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HomeMy WebLinkAboutReport 02Z: -Lf'. l44 . c+a04 C • E74f l'i tl. VILKL! 3`1J. llcw. t-. Li 3
6MOM
�
Type ot?Min
mrm of PSI
P Pap
mbw
1990-1159
NDA
DRNG
13523
SE
189TH PLACE
REF 90-11 D6
68602
1980-1160
C
DRNG
13529
SE
189TH PLACE
13517 SE 189TH PL
66602
1990.1184
NDA
DRNG
13529
SE
189TH PLACE
REF 90-1106
68602
1990-1630
C
FLDG
19114
130TH AVE
5E
STREAM OVER -PLOW
68662
1991.1090
C
DRAINAGE
1$532
131ST AVE
5E
WATER PONDS IN YARD
5B5G2
1991-1090
NDA
DRAINAGE
18532
131ST AVE
SE
YARD PONDS
656G2
1891-1000
5R
DRAINAGE
18532
1316TAVE
BE,
TO CIP
68602
1993-0641
WQC
SEDIMENT
13120
5E
192ND ST
686G2
19940676
WCC
GREENK2O
SE
192ND & 134TH A
BE
DUCKWEED
6116G2
1995.0;70
WOO
OIL/CARS
15312
133RD AVE
BE
RESIDENTIAL CAR MAINTENANCE
686G2
19950374
C
FILLING
BE
192ND 8134TH
SE
WETLAND - REFD TO DDES
66602
1996-0391
FCR
POND?
19118
130TH PL
SE
HOLD-GPR WILL CALL HER 4 MORE DETAI
666G2
1996.0391
MDA
POND?
19118
130TH PL
SE
HOLD-GPR WILL CALL HER 4 MORE DETAI
68602
1996.0391
R
POND?
19118
130TH PL
BE
HOLD-GPR WILL CALL HER 4 MORE DETAI
r
506G2
1996-0480
C
CRK FLDS
13607
BE
192ND
? GROUNDWATER IMPACT WATER POND!
6B6G2
1996.0921
FOR
RID POND
13341
SE
196TH ST
OUTLET PIPE OBSTRUCTED ASSF8SMEN
6136G2
1998-1428
C
SWALE
18914
129TH PLACE
BE
OFFSITE FLOW IMPACTING PVT DRNG SY
666G2
1996-1428
NDA
SWALE
18914
129TH PLACE
SE
OFFSITE FLOW IMPACTING PVT DRNG BY
6WG2
1996-1428
R
SWALE
18914
129TH PLACE
SE
OFFSITE FLOW IMPACTING PVT DRNG SY
686G2
- 1996-1550
C
DRNG
19121
124TH AVE
BE
PLUGGED DM CULVERT IMPACT TO PVT
686F2
1996.1894
C
RUNOFF
13416
SE
167TH
WATER OVER SIDEWALK GROUNDWATE
686G2
1997-0940
C
DRNG
13007
SE
188TH PL
GROUNDWATERfSHEETFLOW PONDING
886G2
1997.1179
C
DRAINAGE
19113
121ST PL
SE
INSTALLATION OF DRNG IN RAW OLDIOFF
886F2
1997.1179
NDA
DRAINAGE
19113
121ST PL
BE
INSTALLATION OF DRNG IN RfW OLDIOFF
W6F2
1997-1178
R
DRAINAGE
19113
121ST PL
BE
;NSTALLATION OF DRNG IN RW OLWOFF
6861=2
1997.1301
C
DRAINAGE
19125
121ST PL
BE
SUBSTANDARD INSTIL OF DRNG SYS PVT
666F2
1997-1319
FOR
DUMPING
21709
146TH ST E
DUMPED BA77ERY IN RID POND
686G2
1998-0926
C
DRAINAGE
19133
121ST PL,
SE
APPARENT OBSTRUCTION IN ROAD DR
686172
1999.0174
FOR
CLG€NLET
13415
BE
187TH PL
INLET PIPE APPARENTLY 68STRUCT'ED
6WG2
1999.0449
C
SPRINGS
13518
BE
186TH PL
NEW SFR GROUND WATER INFIL ONTO P
686G2
1999-0632
C
EASEMENT
19114
130TH AVE
SE
INFO PROViOED ABOUT RID POND ON PR
688G2
1998-0679
FOR
FENCE
18932
133RD PL
SE
LEANING FENCE NEEDS REPAIR
686G2
2000-0398
C
DDM
12623
SE
192ND ST
REQUEST TO DIVERT FLOW DISCHARGIN
686F2
2003-0736
FOR
MNM
19000
'1,UTH AVE
BE
CEDAR BOARD FENCE AROUND PERIMET
66662
2001-0548
WOP
WQA
13120
BE
192ND ST
6MG2
20D2-0094
FI
REM
13055
SE
192ND ST
SWM#83 REMEASURE OF ORIGINAL 17.7
5MG2
2002.0094
FIR
REM
13055
BE
192ND ST
SWM#63 REMEASURE OF ORIGINAL 17.7
686G2
2002.0204
FCR
MMG
19000
134TH AVE SE
1) PSE UTILITY BOX DAMAGED, CALLED
686G2
2002.0424
C
DDM
13003
SE
188TH PL
SINKHOLE DEVELOPED APPARENTLY OV
688G2
2002-0424
NDA-
DDM
13003
9 F
1887H PL
SINKHOLE DEVELOPED APPARENTLY OV
666G2
Page 2 of 3
SEP,14.23a4 E:05FM KC WLRD
rio. 10E F. 3/3
C=wa
TVA
i1p of
A of Prfto
lo
Cab
2002.0424
R
DOV
13003
SE 188TH PL
SINKHOLE DEVELOPED APPARENTLY OV
686G2
2003.0256
C
DD IV
18759
130TH AVE SE
LOCAL PONDING PROBLEM. MAY RE THE
686G2
2003.0545
WOR
WQI3
18801
1287H PL SE
686F2
20030762
WQA
WQAI
19433
VASHON HWY SW
BMPS ary ALL iN PLACE
685F2
2003.0909
WQC
WQDR
18601
126TH PL BE
AUTO FLLIQ RESIDUE ON STREET A$ A R
686F2
S;Vbser�e,t
6,17y\
jecLi6_a
't'�c.4d{ beaver OlAtA
Fwp3of3
Fleuve des voiles and Cogger Plats
Runoff Calcs Compare offsite flows to fully developed onsite flows to
determine need for bypass.
