�IAW PLAT .
n' Renton, Washingfon
m
m Technical Information Report Addendum
Prepared For:
�roy Schmeil
CALLIDID� DEVELO�ME�VT IIVC.
16838 SE 43�d Street
Issaquah, WA 98027 �
Phone: (425) 818-8829
Fax: (425) 818-8843
Prepared by:
Pacific Engineering Design, LLC.
15445 53RD Avenue S.,
Seattle, WA 98188
Phone: (206) 431-7970
Fax: (206) 388-1648
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August 9, 2012 Pacific Engineering Job No. 12007
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TABLE OF CONTENTS
Narrative of addendum
The proposed Reedshaw Plat has been changed from 13 lots to 12 lots. Lot 1 to lot 3
rernains the same. The lot lines of original lot 11 to 13 remains the same. Lot 12 is
renamed as lot 10 and lot 13 is renamed as lot 12. Lot 4 and 7 is combined as new lot 4.
Lot lines of lot 4 to lot 9 are adjusted to form 4 uniform lots 5, 6, 8 and 9. The original
lot 8 is replaced with a larger lot 7. Limited infiltration and porous pavements are used as
flow control BMPs. The detention,�wet vault is replaced by a detention pond for Flow
control and a StormFilter manhole with 2 ZPG 27"high 11.3 gpm cartridges is used for
water quality treatment for the new pollution generating impervious and pervious areas.
Structural design of the retaining wall for the detention pond will be included in a
separate submittal as building permit requirements.
IV. FLOW CONTROL / WATER QUALITY FACILITY ANALYSIS
ANDDESIGN.................................................................................................... 3
V. CONVEYANCE SYSTEM ANALYSIS................................................... 14
Reedshaw Plat PED Job number: 12007
�
li/ F�OViI CO(VTRO� / 1IV�►TER C��IALII'Y �ACILITY '
AN�►Ll(�I� AND DE�IGN
IV.1 HYDRAULIC ANALYSIS
The drainage analysis used King County Runoff Time Series (KCRTS) software
version 4.2. The on-site soils are (AgC)Alderwood Series KCRTS Soil Group
Till. The proposal is located in Sea-Tac rainfall region with a scale factor of 1.0.
iV.2 EXiSTIiVG CONDITIONS
The Site of the proposed ReedShaw Subdivision encompasses approximately
2.25 acres. Excluding 0.37 acres utility easement, total drainage area is 1.88
acres. Per 2009 KCSWDM, assume 1.88 acres of till forest under existing
condition.
Total drainage area = 1.88 acres
Total impervious area = 0.00 acres
Total pervious area = 1.88 acres (till forest)
K�_ng County Rurqff Tim2 Series Progran
Vers-on 4.42b
-------------------------------------------------------------------------------
KCRTS Corunand
CREF.TE a new Time Series
------------------------
Frodi:ction of Runoff Iime Series
Project Location : Sea-Tac
Computing Series : predev.tsf
R.e�-ona1 Scale Factor : 1.00
Data Type : Reduced
�=eating Hourly Time Series File
Loading Time Series File:C:\KC SWDM\KC DATA\STTF60R.rnf 8
Iiil Forest 1.88 acres Scaling Yr: 8
Loading 7ir�e Series F_le:C:�KC SWDM\KC DATP.\STE160R.rnf 8
Inper,.�ious 0.00 acres Adding Yr: 8
--------------
Total Area : 1.88 acres
Pea:{ �ischarge: .,.2C4 C,S at 9:.,� cr Jar 9 in Year 8
�toring Time Series File:predev.tsf 8
T-�me S2�-es Computed
Existing condition peak flows:
Q 2y = 0.052 cfs.
Q 10y = 0.091 cfs.
Reedshaw Plat PED Job number: 12007
3
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Flow Fr� ,�2ncv �.ra _ '_-
Time Series File:predev.ts`
Project Location:Sea-Tac
---Annual Peak Flow Rates-- �-oJ� Fre�-�erc�✓ Anal�,�s=s-
Flow Rate Rank Time of Peak - - 2eaks - - Rark neturn crob
(CFSj (CFS) Period
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0.032 7 1/06/02 3:00 0.118 2 25.00 G.°5�
0.088 4 2/28/03 3:OQ 0.091 3 10.00 0.90C
0.0�3 8 3/24/04 20:00 0.�88 4 5.�0 C.8G0
0.052 E 1/05/05 8:�0 0.�77 5 3.00 0.65�
0.091 3 1/18/06 20:�0 0.052 6 2.00 0.5�0
0.077 5 11/24/06 4:00 0.032 7 1.30 0.2�"_
G.=51 1 1/09!OS 9:�0 C.�G3 E 1.1C 0..,._
�o�n�uted Pea:�s ".-4G �O.u� C�.yB�
IV.3 DEVELOPED CONDITIONS
The ReedShaw Subdivision proposed 12 single-family homes. Impervious area
for roadway and sidewalk in Redmond Avenue NE is 0.38 acre. Total lot size of
the 12 lots is 1 .27 acres.
Flo�nr control �I�IPse
1. Porous asphalt or porous concrete pavements are used for the 12
driveways to each lot.
2. Limited infiltrations are used to handle roof areas from the 12 lots.
Onsite soil can be classified as fine sand/loamy sand (SM) according to the
geotechnical report. Every 1000 square feet of tributary impervious area requires
75 feet of gravel infiltration trench or 230 cubic feet of dry well.Assume that each
lot will has 1750 sf of impervious area (roofs, walkways, driveways, etc.).
Impervious areas in the 12 lots will be approximately 12 * 1750 = 21,000 sf.
Limited infiltration and permeable pavement (fvr walkway and driveway in each
lot)will be used to handle the impervious areas in the 12 lots. After apply the
50% impervious area, 50% grass credit. Total impervious areas in the 12 lots
can be counted as 21,000 '` 0.5 /43560 = 0.24 acres.
Asphalt pavement for three private access driveways (NE 14th Place, NE 14�n
Street and driveway to lot 12 and detention pond) is 6,940 sf = 0.16 acres.
Impervious area on top the proposed detention pond is approximately 0.03 acre.
Total impervious area will be approximately 0.38 + 0.24 + 0.16 + 0.03 = 0.81
acres. The remaining area is 1.88 — 0.81 = 1.07 acres and is assumed to be till
lawn.
Total drainage area = 1.88 acres
Reedshaw Plat PED Job number: 12007
4
TOTAL DRAINAGE AREA = 1.88 AC.
TOTAL IMPERVIOUS AREA = 0.81 AC.
r � __ -" TOTAL PERVIOUS AREA = 1.07 AC. (TILL GRASS) _____ _ ---- - -- - - -��� - -------- �G'��- = -
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=41Q II.. I , o ~� I I I I � I �ry I 'a I I / I j I"�i -- 1 �
i. '! I I � i N' � i i i a i i � T--�' _� I�� �'---- ---- �------r-------1---� i"� � � i � 1
,j a � I � I i v � � PAD=416.5 � 1 .�" � _ `- -�
N �� 2 xtDE � / � � Lc_ � I / I1.`I � I I i--r-----�
i � � 3 i ; o o i i i � i � 1 �m+nm�a � � �� - - � �� -- -- -,•C'�� I i � � i 1
,� � 1 i T I.o � II� i C i I Ni t �' e.s�cou,,.��1 i ; � � i, a �---�= ---� 'i � � � � i � � i
I o Ij i' '^�'N, Nn�p I j � � j � .�r�i � � �EET C08 � I � � I � � i i /i n I i �°` 6 I �e1 j � I � I �6 i
�� , . u un� i i � �� IPA6�42.�5 I i � � �o�us� � i 9 / i i i � i � a� �r I °` 3 i
z� r ' ,,�� � i > , I I � i � ASPHAL7 i I i i � � � i � 2 �w I i I i
�/ �' PAD=�35.5
Y� ' I i I I I hP �� I I � I PAD=�3J.5 I/ I "�L i I
`-',Z ,� � �� - ' ---�-' I � _ ��---�__�� � ; � ' �o=4sas � � I �� �� i j I I � i j . a i
o i l�t � � � � �'� i i � ��� i � i i� �i j n i
�o �.,I E � i 6 1 ,�' . -��- -- ------�---�' 1 � i�i �:. � � � � �------- � ,���� � �� ��----�
I J ' ' � =- - � = - - - - �� � , � ' y _� � i:�A
! i - - -
� r �-', � � ,�� � �� �i� _� � = f��'07 2 E � �' �-'�,'��� ' � � �� 480.62 � ��,�,'� ' ' i ----
��iinoN borro i�D / i ! � ; , ��� ��_, � I � i � i ' �"�r:�!� A«�/ ', '-�.
I REQUIRED LIYE � r ,,I � � _ .�`i ;ACG�'SS/llTL '� '� . � r � r � U7L EuMT. �� `.