5/30/08
FLEUVE DES VOILES;
Flow Frequency Analysis
Time series File:offsite.tsf
Project Location sea -Tac
---Annual Peak Flow Rates ---
Flow Rate Rank Time of Peak
(CFS)
0.411 4 2/09/01 15:00
0.252 7 1/05/02 16:00
0.441 2 2/27/03 7:00
0.191 8 8/26/04 2:00
0.254 6 1/05/05 8:00
0.420 3 1/18/06 16:00
0.395 5 11/24/06 3:00
0.795 1 1/09/08 6:00
Computed Peaks
Flow Freqquency Analysis
Time series File: devsite.tSf
Project Location:sea-Tac
---Annual Peak Flow Rates ---
Flow Rate Rank Time of Peak
(CFS)
1.25 6 2/09/01 2:00
1.04 8 1/05/02 16:00
1.50 3 2/27/03 7:00
1.14 7 8/26/04 2:00
1.36 4 10/28/04 16:00
1.33 5 1/18/06 16:00
1.66 2 10/26/06 0:00
2.51 1 1/09/08 6:00
Computed Peaks
COGGER:
Flow Frequency Analysis
Time series File.offsite.tsf
Project Location:sea-Tac
---Annual Peak Flow Rates ---
Flow Rate Rank Time of Peak
(CFS)
Computed Peaks
Computed Peaks
computed Peaks
Computed Peaks
Computed Peaks
Computed Peaks
computed Peaks
computed Peaks
Flow Frequency Analysis
Time series File:devsite.tsf
Project Location:sea-Tac
-----Flow
Frequency
Analysis-------
- - Peaks
- - Peaks
- - Rank
Return
Prob
(CFS)
Period
Period
2.51
0.795
1
100.00
0.990
0.441
2
25.00
0.960
0.420
3
10.00
0.900
0.411
4
5.00
0.800
0.395
5
3.00
0.667
0.254
6
2.00
0.500
0.252
7
1.30
0.231
0.191
8
1.10
0,091
0.677
50.00
50.00
0.980
-----Flow
Frequency
Analysis-------
- - Peaks
- - Rank
Return
Prob
(CFS)
0.266
Period
0.980
2.51
1
100.00
0.990
1.66
2
25.00
0.960
1.50
3
10.00
0.900
1.36
4
5.00
0.800
1.33
5
3.00
0.667
1.25
6
2.00
0.500
1.14
7
1.30
0.231
1.04
8
1.10
0.091
2.23
50.00
0.980
LogPearson III Coefficients
Mean= -0.897 stdDev= 0.140
skew= 0.468
-----Flow
Frequency Analysis-------
- - Peaks
- - Rank Return
Prob
(CFS)
0.299
Period
100.00
0.990 OD -Y (Z
0.266
50.00
0.980
0.234
25.00
0.960
0.194
10.00
0.900
0.186
8.00
0.875
0.165
5.00
0.800
0.124
2.00
0.500
0.099
1.30
0.231
LogPearson III Coefficients
Mean= -0.672 stdDev= 0.099
skew= 0.516
---Annual Peak Flow Rates--- -----Flow Frequency Analysis -------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Computed Peaks 0.394 100.00 0.990
Computed Peaks 0.361 50.00 0.980
Computed Peaks 0.330 25.00 0.960
computed Peaks 0.288 10.00 0.900
computed Peaks 0.280 8.00 0.875
computed Peaks 0.256 5.00 0.800
computed Peaks 0.209 2.00 0.500
computed Peaks 0.178 1.30 0.231
Existing upstream (Offsite) 100 -year Q = 0.795 + 0.299 = 1.094 cfs
50% of 100 -year Developed (undetained) Q = 0.5*2.51 + 0.394 = 1.452 cfs
1.094cfs < 1.452cfs; therefore, no need to bypass offsite flows.
P�L DS S C�
PtL U"DE-T, P .
SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
KCRTS is the "Effective Impervious Area" (EIA), the total impervious area multiplied by the effective
impervious fraction. See Table 3.2.2.E, p. 3-29 for effective impervious fractions that apply to standard
impervious surfaces. Table 1.2.3.0 lists effective impervious factions for alternative materials and
approaches.
Non -effective impervious area (i.e., total impervious area less EIA) is assumed to have the same
hydrologic response as the immediately surrounding pervious area. For example, for existing
residential areas with rooftops draining to splash pads on lawns or landscaping, the non -effective portion
of the roof areas would be treated as pasture for predevelopment conditions (if DU/GA < 4.0) and grass
for post -development conditions. Note: Credits.for infiltration/dispersion of downspouts on individual
lots in proposed single family residential subdivisions are applied separately on a site-specific basis (see
Note 3, Table 3.2.2.E).
The effective impervious fraction can be selected from Table 3.2.2.E or determined from detailed site
surveys. With the exception of figures for compacted gravel and dirt roads and parking lots, the figures in
Table 3.2.2.E are average figures cited by the USGS (Dinicola, 1990).
Fic�ky-e_ -- 3.9 A -(.)e 0,30 X04 r- 0110 Ac- Ime,
3 z AG. k� �. (pas �Are,
.{~ 1 0- A c— r c 51—
I.,y$ Ac. N4, V, (Ina 5hA )
1/24/2005 2005 Surface water Design Manual
3-28
Dwelling Units/Gross
Acre
% Impervious{�f
Dwelling Units/Gross
Acre
% Impervious
1.0 DU/GA
1512)
4.5 DUIGA
46
1.5 DU/GA
20
5.0 DU/GA
48
2.0 DUIGA
25
5.5 DU/GA
50
2.5 DUIGA
30
6.0 DU/GA
52
3.0 DU/GA
34
6.5 DU/GA
54
3.5 DU/GA
38
7.0 DUIGA
56
4.0 DU/GA
42
7.5 DUIGA
58
For PUDs, condominiums, apartments, commercial businesses, and
industrial areas, percent impervious coverage must be computed.
Notes:
(�) Includes streets and sidewalks. Q,
«} These figures should be adjusted by the effective impervious fraction given in Table 3.2.2.E, if
applicable. Values from Table 3.2.2.E may be interpolated as necessary.
Fic�ky-e_ -- 3.9 A -(.)e 0,30 X04 r- 0110 Ac- Ime,
3 z AG. k� �. (pas �Are,
.{~ 1 0- A c— r c 51—
I.,y$ Ac. N4, V, (Ina 5hA )
1/24/2005 2005 Surface water Design Manual
3-28
APPENDIX B-1
DRAINAGE COMPLAINT ANALYSIS
(previously submitted)
SOOS CREEK PLAT
DRAINAGE COMPLAINT ANALYSIS
LEVE
TECHNICAL DESIGN AND INFORMATION REPORT
FOR PRELIMINARY PLAT REVIEW
For the King County DDES: SUBDIVISION FILE A03PO286_
Addendum to
Report of January 26, 2004
f
Richard A Boston
Boston Design and Development Co LLC
425-226-2145:
Neal M Ja ue P.E.
Jacques Consulting
206-242-5322
Soos Creek Plat By Jacques Consulting
TIR March 20, 2004
0 41
TIR Addendum
DRAINAGE COMPLAINTS
King County records were examined for downstream drainage complaints per core requirement
#2. Note that at the discharge point this project contributes approximately 2% to the drainage
basin flow thus requiring %• mile investigation. But this report investigated southeasterly for one
mile along the Soos Creek Basin (see attached map). The area was inspected and the
ComM
complaint lisfims. for a ane mile r-adixg were examined. The Soos Creek drainage basin in this
area is relatively flat wide and heavily vegetated (grass) with no erosion or flooding problems.
The complaint list is attached but they all deal with issues which are uphill either west or east of
the Soos Creek Basin.
Only one was somewhat relevant, Complaint Number 96-1550, which is a class I issue
(attached). This complaint in 1996, describes the I r culvert across 124th Ave SE at SE 192 as
blocked and thus erosion over the 124th gravel road. The solution, to unblock it, was done. The
downstream flow from this project does not flow in this location but because the project access
road goes over it, it was included. In February 2004 property owners were notified of King
Couq y's plan to widen SE 192 for a left tura lane, thus this culvert will lWely be modified. The
subject project final engineering will have consideration for the revised County intersection
design.
The remainder of the complaints had no relation at all with the project. The five page list and a
snap showning location of the most significant problems (eight ponding/flooding complaints) is
attached for general reference. These all involved tributary flows from west or east down into
drainage systems flowing eventually into Soos Creek Basin. None have any relation to this-
projects
hisprojects drainage in the Creek itself.
In conclusion, for the subject project drainage path, there is no indication of any category 1, 2, or
3 issues with drainage within one mile downstream. Note the TIR downstream analysis dated
Jan 26, 2004 for additional discussion.