,,srae�cF=�cF Cf4 / i 1 :� � i � �' �
PRONDfD' � � �--� � ; �-�' ^ r,- � - � l N ;
� ystauc� s.s2o cFs'Hf�NNYI � �� � � snNc�� m N � .i � i � , r �i
� J J Cj` I I CHAlN�LINK F6aEE ry� p m ����•�p � � ��.I / \� !
Z Z ���V I � AROUND PON�," e,�v _e,'1 p � � "� �� � � I / � �
I I��., i i �, . � d � r .
DEVELOPED CONDITION NOTE:
SCALE: 1" - 40' LIMITED INFILTRATION IS USED FOR ALL THE 12 LOTS. 75 LF OF
GRAVEL INFILTRATION TRENCH OR 230 CF OF DRY WELL IS
REQUIRED FOR EVERY 1000 SF OF TRIBUTARY IMPERVIOUS AREA.
Total impervious area = 0.81 acres
Total pervious area = 1.07 acres (till grass)
King Coun`y R�Zrcff Tir�.e Series _rocran
Version 6.00
K�RTS Command
�..�'aT� a new Time Serie=
------------------------
Pr���ctior. cf R.Lno�f i1T.E Ser'es
Proje�t Location : Sea-Tac
Computing Series : dev.ts�
R�gional Scale Factor : 1.50
Data Type : Reduced
�reating Hourly Time Series Fi:e
Loading Time S�r'_,._= Fi=e:C:'�.K� S�ti�A�i'�.KC ���A�,,ST�G'c0=.._r.' 8
T_11 Grass 1.07 acres Scal_r.� �'r: �
Loading Time Series File:C:\KC SWDhf\KC D�TF.\STE=50R..rnf �
=:n�sr-rious 0.81 aCres A�^ ac �r: E
--------------
Total Area : 1.88 acres
Pe3:�: D_sc'�arg�: .,.52� �FS at F:,,,, on �ar. ? in Y2,r �
S�orinc ,i:r:e Series Fi'_e:3e-,�.�sf E'
^_..- ..�__�� ��T:�uted
Developed condition peak flows before detention:
Q 2y = 0.271 cfs.
Q10y = 0.322 cfs.
Q100y = 0.609 cfs.
Flow Freq-sency Ar.a1,s-s
=ine Series File:dev.ts�
Prc-,ect Location:Sea-Tac
---F.nnual Peak Flow Rates--- -----clow Frequency Analys_s-------
zlo��; Rate Rank Time of Peak - - Peaks - - Rank Return Prcb
(��FS) (CFS) Period
C.292 5 2/09/O1 2:00 0.609 1 140.00 0.99�
C.222 7 1/05/02 16:00 0.355 2 25.00 0.96C
0.355 2 2/27/03 7:00 0.322 3 10.00 0.90C
0.222 8 8/26/04 2:00 0.308 4 5.00 0.8G0
0.271 6 10/28/04 16:00 �.292 5 3.00 Q.cS?
��.308 4 1/18/06 16:00 0.271 6 2.00 O.��C�
�.322 3 10/26/06 0:00 0.222 7 1.30 0.23'_
�.6�9 1 1/09/08 6:Q0 0.222 8 1.10 0.09:
��cputed Peaks 0.52� 5C.CQ 0.98C
IV.4 DETENTION ROUTING CALCULATIONS
The City of Renton requires that Level 2 Flow Control Standard be applied to this
project. This standard requires "maintaining the durations of high flows at their
predevelopment levels for all flows greater than one-half of the 2-year peak flow
Reedsha«�Plat PED Job number: 12007
5
up to the 50-year peak flow." Also, the pre-developed peak flow rates for the
2-year and 10-year runoff events are also maintained when applying the Level 2
flow control standard.
Using the appropriate release rates, the developed time-series were modeled in
a pond with 8.5 feet of water depth for live storage and a bottom of 945 square
feet. A control structure with three orifices is designed to meet the release rates
and frequency duration standards. These calculations have been included.
Based on our calculation the volume required to meet the Level 2 Flow Control ',
Standard for the site is 19,368 cf(using an 8.5 feet design depth for live storage). '
Available live storage of the pond is 19,520 cf > 19,368 cf. o.k.
Re�ention'Deten�ion Fac'_l-�y
'Iy�e ot Facility: �e�ention Ponc I�
Side Slope: 1.82 H:1V ��
P�nd Bottom Length: 47.00 ft I
-ond Bottom Width: 20.00 ft '
Pond Bottom Area: 940. sq. ft ',
^op Area at 1 `t. FB: 4453. sq. ft '
C.102 acres
E`-ective Storage Depth: 8.50 ft
Staae 0 �'_evation: 0.00 ft ',
S�oraae Volume: 19512, cu. ft
Q.448 ac-ft
=.-ser Head: 5.50 ft
Riser Diam.eter: 12.00 inches
Pd��-.��er of orifices: 3
Full Head Pipe
�rifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
1 �.00 0.63 0.031
2 5.75 1.25 0.070 4.0
3 7.25 0.88 0.023 4.0 '
Top Notch Weir: Nor.e
Out�-ioa� �catir.g Cu_ve: Ncre
Stac2 E_eva=ior, Storac� Disc�arc= P2rco�_aticr. Surf Ar2a
(ft) (_t) (cs. ft) (ac-f�) (cfs) (cfs) (sq. ft)
0.00 0.00 0. 0.000 O.00C Q.O�� 940.
0.01 0.01 9. Q.000 0.001 Q.00 942. '
C.02 0.02 19. 0.000 0.001 0.00 945.
C.C3 0.03 28. 0.001 0.002 G.00 957.
0.04 O.C4 38. 0.001 0.002 0.00 950.
�.05 �.05 47. 0.001 0.002 O.QO 952.
0.22 0.22 213. 0.005 0.005 0.00 994.
0.39 0.39 385. 0.009 C.007 0.00 1037.
0.55 0.55 555. 0.013 0.008 0.00 1078.
0.72 0.72 742. 0.017 0.009 0.00 1122.
0.89 0.89 936. 0.021 0.010 0.00 1168.
1.05 1.05 1127. 0.026 0.011 0.00 1211.
'.22 1.22 1336. 0.031 0.012 0.00 1257.
-.39 i.39 1554. 0.036 0.012 0.00 1305.
=.55 1.55 1766. 0.041 0.013 0.00 1350.
�.72 1.72 2000. 0.046 0.014 a.00 '_399.
1.89 1.�9 2242. 0.051 0.015 0.00 1448.
Reedshaw Plat PED Job number: 12007
6
2.05 2.G5 2478. 0.057 G.Oi5 C.00 149c.
2.22 2.22 2736. 0.063 0.016 0.00 1547.
2.39 2.39 3003. 0.069 O.C16 Q.00 1599.
2.55 2.55 3263. 0.075 0.017 0.00 1648.
2.72 2.72 3548. 0.081 0.017 0.00 1701.
2.89 2.89 3842. 0.088 0.018 0.00 1755.
3.05 3.05 4127. 0.055 0.�19 0.40 i807.
3.22 3.22 4439. O.lQ2 0.019 G.00 1863.
3.39 3.39 4760. Q.109 0.019 0.00 1919.
3.55 3.55 5071. G.116 0.020 �.00 1973.
3.72 3.72 5412. 0.124 0.020 0.00 2031.
3.89 3.89 5762. 0.132 C.021 0.00 2039.
4.05 4.a5 6101. �.14C 0.021 0.0a 2145.
4.22 4.22 6470. �.149 Q.022 0.00 2205.
4.39 4.39 6850. 0.'_57 a.022 O.00 2266.
4.55 4.55 7218. 0.166 0.023 0.0a 2324.
4.72 4.72 7618. 0.175 0.023 0.0a 2386.
4.89 4.89 8029. 0.184 O.Q23 0.00 2449.
5.a5 5.05 842E. 0.193 0.a24 0.00 2509.
5.22 5.22 8858. 0.203 0.024 0.0� 2574. �
5.39 5.39 9301. 0.214 0.025 0.00 2639.
5.55 5.55 9728. 0.223 0.025 0.00 2702.
5.72 5.72 10193. Q.234 0.025 0.00 2768.
5.75 5.75 10276. a.236 0.025 0.00 2780.
5.76 5.76 10304. 0.237 0.026 0.00 2784.
5.78 5.78 10360. d.238 0.027 0.00 2792.
5.79 5.79 10388. 0.238 0.028 0.00 2796.
5.80 5.80 10916. 0.239 a.031 0.00 2800.
5.82 �.82 10472. 0.24C 0.034 0.00 2808.
5.83 5.83 10500. 0.241 0.037 0.00 2812.
5.84 5.84 1a528. �.242 0.038 0.00 2816.
5.85 5.85 1a556. 0.242 �.039 0.00 2820.
6.02 6.02 11041. 0.253 0.048 O.00 2888.
6.19 6.19 11538. 0.265 0.054 0.00 2957.
6.35 6.35 12017. 0.276 0.060 0.00 3023.
6.52 6.52 12537. 0.288 0.064 0.0� 3093.
6.69 6.69 13069. 0.3C0 0.068 Q.00 3165. ;
6.85 6.85 13580. 0.312 0.072 0.00 3232. �,
7.02 7.02 14136. 0.325 0.076 0.00 3305. ',
7.19 7.19 14704. 0.338 0.079 0.00 3378. �
7.25 7.2� 14908. 0.342 0.080 0.00 3405.
7.26 7.26 14942. 0.343 0.081 0.00 3409.
7.27 �.27 14976. 0.344 0.081 0.00 3413.
7.28 7.28 15010. 0.345 0.082 0.�0 3418.
7.29 7.29 15044. 0.345 0.084 0.00 3422.
7.30 7.30 15078. 0.346 0.086 O.Oa 3426.
7.31 7.31 15113. 0.347 0.087 0.0a 3431.
7.32 7.32 15147. 0.348 0.087 0.00 3435.
7.49 7.49 15737. G.361 0.�95 0.00 3510.
7.66 7.6E 16340. 0.375 0.101 0.40 3585.
7.82 7.82 16920. 0.388 0.106 0.00 3657.
7.99 7.99 17548. 0.403 �.111 0.00 3734.
8.16 fi.16 18190. 0.418 Q.116 0.00 3812.
8.32 8.32 18805. 0.432 0.120 0.00 388c.
8.49 8.49 19473. 0.447 0.124 0.00 3965.
8.50 8.50 19512. C.4S8 0.124 0.00 397C.
8.60 8.60 19912. a.457 0.435 0.00 401�.
8.70 8.70 24316. 0.466 1.000 0.00 400�.
8.80 8.80 20725. 0.476 1.730 O.OQ 4112.
8.90 8.90 21138. 0.485 2.530 O.OG 4160.
9.00 9.00 21557. 0.495 2.810 0.0� 4208.
9.10 9.i0 21980. 0.505 3.070 0.00 4257.
Reedshaw Plat PED Job number: 12007
7
9.20 9.20 22408. 0.514 3.300 �.00 4305.
9.30 9.30 22841. 0.524 3.520 0.00 4354.
9.40 9.40 23279. 0.534 3.730 O.QO 4403.
9.50 9.50 23722. 0.545 3.930 0.00 4453.
9.60 9.60 24169. 0.555 4.110 0.00 4502.
9.70 9.70 24622. 0.565 4.290 0.00 4552. '
9.80 9.80 25080. 0.576 4.46G 0.00 4603.
9.90 9.90 25543. 0.586 4.630 0.00 4653.
10.00 10.00 26011. 0.597 4.790 0.00 4704.
10.10 i0.10 26483. 0.608 4.94G 0.00 4755.
10.20 i0.20 26961. 0.619 5.090 O.QO 4806.
1�.30 �0.30 27445. 0.630 5.230 0.00 4858.
Hyd Inflow Outflow Peak Storage
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 0.61 0.15 0.12 8.�6 8.46 19368. G.445
2 p.2g ******* 0.11 7.83 7.83 16959. 0.389
3 0.29 0.09 0.08 7.07 7.07 14300. a.328
4 0.35 ******* 0.08 7.05 7.05 14226. 0.327
5 0.31 ******* 0.06 6.41 6.41 12192. 0.280
6 0.18 Q.05 0.04 5.87 5.87 1�622. 0.244
7 0.22 ******* 0.02 5.18 5.18 8744. Q.201
8 0.22 ******* 0.02 3.52 3.52 5005. Q.115
----------------------------------
Route Time Series through Facility
Inflow Time Series File:dev.tsf
O��tflow Time Series File:rdo•st2 '
Inflow/Outflow Anaiysis
Peak Inflow Discharge: 0.609 CrS at 6:OC on Jar. 9 in Year 8
Peak Outflow Discharge: 0.123 CFS at 13:00 on Jan 9 in Year 8
Peak Reservoir Stage: 8.46 Ft
Peak Reservoir Elev: 8.46 Ft
Peak Reservoir Stor�ge: 19368. Cu-Ft
. 0.445 P.c-F�
Flow Freqaency Analysis
Time Series File:rdout2.tsf �
Project Location:Sea-Tac �
---Annual Peak _1o�r Rates--- -----Flow Frequency Ar:a�ys�_s-------
F1ow Rate Rank Time of Peak - - Peaks - - Rar.k Return Pro�
(CFS) (CFS) (ft) Period
0.106 2 2/09/O1 21:00 C.123 8.46 1 100.00 0.990 II
0.024 7 12/29/O1 11:OC 0.106 7.83 2 25.00 0.96C �I
0.076 4 3/06/03 22:00 0.077 7.07 3 10.00 0.90� I
Q.02� 8 8/26/04 7:00 0.076 7.05 4 5.60 0.80�
O.OS� 6 1/68/�5 1:00 0.061 6.41 5 3.�0 0.6E� lil
0.061 5 1/19/�6 2:00 �.040 5.87 6 2.00 0.50� I
0.077 3 11/24/�6 9:00 �.a24 5.1fi 7 1.30 0.23i I
0.123 1 1/09/08 13:00 �.020 3.52 8 1.10 0.091 I�
Computed Peaks 0.118 8.23 �O.QO 0.980 ,
Flow Duration from Time Series File:rdout2.ts` I,
Cutoff Count Freauer.cy CDF Exceedence_Probabi�ity �I
CFS � a $
0.002 35979 58.674 58.674 41.326 0.413E+G0
0.005 5090 8.301 66.975 33.025 0.33�E-G��
0.008 3841 6.264 73.239 26.761 0.268E-GO
0.011 4240 6.915 80.153 19.847 0.198E-G0
0.013 3867 6.300 86.46G 13.540 0.135�+G�
Reedshaw Plat PED Job number: 12007
8
0.016 3053 4.979 91.438 8.562 0.856E-01
0.019 1979 3.227 94.666 5.334 0.533E-01
�.022 14Q5 2.291 96.957 3.043 0.304E-Oi
0.025 1401 2.285 95.242 6.758 0.758E-02
0.028 54 0.088 99.330 0.670 0.670E-02
0.031 13 0.021 99.351 0.649 Q.649E-02
�.034 32 0.052 99.403 0.597 0.597E-02
G.037 16 0.026 99.429 0.571 0.571E-02
��.04� 34 0.055 99.485 0.515 0.515E-02
�.043 27 0.044 99.529 0.471 0.471E-02
0.046 22 0.036 99.565 0.435 0.435E-D2
O.C49 30 0.049 99.614 0.38E 0.386E-02
0.052 22 0.036 99.649 0.351 0.351E-02
0.055 23 0.038 99.687 0.313 0.313E-02
G.058 14 0.023 99.710 0.290 0.290E-02
G.061 22 0.036 99.746 0.254 0.254E-02
Q.064 37 0.060 99.806 0.194 0.194E-�2
G.067 25 0.641 99.847 0.153 0.153E-02
�.070 10 0.016 99.863 0.137 C.137E-02
�.073 16 0.026 99.889 0.111 0.111E-02
�.076 15 0.024 99.914 0.086 0.864E-03
�.Q79 18 0.029 99.943 0.057 0.571E-03
�.G82 6 0.010 99.953 0.047 0.473E-03
�.G85 0 0.000 99.953 0.447 0.473E-03
O.G88 3 0.0a5 99.958 0.042 0.424E-03
0.091 6 0.010 99.967 0.033 0.326E-03
0.093 4 0.007 99.974 0.026 0.261E-03
0.096 2 0.003 99.977 0.023 0.228E-03
0,099 3 0.005 99.982 0.018 0.179E-03
G.1�2 4 �.007 99.989 0.011 0.114E-03
G.105 4 O.Q07 99.995 Q.005 0.489E-Q4
���r=_tion Comparison Anaylsis
Base File: predev.tsf
tdew File: rdou`�2.tsf
�•a�o'f U�:its: Discharge in CFS
-----Fraction of Time----- ---------Check of Tolerance-------
�L�c_� Base New $Char.ge Probability Base New °�Change
�.C26 I 0.94E-02 0.74E-02 -21.4 I 0.94E-02 0.�26 0.025 -3.6
G.033 I 0.63E-G2 0.62E-02 -1.6 ', 0.63E-02 0.033 0.032 -2.3
�.CaO I 0.50E-02 0.52E-02 3.9 I 0.50E-02 O.G40 0.042 3.5
�.047 I 0.37E-02 0.42E-02 12.3 I 0.37E-02 O.G47 0.050 5.4
� .C54 I 0.28E-G2 0.32E-02 12.6 I 0.28E-02 0.054 0.058 7.5
�.062 I 0.22E-Q2 0.24E-02 8.1 I 0.22E-02 0.062 0.063 1.8
�.a69 i 0.15E-G2 0.14E-02 -3.3 I 0.15E-02 0.�69 0.068 -0.8
�.a76 I O.10E-02 0.86E-03 -14.5 I O.10E-02 0.076 0.074 -2.5
�.083 I 0.62E-03 0.47E-03 -23.7 I 0.62E-03 0.083 0.078 -6.4
�.090 I 0.34E-03 0.33E-03 -4.& I 0.34E-03 0.090 0.090 -0.2
�.097 I 0.23E-03 0.21E-03 -7.1 I 0.23E-03 0.097 0.097 -0.5
�.104 i 0.16E-03 0.98E-04 -40.0 I 0.16E-03 0.104 D.101 -3.2 '
�.111 i 0.11E-43 O.00E+00 -100.0 � 0.11E-03 C.111 0.103 -�.2 '
�.118 I 0.16E-04 O.00E+00 -100.0 � 0.16E-0� C.1=� Q.iG6 -1C.2
':ax_m;,�m positive excursion = 0.003 cfs ( 7.7%)
�c�urring at 0.043 c`s on the Base Data:predev.tsf
a-d at �.047 cfs on tne New Data:rdout2.tsf
Maximum negative excursion = 0.004 cfs (-1�.4�)
occurring at 0.029 cfs on the Base Data:predev.�sf
and at 0.025 cfs on the New Data:rdout2.tsf
Developed condition peak detention pond release rates:
Reedshaw Plat PED Job number: 12007
9
Q 2y = 0.040 cfs. < 0.052 cfs (Ex. 2 year peak) o.k.