1
Soos Creek Plat
TIR
N
By Jacques Consulfing
March 20, 2044
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DRAINAGE RgVEMGATION REPORT
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1991.1005 C DRAII4AGE 13318 BE 199TH ST 6860#
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t 53 STUDY SE WEPLAMD QRM*00 I'p4E CFIAWN
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APPENDIX C
ANALYSIS AND DESIGN
APPENDIX C-1
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FLEUYE UE
EXISTING (SF):
SI TE
BUILDING: 295 (0.03 AC)
PAVEMENT: 1,516 (0.03 AC)
FOREST: 262,258 (6.02 AC
SUBTOTAL: 264,069 (6.06 AC)
124TH AVE SE
PAVEMENT: 7,064 (0.16 AC)
PASTURE: 4,749 (0.11 AC)
FOREST: 3,329 (0.08 AC
SUBTOTAL: 15,142 (0.35 AC)
TOTAL: 279,211 (6.41 AC)
PROPOSED (SF):
SI TE
BUILDINGS: 123,097 (2.83 AC)
PAVEMENT: 38,504 (0.88 AC)
SIDEWALK: 5,110 (0.12 AC)
POND: 17,000 (0.39 AC)
LANDSCAPE: 80,358. 1.84 AC
SUBTOTAL: 264,069 (6.06 AC)
BY-PASS (124TH AVE SE)
PAVEMENT,12,681 (0.29 AC)
SIDEALK: 2,461 (0.06 ACJ
SUBTOTAL: 15,142 (0.35 AC)
TOTAL: 279,211 (6.41 AC)
0 75 150
SCALE: 1" = 150 ft.
OFF --SITE TRIG. AREA (SF):
IMPERVIOUS: 30,893 (0.71 AC)
PASTURE: 140,734 (3.23 AC)
FOREST: 41,817 (0.96 AC
TOTAL: 213,444 (4.90 AC)
bypass.tsf
T
1.00000
T
[T] Enter the Analysis TOOLS nodule
[P] compute PEAKS and F1Ow Frequencies
exist.tsf
exist.pks
[P]Compute PEAKS and Flow Frequencies
dev.tsf
dev.pks
[P] compute PEAKS and Flow Frequencies
bypass.tsf
by ass.pks
[R RETURN to Previous Menu
[X exit KCRTS Program
KCRTS Program...
File Directory:
C:\KC_SWDM\KC_DATA\
[C]
CREATE a new
Time Series
ST
7.06
0.00
0.000000
Till Forest
3.34
0.00
0.000000
Till Pasture
0.00
0.00
0.000000
Till Grass
O.OD
0.00
0.000000
outwash Forest
0.00
0.00
0.000000
outwash Pasture
0.00
0.00
0.000000
outwash Grass
0.00
0.00
0.000000
wetland
0.91
0.00
0.000000
Impervious
exist.tsf
T
1.00000
T
[C]
CREATE a new
Time Series
ST
0.96
0.00
0.000000
Till Forest
3.23
O.DO
0.000000
Till Pasture
1.84
0.00
0.000000
Till Grass
0.00
0.00
0.000000
outwash Forest
0.00
0.00
0.000000
outwash Pasture
0.00
0.00
0.000000
outwash Grass
0.00
0.00
0.000000
wetland
4.93
0.00
0.000000
Impervious
dev.tsf
T
1.00000
T
[C]
CREATE a new
Time Series
ST
0.00
0.00
0.000000
Till Forest
0.00
0.00
0.000000
Till Pasture
0.00
0.00
0.000000
Till Grass
0.00
0.00
0.000000
Outwash Forest
0.00
0.00
0.000000
outwash Pasture
0.00
0.00
0.000000
outwash Grass
0.00
0.00
0.000000
wetland
0.35
0.00
0.000000
Impervious
bypass.tsf
T
1.00000
T
[T] Enter the Analysis TOOLS nodule
[P] compute PEAKS and F1Ow Frequencies
exist.tsf
exist.pks
[P]Compute PEAKS and Flow Frequencies
dev.tsf
dev.pks
[P] compute PEAKS and Flow Frequencies
bypass.tsf
by ass.pks
[R RETURN to Previous Menu
[X exit KCRTS Program
Fleuve des voiles Plat
Runoff Cal cs
6/13/08
Flow Frequency Analysis
Time Series File:exist.tsf
Project Location:5ea-Tac
---Annual Peak Flow Rates ---
Flow Rate Rank Time of Peak
(CFS)
0.827 2 2/09/01 15:00
0.397 7 1/05/02 16:00
0.774 3 2/28/03 3:00
0.242 8 8/26/04 2:00
0.458 6 1/05/05 8:00
0.749 4 1/18/06 16:00
0.694 5 11/24/06 4:00
1.34 1 1/09/08 6:00
computed Peaks
Flow Frequency Analysis
Time series File:dev.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates ---
Flow Rate Rank Time of Peak
(CFS)
1.57 5 2/09/01 2:00
1.24 8 1/05/02 16:00
1.86 2 2/27/03 7:00
1.28 7 8/26/04 2:00
1.54 6 10/28/04 16:00
1.68 4 1/18/06 16:00
1.85 3 10/26/06 0:00
3.18 1 1/09/08 6:00
Computed Peaks
Flaw Frequency Analysis
Time series File:bypass.tsf
Project Location:5ea-Tac
---Annual Peak Flow Rates ---
Flow Rate Rank Time of peak
(CFS)
0.085 7 2/09/01 2:00
0.075 8 1/05/02 16:00
0.104 3 12/08/02 18:00
0.087 6 8/26/04 2:00
0.104 4 10/28/04 16:00
0.091 5 1/18/06 16:00
0.127 2 10/26/06 0:00
0.165 1 1/09/08 6:00
Computed Peaks
Level 1 Det Pond (4.5' deep)
Qmax = (4/3*0.458)-0.087 = 0.524
Ht = 3/4*4.5 = 3.38'
-----Flow
Frequency
Analysis -------
- - Peaks
- - Rank
Return
Prob
(CFS)
Period
Period
3,18
1.34
1
100.00
0.990
0.827
2
25.00
0.960
0.774
3
10.00
0.900
0.749
4
5.00
0.800
0.694
5
3.00
0.667
0,458
6
2.00
0.500
0.397
7
1.30
0.231
0.242
8
1.10
0.091
1.17
50.00
50.00
0.980
-----Flow
Frequency
Analysis -------
- - Peaks
- - Rank Return
Prob
(cps)
Prob
Period
3,18
1
100.00
0.990
1.86
2
25.00
0.960
1.85
3
10.00
0.900
1.68
4
5.00
0.800
1.57
5
3.00
0.667
1.54
6
2.00
0.500
1.28
7
1.30
0.231
1.24
8
1.10
0.091
2.74
0.091
50.00
0.980
-----Flow
Frequency
Analysis-------
- - Peaks
- - Rank
Return
Prob
(CFS)
Period
0.165
1
100.00
0.990
0.127
2
25.00
0.960
0.104
3
10.00
0.900
0.104
4
5.00
0.800
0.091
5
3.00
0.667
0.087
6
2.00
0.500
0.085
7
1.30
0.231
0.075
8
1,10
0.091
0.153
50.00
0.980
Fleuve des Voiles
Retention/Detention Facility
6/16/08
Type of Facility:
Detention Pond
207.
Side Slope:
3.00
H:1V
6926.
Pond Bottom Length:
143.78
ft
0.010
Pond Bottom Width:
47.93
ft
0.09
Pond Bottom Area:
6891,
sq. ft
0.076
Top Area at I ft. FB:
14307,
sq. ft
0.13
906.
0.328
acres
0.00
Effective Storage Depth:
4.50
ft
1117.
Stage 0 Elevation:
0.00
ft
7076.
Storage Volume:
43751.
cu. ft
0.031
0.107
1.004
ac -ft
0.22
Riser Head:
4.50
ft
0.116
Riser Diameter:
12.00
inches
0.25
Number of orifices:
2
0.124
0.00
7181.
Full Head
Pipe
orifice # Height
Diameter Discharge
Diameter
(ft)
(in)
(CFS)
(in)
1 0.00
3.02
0.524
0..00.
2 3.38
2.71
0.210
6.0
Top Notch Weir:
None
O.OQ
7535.
Outflow Rating Curve:
None
4726.
0.108
Stage Elevation Storage Discharge Percolation Surf Area
(ft) (ft) (cu. ft) (ac -ft) (cfs) (cfs)_ (sq. ft)
0.03
0.03
207.
0.005
0.044
0.00
6926.
0.06
0.06
416.
0.010
0.062
0.00
6960.
0.09
0.09
625.
0.014
0.076
0100
6995.
0.13
0.13
906.
0.021
0.088
0.00
7041,
0.16
0.16
1117.
0.026
0.098
0.00
7076.
0.19
0.19
1330.
0.031
0.107
0.00
7111.
0.22
0.22
1544.
0.035
0.116
0.00
7146.
0.25
0.25
1759.
0.040
0.124
0.00
7181.
0.35
0.35
2483. �
0.057
0.146 /�
0.00
7298.
0.45
0.45
3219
0.074
0.166 rr
0..00.
7416.
0.55
0.55
3966.
0.091
0.183
O.OQ
7535.
0.65
0.65
4726.
0.108
0.199
0.00
7654.
0.75
0.75
5497.
0.126
0.214
O.DO
7774.
0.85
0.65
6281.
0.144
0.228
0.00
7895.
9
0.95
7076.1
0.162
0.241,
0.00
8017,
1.05
1.05
7884.
0.181
0.253
0.00
8139.
1.15
1.15
8704,
0.200
0.265
0.00
8262.
1.25
1.25
9536.
0.219
0.276
0.00
8385.
1.35
1.35
10381_
0.238
0.2877?0�
0.00
8510.
1.45
1.45
��?j
11238.�r
0.256
0_.298}
0.00
8635.
1.55
1,55
12108,
0.278
0.308
0.00
8761.
1.65
1.65
12990.
0.298
0.317
0.00
8887.
1.75
1.75
13885.
0.319
0.327
0.00
9014.
1.85
1.85
14793.` %\
0.340
0.336 �(�
0.04
9142.
1.95
1.95
15714. iA`
0.361
0.345 ,77
0.00
9271.
2.45,
_ 2.05
16647.
0.382
0. 59 6.0
.
2.15
2.15
17594.
0.404
0.362
0.00
9531.
2.25
2.25
18554. 0,426
0.371
0.00
9662.
9793.
2.35
2.35
19526. 4311/0.448
0.379 (�
0.00
2.45
2.45
20512.x,
0.471
0.387 �' 1�
0.00
9926.
2.55
_
2.55
21512,
0.494
0.395
0.00
1 a .
2.65
2.65
22524.
0.517
0.402
0.00
10192.
2.75
2.75
23550. l
0.541
0.410
0.00
10327.
2.85
2.85
24589, 10.564
0.41.7
0.00
10462.
2.95
2.95
25642.
0.589
0.424
0.00
10598.
3.05
3.05
26709.
0.613
0.431
0.00
10734.
3.15
3.15
27789.
0.638
0.439
0.00
10872.
3.25
3.25
28663.
0.663
0.445
0.00
11010.
3.35
3.35
29991.
0.689
0.452
0.00
11149,
3.38
3.38
30326.
0.696
0.454
0.00
11190.
3. 41
3 4
30663.
D.704
0.458
0.00
11232.
3.44
3.44
31000.
0.712
0.465
0.00
11274.
3.46
3.46
31226. .,
0.717
0.477
0.00
11302.
3.49
3.49
31566.
0.725
1�
0.4911 1
0.00
11344,
----------------------------------
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series File:rdout
POC Time Series File:dsout
Inflow/Outflow Analysis
Peak Inflow Discharge: 3.18 CFS at 6:00 on Jan 9 in Year 8
Peak Outflow Discharge: 2.31 CFS at 10:00 on Jan 9 in Year 8
Peak Reservoir Stage: 4.79 Ft
Peak Reservoir Elev: 4.79 Ft
3.55
3.55
32249.
0.740
0.530
0.00
11428.
3.58
3.58
32592.
0.748
0.555
0.00
11471.
3.61
3.61
32937.
0.756
0.563
0.00
11513.
3.71
3.71
34096.
0.783
0.589
0.00
11654.
3.81
3.81
35268.iQ0.810
0.611 0.00
11796.
3.91
3.91
36455�j
0.837
0.632
, 0.00
11939.
, -'"
`r $"�'
0
12C83.
4.11
4.11
38871.
0.892
0.670
0.00
12227.
4.21
4.21
40101.
0.921
0.687
0.00
12372,
4.31
4.31
41346.
0.949
0.704
0.00
12518.
4.41
4.41
42605.
0.978
0.720
0.00
12664.
9.50
4. 0
4 751.
1.009
0.739
0.00
127 96,
4. 0
45038.
1.034
1.060
0.00
12994,
4.70
4.70
46340.
1.064
1.630
0.00
13093.
4.80
4.80
47656,
1.094
2.380
0.00
13242.
05.00
4.90
4.90
48988.
1.125
3.180
0.00
13392. 00-
5.00
5.00
50335.
1.156
3.480
0.00
13543.
5.10
5.10
51697.
1.187
3.750
0.00
13694.
5.20
5.20
53074.
1.218
4.000
0.00
13846,
5.30
5.30
54466_
1.250
4.230
0.00
13999.
5.40
5.40
55873.
1.283
4.440
0.00
14152.
,5.50
5.50
57296.
1.315
4.650
0.00
14307.
5.60
5.60
58735.
1.348
4.850
0.00
14462,
5.70
5.70
60189.
1.362
5.040
0.00
14617.
5.80
5.80
61658.
1.415
5.220
0.00
14774.
5.90
5.90
63143.
1.950
5.390
0.00
14931.
6.00
6.00
64644.
1.484
5.560
0.00
15089.
6.10
6.10
66161.
1.519
5.720
0.00
15247,
6.20
6.20
67694.
1.554
5.880
0.00
15407.
6.30
6.30
69243.
1.590
6.030
0.00
15567.
6.40
6.40
70807.
1.626
6.180
0.00
15728.
6.50
6.50
72388.
1.662
6.330
0.00
15889.
Hvd
Inflow
Outflow
Peak
Storage
Stage
Flev
(Cu-Ft1
(Ac-Ft1
1
3.18
2.31
4.79
4.79
47529.
1.091.
2
1.57
1.11
4.61
4.61
45153.
1.037
3
1.59
0.74
4.50
4.50
43766,
1.005
4
1.68
0.71
4.37
4.37
42041.
0.965
5
1.B6
0.65
4.01
4.01
37642.
0.864
6
1.01
0.42
2.93
2.93
25394.
0.583
7
1.24
0.33
1.76
1.76
13940.
0.320
6
1.28
0.31
1.55
1.55
12149.