Q10y = 0.077 cfs. < 0.091 cfs (Ex. 10 year peak) o.k.
Q100y = 0.123 cfs. < 0.151 cfs (Ex. 100 year peak) o.k.
The 100 year 15 minute developed peak flow:
Q100y-15min = 1.47 cfs
King �oLnty :�incfi Tirce Ser�_es Pr�gra:n
Version 6.00
KCRTS Command
CREe:�E a new Time Series
------------------------
=_oduction of Runoff iime Series
Froject L�ca�ior : Sea-Tac
CoR.putir.g Series : dev.tsf
F.e�ional Scale Factor : 1.00
Data Type : Reduced
�reating 15 Minute Time Series File
Loading ^_itr:e Series File:C:\KC SWDM.\KC DATA\S^tTG60R.rnf 8
=i11 Grass 1.07 acres Scaling Yr: 8
Loading Time Series File:C:\KC SWDM\KC DATA\STE160R.rnf 8
=rr.�er-•,�iou= 0.81 acres Adding Yr: 8
--------------
�otal Area : 1.8fi acres
_�ai: �i=c'r.arge: 1.�7 CFS a; 6:OC cn Jan 9 in Year 8
Storing Time Series File:dev-15.tsf 8
"-��r.2 Series �omouted
F1ow Frequency Analysis
Tirie Series File:dev-15.tsf
P=oject Locatior.:Sea-Tac
---Annual Peak Flow Rates--- -----F1ow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.386 6 8/27/O1 18:40 1.54 1 100.00 0.990
G.304 8 1/05/02 15:C0 0.9E4 2 25.40 0.960
0.964 2 12/OS/02 17:'5 0.666 3 1�.00 0.9�0
0.311 7 8/26/04 0:45 0.558 � 5.00 0.800
�.066 3 11/17/09 5:00 0.502 5 3.00 0.667
�.502 5 10/27/05 10:45 0.386 6 2.00 0.500
G.558 4 10/25/06 22:45 0.311 7 1.30 0.231 '
1.50 1 1/09/OH 6:30 0.304 8 1.10 6.091
�o:np�s`ed Peaks 1.32 50.00 0.980
Primary overflow:
The 12° riser in the flow control structure provides the primary overtlow I
At head = 0.3' over the riser over flow elevation ��
Reedshaw Plat PED Job number: 12007 I
10 I
Qweir = 9.739 * D * H ** (312} = 9.739 * 1 * 0.3 ** 1.5 = 1.60 cfs > 1.50 cfs o.k.
The 12" riser has the capacity to handle the 100 year 15 minute developed peak.
Sec�roclary inle# #o the controB �#ruc#ure:
Secondary inlet to the control structure is provided by a grated opening
{"jailhouse windown) in the control structure.
Q = C * (L - 0.2 *H) * H ** (3/2)
L = Q / (C * H ** 1.5) + 0.2 * H = 1.50 / (3.284 * 0.3 ** 1.5) + 0.2 * 0.3 = 2.84'
Assume H = 0.3'
P = 8.5'
C = 3.27 + 0.4 * H /F' = 3.27 + 0.4 * 0.3 / 8.5 = 3.284
Use 3' long x minimum 6" high grated opening.
Emergency overflow path:
Rectangular emergency overFlow weir:
The pond has a rectangular emergency overflow weir at the concrete retaining
wall.
Assume H = 0.2'
Required length of the weir:
L = Q100/(3.21 * H ^ 1.5) = 1.50 / (3.21 * 0.2 ^ 1.5) = 5.22' < 6'
UseL = 6'
A 6' long weir will be used.
Rip rap swale:
A rip rap swale will be installed from the emergency overflow weir to the back of
the sidewalk along Sunset Boulevard. A catch basin located at the end of the rip
rap swale will pick up the overflow runoff and conveys it to the drainage system
along Sunset Boulevard. The proposed rip rap swale has a cross section of
bottom width 1', top width 5', side slopes 2:1, and rock depth 2'. Longitudinal
slope of the rip rap swale is approximately 13%, capacity of the swale with 0.3'
water depth is:
Q = 1.49 * A * R ** (2/3) *SQRT(S) / n
A = wetarea = 1 * 0.3 + 2 * 0.3 * 0.3 = 0.48sf.
R = Hydrulic radius = wet area/wet perimeter
= 0.48/(1+ 2 * 0.3 * SQRT (1 + 2 *2)) = 0.20ft.
N = manning's coefficient = 0.04
Q = 1.49 * 0.48 * 0.2 ** (213) * SQRT(0.13)10.04 = 2.24cfs > 1.50cfso.k.
Rip rap shall be reasonably well graded with gradation as follows:
Maximum stone size: 24 inches (nominal diameter)
Median stone size: 16 inches
Minimum stone size: 4 inches
Reedshaw Plat PED Job number: 12007
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Figure 1 Flow durations chart
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Reedsha��� Plat PED Job number: 12007
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3,2.2 KCRTS/RUNOFF FILES METAOD—GENERATING TIME SERIES
_- ,_..
- TABLE 33.2.B EQUIVt�,ENCE BETWEEN SCS SOIL TYPES A1VD KCRTS SOIL TYPES
SCS Soil Type SCS 6(CRTS Soi9 Notes
�oNS��G SO�L Hydrologic Group
Soil Group
Alderwood (Ag6, gC AgD) C Til!
Arents,Alderwood Materiai(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 Tiil 3
Edgewick(Ed) C Till 3
Everett (Ev6, EvC, EvD, EwC) A/B Outwash 1
Indianola (1nC, InA, InD) A Oufwash 1
Kitsap(Kp6, KpC, KpD) C Till
Klaus (KsC) C Outwash 1
Neilfon (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
Salal (Sa) C Till 3
Sammamish (Sh) D Till 3 '
Seattle (Sk) D Wetland !
Shatcar(Sm) D Till 3 I
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�utwash soils are saturated or underlain at shallow depth(<5 feet)by glacial till, they should I
be treated as till soifs. I
2. These are bedrock soils, but calibration of HSPF by King County DNRP 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 wafer
table. In the absence of detailed study,fhese soils should be treated as till soils.
4. Buckley soils are formed on the low-permeabifity Osceola mudflow. Hydrologic response is
assumed to be similar to that of till soils.
2Q09 Surface Water Design Manual 1/9/2009
3-25
SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.2.A RAINFALL REGIONS AND REGIONAL SCALE FACTORS
ST '9.0/
ST 1.0 �q p,g LA 0.9 �-p► �•� LA 'f.2
ST1�� � ' - � SNONONISNCOIINTY
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VIERCE COUNTi� � � � . -
ST 1 A
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Rainfali Regions and �ao.$f ~�
�
Regional Scale Factors �a o.s
L.-=a Incorporated Area
LA 1.0 LA 1.2
._.c.� River/Lake
Major Road
1/9/2009 2009 Surface Water Desib Manual
3-22
SECTION C.2 FLOW CONTROL BMPs
C.2.3.5 MAINTENANCE INSTRUCTIONS FOR LIMITED INFILTRATION
If tbe iimited infiltration flow control BMP is proposed for a project,the following maintenance and
operation instructions must be recorded as an attachment to the required declaration of covenant and
grant of easement per Requirement 3 of Section C.1.3.3 (p. C-18). The intent of these instructions is to
explain to future property owners,the purpose of the BMP and how it must be maintained and operated.