0.279
Hyd
R/D Facility
Tributary Reservoir
POC Outflow
Outflow
Inflow Inflow
Target
Calc
1
2.31
0.17 ++x*x*xx
*x*+:**
2.37
2
1.11
0.09 ********
***++xx
1115
3
0.74
0.09 ********
0.77
0.77
4
0.71
0.09 +**+++**
*xx***+
0.75
5
0.65
0.10 +**+++**
*******
0.68
6
0.42
0.06 ********
0.46
0.96
7
0.33
0.07 +*+x*.++
xx*****
0.35
8
0.31
0.09 +*+*xxxx
****+**
0.33
----------------------------------
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series File:rdout
POC Time Series File:dsout
Inflow/Outflow Analysis
Peak Inflow Discharge: 3.18 CFS at 6:00 on Jan 9 in Year 8
Peak Outflow Discharge: 2.31 CFS at 10:00 on Jan 9 in Year 8
Peak Reservoir Stage: 4.79 Ft
Peak Reservoir Elev: 4.79 Ft
Peak Reservoir Storage: 47529. Cu -Ft
1.091 Ac -Ft
Add Time Series:bypass.tsf
Peak Summed Discharge: 2.37 CFS at 10:00 on Jan 9 in Year 8
Point of Compliance File:dsout.tsf
Flow Frequency Analysis
Time Series File:rdout.tsf
Project Location:8ea-Tac
---Annual
Peak
Flow Rates ---
Flow Rate
Rank
Time of
Peak
[CFS}
2.37
1
100.00
1.11
2
2/09/01
19:00
0.328
7
1/06/02
5:00
0.652
5
2/29/03
7:00
0.308
8
8/24/04
0:00
0.422
6
1/05/05
14:00
0.713
4
1/18/06
22:00
0.738
3
11/24/06
7:00
2.31
1
1/09/08
10:00
Computed Peaks
Flow Frequency Analysis
Time Series File:dsout.tsf
Project Location:Sea-Tac
---Annual
Peak
Flow Rates ---
Flow Rate
Rank
Time of
Peak
(CFS)
1.15
2
2/09/01
19:00
0.354
7
1/06/02
3:00
0.680
5
2/28/03
6:00
0.333
8
8/23/04
23:00
0.457
6
1/05105
8:00
0.749
4
1/18/06
21:00
0.771
3
11/24/06
6:00-
2.37
1
1/09/08
10:00
Computed Peaks
-----Flow Frequency Analysis-------
- - Peaks - - Rank Return Prob
(CFS) (ft) Period
2.31 4.79 1 100.00 0.990
1.11 4.61 2 25.00 0.960
0.738 4.50 3 10.00 0.900
0.713 4.36 4 5.00 0.800
0.652 4.01 5 3.00 0.667
0.422 2.92 6 2.00 0.500
0.328 1.76 7 1.30 0.231
0.308 1.55 8 1.10 0.091
1.91 4.74 50.00 0.980
-----Flow Frequency Analysis-------
- - Peaks -
- Rank
Return
Prob
(CFS)
Period
2.37
1
100.00
0.990
1.15
2
25.00
0.960
0.771
3
10.00
0.900
0.749
4
5.00
0.900
0.680
5
3.00
0.667
0.457
6
2.00
0.500
0.354
7
1.30
0.231
0.333
8
1.10
0.091
1.96
50.00
0.980
0
0
0
LCJ
a
N
O
�LO
L
N
N
Ln
rn
0
Co
ti
r,
(SJO) e5jegosiq
0
co
0
N
a
r
LS
N
•r
COGGER PLAU
EXISTING SITE (SF):
FOREST: 54,573 (1:25 AC)
TOTAL: 54,573 (1:25 AC)
PROPOSED SITE (SF):
BUILDINGS: 24,184 (0.56 AC)
PAVEMENT: 9,806 (0.22 AC)
SIDEWALK: 1,178 (0.03 AC)
LANDSCAPE: 19,405 (0.45 AC)
TOTAL: 54,573 (1.25 AC)
OFF-SITE TRIG. AREA (SF):
IMPERVIOUS: 14,113 (0.32 AC)
PASTURE: 64,295 (1:48 AC)
TOTAL: 78,408 (1.80 AC)
KCRTS Program...File
0.00
Directory:
Till Forest
C:\KC_SWDM\KC_DATA\
0.00
0.000000
Till Pasture
[C] CREATE a new
Time Series
0.000000
5T
0.00
0.00
0.000000
1.25
0.00
0.000000
Till Forest
1.48
0.00
0.000000
Till Pasture
0.00
0.00
0.000000
Till Grass
0.00
0.00
0.000000
Outwash Forest
0.00
0.00
0.000000
outwash Pasture
0.00
0.00
0.000000
Outwash Grass
0.00
0.00
0.000000
wetland
0.32
0.00
0.000000
Impervious
exiSt. tsf
F
1.00000
T
[C] CREATE a new Time Series
ST
0.00
0.00
0.000000
Till Forest
1.48
0.00
0.000000
Till Pasture
0.44
0.00
0.000000
Till Grass
0.00
0.00
0.000000
Outwash Forest
0.00
0.00
0.000000
Outwash Pasture
0.00
0.00
0.000000
Outwash Grass
0.00
0.00
0.000000
wetland
1.13
0.00
0.000000
Impervious
dev.tsf
F
1.00000
T
[T] Enter the Analysis TOOLS Module
P Compute PEAKS and Flow Frequencies
exist.tsf
exist.pks
[P] Compute PEAKS and Flow Frequencies
dev.tsf
dev.pks
[R] RETURN to Previous Menu
[X] eXit KCRTS Program
corp- LVed Z
1-, VV,Le S E s ) V)eu -
Cogger Plat
Runoff talcs
6/16/08
Flow Frequency Analysis
Time Series File:exist.tSf
Project LOCation:sea-Tac
--Annual Peak Flow Rates ---
Flow Rate Rank Time of Peak
(CFS)
Computed Peaks
Computed Peaks
computed Peaks
computed Peaks
computed Peaks
computed Peaks
computed Peaks
computed Peaks
LogPearson III Coefficients
Mean= -0.825 Stdoev= 0.162
skew= 0.319
-----Flow
Frequency Analysis -------
- - Peaks
- - Rank Return
Prob
(CFS)
Period
Period
0.389
100.00
0.990
0.343
50.00
0.980
0.299
25.00
0.960
0.244
10.00
0.900
0.233
8.00
0.875
0.204
5.00
0.800
0.147
2.00
0.500
0.112
1.30
0.231
Flow Frequency Analysis LogPearson III coefficients
Time Series File.dev.tsf Mean= -0.445 stdDev= 0.119
Project Location:Sea-Tac skew= 0.388
---Annual Peak Flow Rates---
FlOw Rate Rank Time of Peak
(CFS)
computed Peaks
computed Peaks
Computed Peaks
computed Peaks
computed Peaks
computed Peaks
Computed Peaks
computed Peaks
Level 2 Det Pond (4.5' deep)
Int size = (0.343-(0.147*0.5)/36-1
0.008
1st int. = 0.147*0.5
0.074
Qmax (orif 1) = 4/3*0.074
= 0.099
Ht (orif 2) = 3/4*4.5
3.38'
-----Flow
Frequency Analysis-------
- - Peaks
- - Rank Return
Prob
(CFS)
Period
0.731
100.00
0.990
0.664
50.00
0.980
0,599
25.00
0.960
0.514
10.00
0.900
0,497
8.00
0.875
0,449
5.00
0.800
0.353
2.00
0,500
0,290
1.30
0,231
Cogger Plat
Retention/Detention Facility
6/16/08
Type of Facility:
Detention Pond
15.
Side Slope:
3.00
H:lV
1479•
Pond Bottom Length:
67.00
ft
0.001
Pond Bottom Width:
22.00
ft
0.04
Pond Bottom Area:
1474,
sq. ft
0.008
Top Area at 1 ft. FB:
5500.
sq. ft
0.05
74.