These instructions are intended to be a minimum;DDES may require additional instructions based ou site-
specific conditions. Also,as the County gains more experience with the maintenance and operation of
these BMPs,future updates to the instructions will be posted on King County's Strrface Water•Desigra
Manual website.
� TEX�'OF IM��'RllCTIONS
Your property contains a stormwater management flow control BMP(best management practice)called
"limifed infiltration,"which was instailed to mitigate the stormwater quantity and quality impacts of some or
all of the impervious surfaces on your property. Limited infiltration is a method of soaking runoff from
impervious area(such as paved areas and roofs}into the ground. Infiltration devices, such as gravel filled
trenches, drywelis, and ground surface depressions,facilitate this process by putting runoff in direct
contacf with the soii and holding the runoff long enough to soak most of it info the ground. To be
successfu{,the soil condition around the infiltration device must be abie to soak water into the ground for a
reasonable number o#years.
The infiltration devices used on your property include the foflowing as indicated on fhe flow control BMP
site plan:�(gravel filied trenches, ❑drywells. The size, placement, and composition of fhese devices as
depicted by the flow control BMP site plan and design details must be maintained and may not be changed
without wriften approval either from the King CoWnty Water and Land Resources Division or through a
future development permit from King County.
Infiltration devices must be inspecfed annually and after major storm events to identify and repair any
physical defects. Maintenance and operation of fhe system should focus on ensuring the system's viability
by preventing sediment-laden flows from entering the device. Excessive sedimentation will result in a
plugged or non-functioning facility. If fhe infiltration device has a catch basin, sediment accumufation must
be removed on a yearly basis or more frequently if necessary. Prolonged ponding around or atop a device
may indicate a plugged facility. If the device becomes plugged,it must be replaced. Keeping the areas
that drain to infiltration devices well swept and clean will enhance the longevity of these devices. For roofs,
frequent cleaning of gutfers wilM reduce sediment loads to these devices.
i/9/2009 2009 Surface�TJater Desib Mamial—Appendix C
G50
C.2.2 FULL INFILTRATION
FIGURE C.2.2.A TYPICAL TRENCH INFILTRATION SYSTEM
roof
drain
PLAN VIEW
NTS 4"rigid or 6"flexfble
perforated pipe
t
;
�
•------------------------------------------------
infiltration trench sump w/solid lid
PLAN VIEW roof drain
NTS
overflow
4"rigid or 6"flexible splash block
perforated pipe
� r h��'y�Y?�,�i�` :i,�y��.
6�� . /?l./../ / /,�i/i i i, i� ;, ��!.�:Cv
_�,._... .......................••--.....
�.o '
6�� �oo Q V
�� p � � Do 0 a d� C 1'min 5,0'min
„ washed rock
12 ;, E= 1 1/2"-3/4° •" �" Q o c °; 1'min
.
-•........ ......................�Q.s..n.°°�r.
I fine mesh � CB sump w/solid lid
crrcan
varies
A
filier fabric
�compacted backtill
�>, -_�;�_-��= ,
6�� �- -
. . _./'
+ � 4"�igid or 6"flexible
0 0 0 °o o� pe�forated pipe
24" °9 0 °9
0 o Da o
�� 9°�o �o p washed rock
12" � po Q o oQ�p�a 1 1/2"-314"
y p o°� o a
��`�•�%�'
�—24"—�I
SECTION A
NTS
2009 Surface Water Design Manual-Appendix C 1/9/2009
C-45
SECTION C.2 FLOW CONTROL BMPs
FIGURE C.2.2.B ALTERNATIVE TRENCH INFILTRATION SYSTEM
from roof
grass
6"min
�overflow � ����\�i\�j/�
/
���2��-3�4�� QaQ °p°oDo �
washed rock %;a a QQ q oo a NOTE: Same length dimensions
18" min
� =o ,o 0 0°a va and site limitations as typical system
/ eQ � a v�o �
°a 4 n 9° p° n
� 2' min I- 15' min
X-SECZION
NTS
filter strip
grass 5' min
I drtvewaY
overflow �'6" min ✓�
� � 1 \1\\\11\'�;
� �`�tE11i1�����/i
o pO i ���
'��j2��-3�4'� a a °v°�o a
washed rock %�a a ° oo o , NOTE: Same length dimensions
•\ ;� ao�Q o 0 0 18' min and site limitations as t y pical s ystem
v oD o �
� Q� � p pOQ
�°p� o �° Q° o
� 2' min �
X-SECTION
NTS
1/9/2009 2009 Surface Water Design Manual—Appendix C
C-46
� C.2.2 FULL INFILTRATION
F`IGURE C.2.2.0 TYPICAL DRYWELL INFILTRATION SYSTEM
�Roof Downspout
House
Catch Basin
�(Yard Drain)
/
�Roof fl_�
Downspout
�
DRY WELL 48 Inch Diameter
Hole Filled with
PLAN VIEW 1�/2-3"Washed
Drain Rock
NTS
Roof Downspout
Mark Center of Hole
with 1"Capped PVC
House Overflow or Other means
Splash Block Topsoil Flush with Surface
= � �l � ,l 1
=�_,:.: - 1' min.
- =_- _� xn.�:,sa,��� �l-, � ,cr���;��=�
p •a,o`� :.J;. a�,,u
110�/ Jc,p�� � ��gL_`�I�Sf��q�.-�i�-�C_c
L �`�y'�S�L`°�J�i��'�1,�J`�OQ�_``.
Fine Mesh Screen I Min.4"dia. �'�--o�c�= �.,� ,�_•°, n
PVC Pipe '�°_:�;'�;=-��—���a.
a C� ��y j
Catch Basin ����y �``�`'
O�� `1'�
'
(Yard Drain) ? ��
� 48 Inch Diameter � Varies
Sides of Hole ,��� Hole Filled with �
Lined with �s 1�/2-3"Washed �
Fiiter Fabric �G� Drain Rock ��,
15' min. �'` -'�-
� i.� f`P,,�'��'i:r�D`'o°^�:--1_
�.,°,����J«,,�r°].��o;���C��-
Min. 1'above Seasonal
DRY WELL High Groundwater Table
SECTfON �
NTS
2009 Surface WaterDesign Manual—Appendix C 1/9/2009
C-47
SECTION C.2 FLOW CONTROL BMPs
FIGURE C.2.2.D TYPICAL GROUND SURFACE DEPRESSION INFILTRATION SYSTEM
from roof
grass
o�rf�ow 12"min f—�,
��t�•-��������.��� �waterstora e ,� �'`" �
� .,t,.,,�� ��.,, g ,,,�- :,,��y�������y,�
,,,.
,,,. 6«minimum �.,�;u,.,: ,�.,,�,�., ,,�,,,,•:1.,�'"�_`l,
freeboard � � I
� �. �, i t 15'min �
infilration
X-SECTION
MTS
grass driveway
overfiow 12"minimum ,�r���
-f-- ,,...�t-�`�
. ,,,,,,x,.,��.�.;, f..,,��..,,,.,,,,,��.,, ,. �waterstorage .,,:.�
6" minimum `��%-- y,�,,.�...��� filter
freeboard f �•,,,�r�.,,,��..•.,,,;.,.. .�� l 5S�P
T � � � ,
Infilration
X-SECTI�N
NTS
1/9/2009 2009 Surface Water Design Manual—Appendix C
C-48
IV.5 WATER QUALITY VOLUME
Basic water quality treatment is required for this project. StormFilter is used to
provide the basic water quality treatment. The StormFilter manhole is located
downstream of the Level 2 detention pond. Presettling is provided by the Level 2
detention pond. 27" 11.3 GPM ZPG cartridges are used.
Water quality flow rate is the 2 year release rate of the detention pond
Qwq = Q 2 year = 0.040 cfs.
Peak flow of the StormFilter manhole is the 100 year release of the detention
pond
Qpeak = Q100 year = 0.123 cfs.
Total area to be treated = 1.32 acres
Total impervious area to be treated = 0.54 acres
Total pervious area to be treated Nflow = 0.78 acres (grass)
Onsite soil: 67.5% sand, 16.25°/a silt and 16.25% clay per Geotechnical report
TSS removal efficiency estimate REe = (%Sand * Csand) + (°/aSilt * Csilt) +
(%Clay * Cclay) _ (0.675 * 0.96) + (0.1625 * 0.80) + (0.1625 * 0.15) = 0.80
Flow rate based sizing:
Required number of cartridges = Qwq * 449 (gpm/cfs) /Q per cart.