0.126
acres
0.00
Effective Storage Depth:
4.50
ft
105.
Stage 0 Elevation:
0.00
ft
1512.
Storage Volume:
13133.
cu. ft
0.003
0.012
0.301
ac -ft
0.09
Riser Head:
4.50
€t
0.013
Riser Diameter:
12.00
inches
0.10
Number of orifices:
2
0.014
0.00
1528.
Full Head
Pipe
Orifice # Height
Diameter Discharge
Diameter
(ft)
(in)
(CFS}
(in)
1 0.00
1.25
0.090
0.00
2 3.10
1.80
0.104
4.0
Top Notch Weir:
None
0.00
1693.
Outflow Rating Curve:
None
Stage Elevation Storage Discharge Percolation Surf Area
(ft) (ft) (cu. ft} (ac -ft) (cfs) (cfs) (s4. ft)
0.01
0.01
15.
0.000
0.005
0.00
1479•
0.03
0.03
45.
0.001
0.007
0.00
1490.
0.04
0.09
59.
0.001
0.008
0.00
1495,
0.05
0.05
74.
0.002
0.010
0.00
1501.
0.07
0.07
105.
0.002
0.011
0.00
1512.
0.08
0.08
120.
0.003
0.012
0.00
1517,
0.09
0.09
135.
0.003
0.013
0.00
1522.
0.10
0.10
150.
0.003
0.014
0.00
1528.
0.20
0.20
306.
0.007
0.019
0.00
1562.
0.30
0.30
467.
0.011
0.023
0.00
1637.
0.40
0.40
633.
0.015
0.027
0.00
1693.
0
qn.
0.023
0,033
0.00
1807.
0.70
0.70
1167.
0.027
0.036
0.00
1665.
0.80
0.80
1356.
0.031
0.038
0.00
1924,
0.90
0.90
1552.
0.036
0.040
0.00
1989.
�..
0.
045
0,045
0.00
2105.
1.20
1.20
2174.
0,050
0.047
0.00
2167•
1.30
1.30
2394,
0,055
0.048
0.00
2229.
1.40
1.40
2620.
0.060
6.050
4 0.00
2292.
1.60 1.6U SU`Ji . U.UIi U.Uz9 U.UU --
1.70 1.70 3336. 0.077 0.055 0.00 2466.
1.80 1.80 3588, 0.082 0.057 0.00 2552.
1 an i an '3847. 0.088 0.058 0.00 2619.
2.10 2.10 4384. 0.101 0.061 U.UU
2.20 2.20 4663. 0.107 0.063 0.00 2823.
2.30 2.30 4949. 0.114 0.064 0.00 2893.
2.40 2.40 5241. 0.120 0.066 0.00 2963,
2.70
2.70
6162.
0.141
0.070
0.00
3178,
2.80
2.80
6464,
0.149
0.071
0.00
3251.
2.90
2.90
6813.
0.156
D.072
0.00
3325.
3.10
3.10
7493.
0.172
0.075
O.D0
3975.
3.12
3.12
'7562.
0.174
0.075
0.00
3491.
3.14
3.14
7632.
0.175
0.078
0.00
3506.
3.16
3.16
7703.
0.177
C.061
0.00
3521,
3.17
3.17
7738.
0.178
0.086
0.00
3529.
3.19
3.19
7809.
0.179
0.092
0.00
3544.
3.21
3.21
7880.
0.181
0.100
0.00
3559.
3.23
3.23
7951.
0.183
0.108
0.00
3574.
3.25
3.25
8023.
0.184
0.110
0.00
3590.
3.27
3.27
8095.
0.186
0.113
C.00
3605.
3.37
3.37
8459
0.194
0.123
0.00
3682.
3.47
3.47
8831.
0.203
0.132
0.00
3760.
3.57
3.57
9211_
0.211
0.1.40
0.00
3639.
3.67
3.67
9599.
0.220
0.147
0.00
3919.
3.77
3.77
9995.
0.229
0.154
0.00
3999,
3.67
3.67
10399.
y.1 0.239
0.160
0
0.00
4080.
3.97
3.97
10811.E
0.248
0.166
0.00
4161.
4.07
4.07
11231.
0.258
0.172
0.00
4244,
4.17
4.17
11660,
0.268
0.177
0.00
4327•
4.27
4.27
12096.
0.278
0,183
0.00
4411.
4.37
4.37
12542.
0.288
0.188
0.00
4495.
4.47
4.47
12995.
0.298
0.192
0.00
4580•
Hyd
Inflow
Outflow
0.312
0.507
0.00
4692y ADD- Yrz
4.70
4.70
14072.
0.323
1.9?O
0.00
4779.
4.80
4.80
14554.
0.334
1.610
0.00
4867.
4.90
4.90
15045.
0.345
2.600
0.00
4955.
5.00
5.00
15545.
0.357
2.890
0.00
5044.
5.10
5.10
16054.
0.369
3.150
0.00
5134.
5.20
5.20
16572.
0.380
3.390
0.00
5224.
5.30
5.30
17099.
0.393
3.610
0.00
5315.
5.40
5.40
17635.
0.405
3.820
0.00
5407.
5.50
5.50
18180.
0.417
4.020
0.00
5500.
5.60
5.60
18735.
0.430
4.210
0.00
5593.
5.70
5.70
19299.
0.443
4.390
0.00
5687.
5.80
5.80
19872.
0.456
4.560
0.00
5782.
5.90
5.90
20455.
0.470
4.720
0.00
5878.
6.00
6.00
21048.
0.483
4.890
0.00
5974.
6.10
6.10
21650.
0.497
5.040
0.00
6071.
6.20
6.20
22262.
0.511
5.190
0.00
6169.
6.30
6.30
22884.
0.525
5.340
0.00
6267.
6.40
6.40
23516.
0.540
5.460
0.00
6366.
6.50
6.50
24157.
0.555
5.620
0.00
6466,
Hyd
Inflow
Outflow
Peak
Storage
Target
calc
Stage
Elev
(Cu -Ft) (Ac
-Ft)
1
0.69
0.39
0.35
4.55
4.55
13368.
0.307
2
0.63
*+*****
0.24
4.52
4.52
13204.
0.303
3
0.61
*******
0.19
4.39
4.39
12623.
0.290
4
0.43
*******
0.18
4.19
4.19
11737,
0.269
5
0.40
*******
0.31
4.54
4.54
13304,
0.305
6
0.36
*******
0.14
3.56
3.58
9269.
0.213
7
0.44
*******
0.07
2.96
2.96
7004.
0.161
B
0.49
*******
0.07
2.53
2.53
5648.