= 0.040 * 449 /11.3 = 1.59, Use 2 cartridges.
Mass based sizing:
Annual average rainfall P = 37 inches
Agency required % removal = 80%
Percent capture = 90%
EMC = 60 mg/L
Vt = P * C * A * % capture
= 37/12 * (0.9 * 0.54 + 0.10 * 0.78) * 43560 * 0.90
= 68176 cf.
Total annual mass ,
Mtotal = Vt * EMC * (28.3 L/cf) * (1 E-6 kg/mg) * (2.2046 Ibs/kg) ,
= 68176* 60* 28.3 *1 E-6 * 2.2046 '
= 255.20 Ibs '
Pre-treatment removal efficiency Epre = 50% (Level 2 detention pond)
Mpre = Mtotal * Epre = 255.20 * 0.50 = 127.60 Ibs ',
Mpass1 = Mtotal — Mpre = 255.20 — 127.60 = 127.60 Ibs
Efilter = 60%, REe > Efilter, o.k. to use Qcart = 11 .3 gpm '�
Mfilter = 127.60 * 0.60 = 76.56 '
Q cart = 11.3 gpm ',
M Cart = 54 Ibs/per cart
Required number of cartridges Nmass = 76.56 / 54 = 1.42, use 2 cartridges.
Both method require use finro 27" 11.3 gpm ZPG cartridges.
Reedshaw Plat PED Job number: 12007
13
Determining Number of
,�V, g
�.��NTE �"� Cartridges for Systems
ENGINEERED SOLUTIONS Downstream of Detention
CONTECH Stormwater Solutions Inc. Engineer: MAZ
Date 6/12/2012
Site Information
Project Name Reedshaw Plat
Project State Washington
Project Location Renton
Drainage Area,Ad 1.32 ac
Impervious Area, Ai 0.54 ac
Pervious Area, Ap 0.78
% Impervious . 41%
Runoff Coefficient, Rc 0.42
Upstream Detention System
Peak release rate from detention, Qrelease peak 0.12 cfs
Treatment release rate from detention, Qrelease Veat 0.04 cfs
Detention pretreatment credit 50%
(from removal e�ciency calcs)
Mass loading calculations
Mean Annual Rainfall, P 37 in
Agency required % removal 80%
Percent Runoff Capture 90%
Mean Annual Runoff,V� 66,725 ft'
Event Mean Concentration of Pollutant, EMC 60 mg/l
Annual Mass Load, Mtota� 249.78 Ibs
Filter System
Filtration brand StormFilter
Cartridge height 27 in
Specific Flow Rate 1.0 gpm/ftz
Number of cartridges -mass loading
Mass removed by pretreatment system, Mpfe 124.89 Ibs
Mass load to filters after pretreatment, MPass� 124.89 Ibs
Estimate the required filter efficiency, Ef�ter 0.60
Mass to be captured by filters, Mfi�ter 74.93 Ibs
Allowable Cartridge Flow rate, C�art 11.25
Mass load per cartridge, M�rt(Ibs) 54.00 Ibs
Number of Cartridges required, Nmass 2
Treatment Capacity 0.05 cfs
Determine Critical Sizing Value
Number of Cartridges using Qrelease Veat+ Nflow 2
Method to Use: MASS-LOADING
SUMMARY
Treatment Flow Rate, cfs 0.05
Cartridge Flow Rate, gpm 11.3
Number of Cartridges 2
1 of 1
C=d�oNTECH�
ENGlNEERED 50LUTIONS Size and Cost Estimate
Pre,�ared by Mark Zeman on June 12, 2012
Reecishaw Plat — �torrnwater �reatr�en# Systern
Renton, WA
Information provided:
• Total contributing area = 1.32 acre
• Impervious area = 0.54 acre
e Detention release rate, Qt�eat = 0.041 Cfs
• Presiding agency = City of Renton, WA
Assumptions:
• Media = ZPG cartridges
o Per cartridge flow rate = 11.25 gpm
• Drop required from inlet to outlet = 3.05' minimum
Size and cost estimates:
The StormFilter is a flow-based system, and therefore, is sized by calculating the peak water quality flow rate
associated with the design storm. However, when the StormFilter is placed downstream of detention the flow rate
generated at the water quality storm is not always representative of the total volume of water that will go through the
system or type of pollutant-loading the system may experience in one year.
For this site, Contech Engineered Solutions LLC recommends using a 48" Manhole StormFilter with (2) 27"
cartridges (see attached detail). The estimated cost of this system is 12 700, complete and delivered to the job site.
This estimate assumes that the vault is 6 feet deep. The final system cost will depend on the actual depth of the unit
and whether extras like doors rather than castings are specified. The contractor is responsible for setting the
StormFilter and all externat plumbing.
Typically, precast StormFilters have internal bypass capacities of 1.8 cfs. If the peak discharge off the site is
expected to exceed this rate, we recommend placing a high-flow bypass upstream of the StormFilter system.
Contech Engineered Solutions could provide our high-flow bypass, the StormGate, which provides a combination
weir-orifice control structure to limit the flow to the StormFilter. The estimated cost of this structure is $4,000. The �
final cost would depend on the actual depth and size of the unit. 'I
�02012 Contech Engineered Solutions LLC 11835 NE Glenn Widing Dr.,Portland OR 97220 Page 1 of 1
«-��1�-.ContechES.com Toll-free:800.548.4667 Fax:800.561.1271 TS-P022
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BY:
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� ���������� ������ ��������
The conveyance analysis included in this report at construction document
submittal (see attached tables). The system will be designed to convey the
25-year peak flows and checked for flooding conditions at the 100-year event per
2009 King County Surface water Design Manual.
Reedsha�v Plat PED Job number: 12007
14
� 3.2.1 RATIONAL METHOD
- . . . ,
TABLE 33.i.A RUNOFR COEFFICIE�ITS-"C"VALUES F�R T�IE RATIONr�I:IlZETI�OD
6eneral Land Covers Single Family Residential Areas�
Land Cover C Land Cover Density C
Dense forest 0.94 0.20 DU/GA(1 unit per 5 ac.) 0.17
Light forest 0.15 0.40 DU/GA(1 unit per 2.5 ac.) 0.20
Pasture 420 0.80 DU/GA(1 uni#per 1.25 ac.) 0.27
Lawns 0.25 1.00 DUIGA 0.30
Playgrounds 0,30 1.50 DiJ/GA 0.33
Gravel areas 0.80 2.00 DU/GA 0.36
Pavement and roofs 0.90 2.50 DU/GA 0.39
Open water(aond, lakes, 1.00 3.00 DU/GA 0.42
wetlands) 3.50 DUIGA 0.45
4.00 DUJGA 0,48
4.50 DUIGA 0.51
5.00 DU/GA 0.54
5.50 DU/GA 0.57
6.00 DUIGA 0.60
�Based on average 2,500 square feet per lot of impervious coverage.
For combinations of land covers lis#ed above, an area-weighted"C�:x Al'sum should be computed based on the
equation C�: x A,_(C�x A,)+ (CZ x AZ)+ ...+(C„x A„},where AB=(A�+AZ+ ...+,q„),the total drainage basin area,
_ '- TABI,E 3.2.I.B C���'�'ICIEN�S�OR THE RATIaNAI,lYiETHai3"i�"EQUATION .
Design Storm Return Frequency aR bR
2 years 1.58 0.58
5 years 2.33 0.63
10 years 2.44 0.64
25 years 2.66 �.65
50 years 2.75 0.65
100 years 2.61 0.63
TABLE 3 21 C_-kR YALITES FOR T,USING THE RATIONAL METHOD - = _ -
Land Cover Category kR
Forest with heavy ground litter and meadow 2.5
Fallaw or minimum tiilage cultivation 4.7
Short grass pasture and lawns 7.0
Neariy bare ground 10,1
Grassed waterway 15.0
Paved area(sheet flow)and shallow gutter flow 20.0
2009 Surface Water Design Manua[ 1/9!2009
3-13
' SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.1.0 25-YEAR 24-HOUR ISOPLWIALS
�S — SN MONISN COUNTY
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1/9`2009 2009 Surface�Vater Desien Manual
3-16
� 3.2.1 RATIONAL IvfETHOD
FIGURE 3.2.1.D 100-YEAR 24-HOUR ISOPLUVIALS
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2009 Surface Water Design Manual 1/9/2009
3-17
AREAS CALCULA710NS
SUMMARY OF CALCULATIONS
AREA TOTAL TOTAL PERVIOUS IMPERVIOUS PERVIOUS IMPERVIOUS RUNOFF
NAME AREA(SF) AREA(AC) AREA(SF) AREA(SF) AREA(AC) AREA(AC) COEFFICIENT
TOTAL 98082.0000 2.2517
81 19606.0 0.450 5881.80 13724.20 0.135 0.315 0.317 0.71
62 782.0 0.01 a 78.20 703.80 0.002 0.016 0.015 0.84
B3 3440.0 0.079 344.00 3096.00 0.008 0.071 0.066 0.84
B4 2864.0 0.066 286.40 2577.60 0.007 0.059 0.055 0.84
B5 13274.0 0.305 3982.20 9291.80 0.091 0.213 0.215 0.71
B6 17552.0 0.403 5265.60 12286.40 0.121 0.282 0.284 0.71
67 1398.0 0.032 139.80 1258.20 0.003 0.029 0.027 0.84
B8 7296.0 0.167 729.60 6566.40 0.017 0.151 0.140 0.84
B9 1586.0 0.036 396.50 1189.50 0.009 0.027 0.027 0.74
B10 5460.0 0.125 1310.40 4149.60 0.030 0.095 0.093 0.74
TRACT A 7070.0 0.162 3393.60 3676.40 0.078 0.084 0.095 0.59
TRACT D 1400.0 0.032 1400.00 0.00 0.032 0.000 0.008 0.25
0.00 0.00
TOTAL 81728.0 1.876 23208.1 58519.9 0.533 1.343
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Project: REEDSHAW PLAT JOB#06085 CALCS BY:TLR DATE: 7/19/2072 I
RATIONA�METHOD PEAK RAINFALL INTENSITY Q=CIRA
-....- _-- --
design storm (years) 25 Enter 10 or 25
- _....-_
24 hr.precip.(in.) 3.5
LOCATION AREA cum.A Tc i, I, Q, pipe dia slope n Q�„ii Vr�u Q�Qrun V at Q, ipe leng travel tim
from to (acres) C AC (min) (cfs) (in.) (ft!ft) (cfs) (ft/s) (ft/s) (ft) (min)
B1 CB#1 0.450 0.71 0.320 0.320 6.3 0.80 2.81 0.90
--- --. ___- ---
CB#1 CB#3 12 0.0265 0.012 6.30 8.02 0.14 4.97 103 0.3
-- - -- -
B2 CB#2 0.018 0.84 0.015 0.015 6.6 0.78 2.72 0.04
CB#2 CB#3 12 0.0052 0.012 2.79 3.55 0.01 0.93 31 0.6
B3 CB#3 0.079 0.84 0.066 0.401 7.2 0.74 2.58 1.03
CB#3 CB#5 12 0.0443 0.012 8.15 10.37 0.13 6.23 134 0.4
___ _._. __ ----
64 CB#4 0.066 0.84 0.055 0.055 6.3 0.80 2.81 0.16
_.._._____.----__ _ ._._......_-
CB#4 CB#5 12 0.0052 0.012 2.79 3.55 0.06 1.57 31 0.3
-_ - - ---
65 CB#5 0.305 0.71 0.217 0.673 7.6 0.71 2.50 1.68
CB#5 CB#7 12 0.0222 0.012 5.77 7.34 0.29 5.26 67 0.2
66 CB#6 0.403 0.71 0.286 0.286 6.3 0.80 2.81 0.81
- ---.._........_ - --- --.._...._.
CB#6 CB#7 12 0.0206 0.012 5.55 7.07 0.15 4.40 53 0.2
- -........_.. - ---....._
B7 CB#7 0.032 0.84 0.027 0.986 7.8 0.70 2.45 2.42
-...._ . _ ---
CB#7 CB#9 12 0.0317 0.012 6.89 8.78 0.35 6.59 28 0.1
, - - -_- _.__.._.
B8 CB#8 0.167 0.84 0.140 0.140 6.3 0.80 2.81 0.39
CB#8 CB#9 12 0.0049 0.012 2.71 3.45 0.15� 2.15 43 0.3
B9 CB#9 0.036 0.74 0.027 1.153 7.8 0.70 2.44 2.81
I CB#9 CB#10 12 0.1055 0.012 12.57 16.01 0.22 10.90 104 0.2
610 CB#1Q 0.125 OJ4 0.093 1.245 8.0 0.69 2.41 3.00
_ � . ---..............-- --__..._
CB#10 POND 12 0.0869 0.012 11.41 14.53 0.26 10.19 34 0.1
12 0.3000 0.012 21.20 26.99 0.00 4.63 6 0.0
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15445 53RD AVE.S.,SEATTLE,WA 98188 PHONE(206)431-7970; FAX:(206)388-1648
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Project: REEDSHAW PLAT JOB#06085 CALCS BY:TLR DATE: 7/19/2012 ,
- .. _ _ __..
_ -
_� __...... _ _......_
RATIONAL METHOD PEAK RAINFALL INTENSITY Q=CIRA
design storm (yeai R= 100 Enter 2 or 100
24 hr.precip.(in.) PR= 3.g - -
LOCATION AREA Sum Tc i, I� Q� pipe dia slope n Q�,ii Vr„ii Q/Qi„�i V at Q, ipe leng travel tim
from to (acres) C C-A C-A (min) (cfs) (in.) (ft/ft) (cfs) (ft/s) (ft/s) (ft) (min)
B1 CB#1 0.450 0.71 0.320 0.320 6.3 0.82 3.19 1.02
-- -- - .- - --. -
CB#1 CB#3 12 0.0265 0.012 6.30 8.02 0.16 5.13 103 0.3
---- _ - _ __-
62 CB#2 0.018 0.84 0.015 0.015 6.6 0.79 3.09 0.05
CB#2 CB#3 12 0.0052 0.012 2.79 3.55 0.02 0.96 31 0.5
63 CB#3 0.079 0.84 0.066 0.401 7.2 0.75 2.94 1.18
_. _ ...._ _ ._..__ _._.
CB#3 CB#5 12 0.0443 0.012 8.15 10.37 0.14 6.45 134 0.3
---- - - _...
64 CB#4 0.066 0.84 0.055 0.055 6.3 0.82 3.19 0.18
_..__.._ _.._.. __ _ _
CB#4 CB#5 12 0.0052 0.012 2.79 3.55 0.06 1.66 31 0.3
B5 CB#5 0.305 0.71 0.217 0.673 7.5 0.73 2.86 1.92
CB#5 CB#7 12 0.0222 0.012 5.77 7.34 0.33 5.43 67 0.2
B6 CB#6 0.403 0.71 0.286 0.286 6.3 0.82 3.19 0.91
---- _.
CB#6 CB#7 12 0.0206 0.012 5.55 7.07 0.16 4.53 53 0.2
B7 CB#7 0.032 0.84 0.027 0.986 7.7 0.72 2.81 2.77
-_ ___ ----
CB#7 CB#9 12 0.0317 0.012 6.89 8.78 0.40 6.87 28 0.1 �
68 CB#8 0.167 0.84 0.140 0.140 6.3 0.82 3.19 0.45
CB#8 CB#9 12 0.0049 0.012 2.71 3.45 0.17 2.21 43 0.3 �
---...___ -- - - - - -
69 CB#9 0.036 0.74 0.027 1.153 7.8 0.72 2.79 3.22
CB#9 CB#10 12 0.1055 0.012 12.57 16.01 0.26 11.17 104 0.2
�.. .___ _---- ___
B10 CB#10 0.125 0.74 0.093 1.245 7.9 0.71 276 3.44
- - -- - -
CB#10 POND 12 0.0869 0.012 11.41 14.53 0.30 10.48 34 0.1
A .6 . 5 8.0 0.70 2.75 3.42
Detention pond primary overflow path '�
100 year pond overflow Q 1.47
--. __ _ -
..._
SF#1 CB#11 12 0.0380 0.012 7.55 9.61 0.19 6.38 57 0.1
1.47 -- - - -
-- _--- -- __ - -.. --
CB#11 EX.CB 12 0.0551 0.012 9.09 11.57 0.16 7.39 10 0.0
15445 53RD AVE.S.,SEATTLE,WA 98188 PHONE(206)431-7970; FAX:(206)388-1648
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DA Planning, Engineering, Project Management �,
Land Development Advisors, LLC 12865 SE 47th Place • Beilevue, WA 98006 �'�
425-466-5203
February 8, 2013
Ms. Kayren Kittrick
City of Renton 6th Floor
1055 South Grady Way
Renton, WA 98057
RE: Reed Shaw Plat
Detention Pond Modifications
LDA Job No. CALX-003
Dear Kayren, l
I have been retained by the builder/developer (Callidus Development) of this project to ,
prepare building permit applications. In preparing the background information to
prepare individual lot drainage plans, we reviewed the TIR prepared in August 2012 by
Pacific Engineering Design, LLC ("PED"). Their analysis assumed 1,750 square feet
("sf') of impervious area for each lot. In addition, limited infiltration and pervious �
pavement driveways were assumed that converted 0.24 acres ("ac") of impervious area
to grass for purposes of the detention calculations. The various areas and assumptions
are further detailed in their TIR (attached).