0.130
----------------------------------
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series File:rdout
Inflow/Outflow Analysis
Peak Inflow Discharge: 0.693 CFS at 6:00 on )an 9 in 1990
Peak Outflow Discharge: 0.352 CFS at 10:00 on „an 9 in 1990
peak Reservoir Stage: 4.55 Ft
Peak Reservoir Elev: 4.55 Ft
Peak Reservoir Storage: 13368. Cu --Ft
0.307 Ac -Ft
Flow Frequency Analysis
Time Series File:rdout.tsf
Project Location:5ea-Tac
---Annual Peak Flow Rates ---
Flow Rate Rank Time of Peak
LogPearson III Coefficients
Mean= -1.015 StdDev= 0.219
Skew- 1.010
------Flow Frequency Analysis-------
- - Peaks - - Rank Return Prob
oVEYt, r. 0V/
{CFS}
(CFS;
(ft)
Period
O.D70
33
2/17/49
2:00
0.352
4.55
1
89.50
0.989
0.119
17
3/04/50
3:00
0.317
4.54
2
32.13
0.969
D.309
3
2/09/51
16:00
0.309
4.54
3
19.58
0.949
0.064
43
1/30/52
13:00
0.242
4.52
4
14.08
0.929
0.064
44
9/30/53
17:00
0.189
4.39
5
10.99
0.909
0.060
22
1/06/54
8:00
0.189
4.39
6
9.01
0.889
0.141
12
2/07/55
23:00
0.187
4.35
7
7.64
0.869
0.133
13
12/21/55
16:00
0.178
4.19
8
6.63
0.849
0.075
24
12/09/56
20:00
0.165
3.95
9
5.86
0.829
0.068
21
1/17/56
7:00
0.158
3.83
10
5.24
0.809
0.070
34
1/24/59
10:00
0.153
3.76
11
4.75
0.789
0.189
5
11/21/59
2:00
0.141
3.56
12
4.34
0.769
0.073
27
11/20/60
17:00
0.133
3.48
13
3.99
0.749
0.060
46
1/03/62
7:00
0.132
3.47
14
3.70
0.729
0.075
25
11/26/62
10:00
0.128
3.43
15
3.44
0.709
0.073
28
1/01/64
22:00
0.123
3.37
16
3.22
0.690
0.075
23
12/01/64
8:00
0.119
3.33
17
3.03
0.670
0.067
40
12/28/65
17:00
0.115
3.29
18
2.85
0.650
0.123
16
1/19/67
19:00
0.099
3.21
19
2.70
0.630
0.067
38
2/19/68
6:00
0.099
3.21
20
2.56
0.610
0.071
32
12/03/68
23:00
0.088
3.18
21
2.44
0.590
0.072
30
1/14/70
14:00
0.080
3.15
22
2.32
0.570
0.099
20
12/07/70
4:00
0.075
3.11
23
2.22
0.550
0.165
9
2/28/72
7:00
0.075
3.11
24
2.13
0.530
0.068
37
12/26/72
7:00
0.075
3.10
25
2.04
0.510
0.073
26
1/16/74
18:00
0.073
2.99
26
1.96
0.490
0.128
15
12/27/74
5:00
0.073
2.99
27
1.89
0.470
0.099
19
12/03/75
23:00
0.073
2.98
28
1.82
0.450
0.054
49
8/24/77
0:00
0.073
2.96
29
1.75
0.430
0.073
29
9/23/78
12:00
0.072
2.86
30
1.70
0.410
0.059
47
11/19/78
8:00
0.071
2.82
31
1.64
0.390
0.158
10
12/15/79.
9:00
0.071
2.81
32
1.59
0.370
0.066
42
12/26/80
6:00
0.070
2.74
33
1.54
0.350
0.169
6
10/06/81
17:00
0.070
2.71
34
1.49
0.330
0.115
18
1/05/83
14:00
0.070
2.69
35
1.45
0.310
0.063
45
1/24184
13:00
0.068
2.57
36
1.41
0.291
0.067
39
6/07/85
8:00
0.068
2.57
37
1.37
0.271
O.i78
8
!/18/86
22:00
0.067
2.53
38
1.33
0.251
0.167
7
11/24/86
7:00
0.067
2.48
39
1.30
0.231
0.066
41
1/14188
20:00
0.067
2.46
40
1.27
0.211
0.055
48
11/05/86
19:00
0.066
2.42
41
1.24
0.191
0.352
1
1/09/90
10:00
0.066
2.39
42
1.21
0.171
0.242
4
4/05/91
3:00
0.064
2.28
43
1.18
0.151
0.071
31
1/29/92
12:00
0.054
2.26
44
1.15
0.131
0.070
35
3/23/93
6:00
0.063
2.22
45
1.12
0.111
0.050
50
12/01/93
16:00
0.060
2.02
46
1.10
0.091
0.132
14
2/19/95
21:00
0.059
1.96
47
1.08
0.071
0.317
2
2/09/96
2:00
0.055
1.70
48
1.05
0.051
0.153
11
1/02/97
12:00
0.054
1.63
49
1.03
0.031
0.068
36
10/30/97
10:00
0.050
1.40
50
1.01
0.011
Computed
Peaks
0.444
4.58
100.00
0.990
Computed
Peaks
0.348
4.55
50.00
0.980
Computed
Peaks
0.271
4.52
25.00
0.960
Computed
Peaks
0.190
4.41
10.00
0.900
Computed
Peaks
0.176
4.15
8.00
0.875
Computed
Peaks
0.141
3.59
5.00
0.800
Computed
Peaks
0.089
3.18
2.00
0.500
Computed
Peaks
0.065
2.36
1.30
0.231
Flow Duration
from Time
Series File:rdout.tsf
Cutoff
Count
Frequency CDF
Exceedence_Probability
CFS
%
%
%
0.005
324991
74.199
74.199
25.801
0.258E+OC
0.015
40459
9.237
83.436
16.564
0.166E+00
0.025
27211
6.213
89.649
10.351
0.104E+00
0.035
17696
4.040
93.669
6.311
0.631E-01
0.045
11959
2.730
96.419
3.561
0.358E-01
0.054
7806
1.783
98.202
1.798
0.180E-01
0.064
4229
0.966
99.167
0.833
0.833E-02
0.074
2536
0.579
99.746
0.254
0.254E-02
O.OB4 313 0.073 99.B19 0.181 0.181E-02
0.094 86 0.020 99.839 0.161 0.161E-02
0.104 45 0.010 99.849 0.151 0.151E-02
0.114 110 0.025 99.874 0.126 0.126E-02
0.124 125 D.029 99.903 0.097 0.975E-03
0.134 81 0.018 99.921 0.079 0.790E-03
0.144 77 0.016 99.939 0.061 0.614E-03
0.153 64 0.015 99.953 0.047 0.468E-03
0.163 53 0.012 99.965 0.035 0.347E-03
0.173 40 0.009 99.974 0.026 0.256E-03
0.183 46 0.011 99.985 0.015 0.151E-03
0.193 49 0.011 99.996 0.004 0.388E-04
0.203 5 0.001 99.997 0.003 0.274E-04
0.213 0 0.000 99.997 0.003 0.274E-04
0.223 1 0.000 99.997 0.003 0,251E-04
0.233 1 0.000 99.998 0.002 0.228E-04
0.243 2 0.000 99.998 0.002 0.183E-04
0.252 1 0.000 99.998 0.002 0.160F-04
0.262 1 0.000 99.999 0.001 0.137E-04
0.272 1 0.000 99.999 0.001 0.114E-04
0.282 0 0.000 99.999 0.001 0.114E-04
0.292 1 0.000 99.999 Q.001 0.913E-05
0.302 1 0.000 99.999 0.001 0.685E-05
0.312 1 0.000 100.000 0.000 0.457E-05
0.322 1 0.000 100.000 Q.000 0.22BE-05
0.332 0 0.000 100.000 0.000 0.228E-05
0.341 0 0.000 100.000 0.000 0.228E-05
0.351 0 0.000 100.000 0.000 0.22BE-05
----------------------------------
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series Eile:rdout
Tnflow/Outflow Analysis
Peak Inflow Discharge: 0.693 CFS at 6:00 on Jan 9 in 1990
Peak Outflow Discharge: 0.352 CFS at 10:00 on Jan 9 in 1990