We have re-analyzed the pond and outlet structure and with some minor modifications
to the control structure, the detention facility will accommodate 1,750 sf of impervious
for each lot. Modifications include raising orifice elevations, changes to orifice �
diameters and raising the overflow elevation about an inch. Details follow. '
Developed Conditions
The following tables summarize the areas and developed runoff used in the original
PED design and those used in this analysis ("Proposed"). Full KCRTS printouts are
attached.
Table 1 — Developed Areas
Area PED ac Pro osed ac
Total Site 1.88 1 .88
Impervious 0.81 total 1.05 total
Private drives 0.16 0.16
Roads 0.38 0.38 '
On-lot 0.24 0.48
Pond 0.03 0.03
Lawn 1.07 0.83
,
� Ms. Kayren Kittrick
February 8, 2013
Page 2
Table 2 - Developed Runoff
Storm Event - ear PED cfs) Proposed cfs
100 0.61 0.67
50 0.52 0.58
25 0.36 0.40
10 0.32 0.40
2 0.27 0.33
Routinq Calculations
The values used in the PED analysis for the pond dimensional parameters were utilized
to redesign the control structure to accommodate the additional impervious area.
Resulting KCRTS output for the facility with control structure modifications is:
Retention/Detention Facility
Type of Facility: Detention Pond
Side Slope: 1.82 H:1V
Pond Bottom Length: 47.00 ft
Pond Bottom Width: 20.00 ft
Pond Bottom Area: 94C. sq. ft
Top Area at 1 ft. FB: 9�02. sq. ft
0.103 acres
Effective Storage Depth: 8.60 ft
Stage 0 Elevation: 0.00 ft
Storage Volume: 19912. cu. ft
0.457 ac-ft
Riser Head: 8.60 ft
Riser Diameter: 12.00 inches
Number of orifices: 3
Full Head Pipe
Orifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
i 0. 00 0.62 0.031
2 6.40 1.00 0.040 4.0
3 7.05 0.93 0.029 4.0
Top Notch Weir: None
Outilow Rating Curve: None
?.�ute Time Series through Facility '�,
Inflow Time Series File:reeddev.tsf I�
�utflow Time Series File:REE�� DCUT
Inflow/Outflow Analys_s
Peak Inflow Discharge: ;1. 5�2 �FS a- F; GO o-� J�-� ° `� Y�ar 8
Peak Outflow Discharge: �.424 CFS a_ =�:G� o� Ja� ° _� Yea� � I
Feak Reservoir Stage: 8.70 Ft ,
?eak Reservoir Elev: 8.70 Ft
P�ak Reservoir Storage: 20327. Cu-^t
. 0.467 Ac-Ft
3�,,d Inflow Outflow Feak St�rag�
.
' Ms. Kayren Kittrick
February 8, 2013
Page 3
Target CGlc S�a,e E-_ev (Cu-Ft) (:�c-_t)
1 0. 67 0.15 0.92 8.70 8.70 20327. 0.46?
2 0.33 0. 12 0.10 8.57 8.57 19805. 0.955
3 0.40 0. 09 0.08 7.87 7.87 17111. 0.393 10 yrok
4 0.40 ******* 0.08 7.85 7.85 17018. 0.391
5 0.35 ******* 0.05 7.10 7.10 14398. 0.3?=
6 0.34 0.05 0.04 6.54 6.54 12593. 0.28? 2 yrok
7 0.26 ******* 0.03 5.67 5. 67 10055. 0.231
8 0.28 ******* 0.02 4.43 4.43 6945. 0. 1��
Duration analysis results confirm the pond with modifications meets the level 2 flow
control duration criteria.
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Probabfiity Ezceedence
D��ration Ccmpar�son Anaylsis
Base F�le: reedex.tsf
New File: reedr dout.tsf
Cutoff Units: Discharge in ��F�
-----Fraction o= T-�ne----- ---------Chec;� o� Tclerar.c2-------
Cutoff Base '_Vew �Change Prc:�a�i=-ty �ase New %C=�a�ce
0.026 � 0.94�-02 0.1_E-01 18.6 � C.94E-02 0.026 0.026 0.4 50% ofthe 2 year ,
0.033 � 0.63E-02 0.64E-02 2.1 I C.63E-02 0.033 0.034 3.� values are equal,
0.040 I 0.50E-02 0.49=-02 -1.6 � 0.50E-02 0.090 0.040 -1.0 no change.
0.047 � 0.37E-C2 G.31E-02 -17.5 I 0.37E-02 0.047 0.045 -�.8
C.054 I 0.28E-02 0.23E-02 -2C.7 � 0.2�E-G2 �.C54 0.049 -1Q.�
O.G62 I 0.22E-02 0.18E-02 -17.0 I 0.22�-02 0.062 0.055 -1G.1
0.069 i 0.15E-02 O.laE-02 -6.7 I 0.15E-02 0.069 0.067 -2.�3
0.076 I O.�OE-OL 0.'lE-C2 4.8 I O.10E-02 0.076 0.077 1.8
0.083 I 0. 62E-03 0.57E-C3 -7.9 I C.62E-03 0.�83 D.062 -0.^
0.�9� � �.34E-03 0.28E-03 -19.0 � C.3�E-03 C.090 0.�9R -1. 9
_ . _�- , = ._3E-C_ S._�_-. - -� , ._ I � .��E-C� � . _��� �_ ,:�,y� - _ ,h.
� Ms. Kayren Kittrick I�,
February 8, 2013 ',
Page 4 !
�.104 , 0.16E-�3 �.CCE+O� -lOC.O � �."_6E-C3 0.104 0.095 -.. .� '
0.111 � 0.11E-03 O.COE+00 -100.0 I 0.11�-03 O.11l 0.097 -13.2
0.? 18 I 0.16E-04 O.GCE+00 -100.0 � 0.�6�-��� �.l"�8 0.099 -16.,�
Maximum positive excursion = 0.001 cfs ( 4.30) < 10%, O K
occurring at 0.033 cfs or the ?ase Data:reedex.tsf
and at 0.035 cfs on the New Data:-eedr dout.tsf
Maximu_n negative excursion = 0.019 cfs (-15.1�)
occurring at 0.118 cfs on the Base Da�G:reedex.tsf
and at O.C99 cfs on tr2 Ne�a Data:reed- dou�.�sf
Table 3 - Detention Pond/Control Structure Comparision
Element PED Proposed
Riser Hei ht 8.5' 8.6'
Orifice No. 1 0.63"/0.00' 0.62"/0.00' no chan es
Orifice No. 2 1.25"/5.75' 1.00"J6.40'
Orifice No. 3 0.88"/7.25' 0.93"/7.05'
Primarv Overflow
The original riser required 0.3' to pass the 100 year flow as calculated by KCRTS using
15-minute time steps. With the additional impervious area, the 100 year flow is 1.66 cfs.
Flow Frequer.cy Analys��s
^_ir.te Series File:reeddevl5.tsf
Froject Location:5ea-Tac
---Annual Peak Flcw Ra�es--- -----Flow Frequercy A�alysis-------
Flcw Rate Rank Time of Peak - - Peaks - - Ran.�c Return Prob
(CFS) (CFS) Feriod
0.50� 6 8/2�/C1 18:00 1.66 1 �OC.CO 0.990
0.367 8 1105/02 15:G0 1.13 2 25.00 0.960
1.13 2 12/08/02 17:'_5 0.7Q6 3 iO.00 �.900
0.403 7 8/23/04 14:30 0.688 4 �.00 0.800
0.688 4 1'/17/04 5:00 0.614 5 3.00 0.667
0.614 5 10/27/05 10:4� �.500 6 2.00 0.500
0.706 3 10/25/06 22:4� 0.403 7 i.3G 0.231
1.66 1 1/C9/08 6:3C 0.367 8 _.'0 0.091
Computed Peaks 1.48 50.00 0.980
The height over the riser is 0.3' as shown on the attached Riser Inflow Curve. With the
additional riser height, the maximum water surface is 0.3'+0.1' or 0.4' higher than
originally designed. Since it is less than the 0.5' minimum freeboard required over the
original riser, this is sufficient.
' Ms. Kayren Kittrick
February 8, 2013
Page 5
Secondarv Overflow
The PED rectangular weir was designed to pass 1.5 cfs in a required length of 5.22'. A
higher flow of 1.66 cfs would require a length of 1.66 cfs/1.5 cfs(5.22') = 5.78'. There
was 6' of weir provided, so ok.
Secondarv Inlet to Control Structure
The original "jailhouse window" required a 3.28' long x 0.3' depth opening to pass 1 .5
cfs. A 0.5' deep opening was provided that would nearly double it's capacity. By
inspection, the additional 0.16 cfs will not have a negative impact to the function of the
inlet.
� Ms. Kayren Kittrick
February 8, 2013
Page 6
APPENDIX
i