Peak Reservoir Stage: 4.55 Ft
Peak Reservoir Elev: 4.55 Ft
Peak Reservoir Storage: 13368, Cu -Ft
0.307 Ac-Ft
Duration Comparison Anaylsis
Base File: exist.tsf
New File: rdout.tsf
Cutoff Units: Discharge in CFS
-----Fraction of Time--------------Check of Tolerance-------
Cutoff Base New %Change Probability Base New %Change
0.074 I 0.42E-02 0.28E-02 -33.9 i 0.42E-02 0.074 0.071 -3.6
0.095 I 0.21E-02 0.16E-02 -21.6 1 0.21E-02 0.095 0.076 -19.2
0.116 I 0.11E-02 0.12E-02 8.4 € 0.11E-02 0,116 0.119 2.8
0.137 I 0.57E-03 0.75E-03 32.3 1 0.57E-03 0.137 0.146 7.0
0.158 I 0.33E-03 0.40E-03 22.9 1 0.33E-03 0.158 0.166 5.2
0.179 I 0.18E-03 0.18E-03 2.5 1 0.16E-03 0.179 0.179 0.4
0.200 I 0.11E-03 0.27E-04 -73.9 1 0.11E-03 0.200 0.187 -6.4
0.221 I 0.53E-04 0.27F-04 -47.8 1 0.53E-04 0.221 0.191 -13.3
0.242 1 0.27E-04 0.16E-04 -33.3 0.27E-04 0.242 0.221 -8.7
0.263 I 0.21E-04 0.14E-04 -33.3 I 0.21E-04 0.263 0.241 -8.3
0.284 I 0.14E-04 0.91E-05 -33.3 1 0.14E-04 0.284 0.266 -6.2
0.305 I 0.14E-04 0.68E-05 -50.0 I 0.14E-04 0.305 0.266 -12.7
0.326 1 0.68E-05 0.23E-05 -66.7 I 0.68E-05 0.326 0.306 -5.4
0.347 1 0.23E-05 0.23E-05 0.0 1 0.23E-05 0.347 0.352 1.3
Maximum positive excursion = 0.010 Cfs [ 7.7%)
occurring at 0.133 cfs on the Base Data:exist.tsf
and at 0.143 c£s on the New Data:rdout.ts£
Maximum negative excursion = 0.018 cfs (-19.4%)
occurring at 0.094 cfs on the Base Data:exist.tsf
and at 0.076 cfs on the New Data:rdout.tsf
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00-
Riser Overflow and Secondary Inlet "Jailhouse Window"
(iteratively sizes the flow control riser and a "jailhouse window" secondary
inlet using the sharp crested weir eqn.)
Project: Fleuve des Voiles
Date: 7/7/2008
By: LT
Rectangular, Sharp Crested Weir
Q=C(L-0.2H)H"312
C = 3.27 + 0.40HIP
Q(100) = 3.91 cfs
H
P
L
C
Q
0.46
4.5
3.9
3.3
3.96
15" riser
0.46
4.5
4.0
3.3
4.04
Jailhouse Window
See Erosion Control Calculations for Emergency Overflow Spillway Sizing
Drainage Calcs FV.xls Jailhouse Window
Printed: 7/812008
APPENDIX C-2
TREATMENT FACILITIES DESIGN
Treatment Pond Sizing Routine
Project: Fleuve des Voiles & Cogger Plats
Treatment Pond
Date: 6/12/2008
Blue represents manual entry fields
Red represents calculated fields
Step 1: Wetpool volume factor (f)
...either 3 or 4.5
f= 3
Step 2: Mean annual rainfall (R)
...from Fig. 6.4.1.A, pg 6-69
R = 0,47 in
Step 3: Runoff (Vr)
... Vr-(0.9Ai+0.25Atg+0.10Atf+0.01 Ao)xR/12
Ai = 219,216 sf
Atg = 99,426 sf
Atf = 0 sf
Ao = 0 sf
Vr = 8,701 cf
Step 4: Wetpool volume (Vb)
...Vb=fVr
Vb = 26,103 cf
Step 5: Wetpool dimensions
...Vb=h(A1+A2)/2 Solve by trial & error
Al = 8,056 sf
L = 52 ft
3L = 155 ft
h= 4 f
S= 2 f
A2 = 4,996 sf
*Vb = 26,103 cf
If Vb calculated in Step 5 < Vb from Step 4, then increase h
Cell 1 must contain 25% - 35% of total Wetpool volume
Cell 1 required volume between 6,526 and
9,136 cf
Cell (50x50) Cell
(50x138)
Al = 2,773 sf Al =
6,880 sf
h= 4 f h=
3 f
S= 2 f S=
2 f
A2 = 1,344 sf A2 =
5,033 sf
V = 8,234 cf V =
17,870 cf "Vb = 26,104 cf
Drainage Calcs FVA& (Treatment Pond j
6!12!2008
KCRTS Program...File Directory:
C:\KC SWDM\KC DATA\
[C] CREATE a new Time Series
ST
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.34
0.00
devl5.tsf
T
1.00000
DEVIS.exc
0.000000 Till Forest
0.000000 Till Pasture
0.000000 Till Grass
0.000000 Outwash Forest
0.000000 Outwash Pasture
0.000000 Outwash Crass
0.000000 Wetland
0.000000 Impervious
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
devl5.tsf
devl5.pks
[R] RETURN to Previous Menu
[X] exit KCRTS Program
Page 1
i 2q 4, AvF, SF,
C KM ID4.1�- F i L-Tez
Flaw Frequency Analysis LogPearson III Coefficients agii, ?yp�S AfCa
Time Series File:devl5rd.tsf Mean= -0.757 stdoev= 0.143
Project Location:5ea-Tac Skew= 1.147 dnjeIOpeat
---Annual
Flow Rate
(cFS)
0.219
0.290
0.159
0.165
0.128
0.135
0.130
0.196
0.156
0.146
0.205
0.192
0.156
0.157
0.134
0.117
0.142
0.112
0.174
0.340
0.160
0.102
0.115
0.222
0.151
0.162
0.203
0.122
0.127
0.218
0.303
0.180
0.211
0.365
0.170
0.129
0.125
0.180
0.219
0.186
0.173
0.200
0.156
0.126
0.150
0.165
0.192
0.205
0.544
0.289
Peak Flow Rates ---
Rank Time of Peak
Computed Peaks
Compute d Peaks
Computed Peaks
computed Peaks
computed Peaks
Computed Peaks
computed Peaks
computed Peaks
2/16/49 17:45
8/15/50 6:45
8/27/51 18:00
10/17/51 7:15
9/30/53 3:00
12/19/53 17:30
7/30/55 21:15
10/04/55 10:00
10/19/56 23:45
1/16/58 10:00
10/18/58 19:45
10/10/59 22:00
2/14/61 20:15
8/04/62 13:15
12/01/62 20:15
6/05/64 15:00
4/20/65 19:30
9/17/66 17:45
11/13/66 17:45
8/24/68 15:00
10/20/68 12:00
5/29/70 7:45
12/06/70 7:00
12/08/71 17:15
4/18/73 9:30
11/28/73 8:00
8/17/75 23:00
10/29/75 7:00
8/23/77 14:30
9/17/78 1:00
9/08/79 13:45
12/14/79 20:00
9/21/81 8:00
10/05/81 22:15
10/28/82 16:00
1/02/84 23:30
6/06/85 19:15
10/27/85 10:45
10/25/86 22:45
5/13/88 17:30
8/21/89 16:00
11/03/89 23:45
4/03/91 20:15
1/27/92 15:00
6/09/93 12:15
11/17/93 16:45
6/05/95 17:00
7/19/96 19:30
12/29/96 11:45
10/04/97 14:15
-----Flow
Frequency
Analysis-------
- - Peaks
- - Rank
Return
Proh
(CFS)
Period
0.544
1
89.50
0.989
0.365
2
32.13
0.969
0.340
3
19.58
0.949
0.303
4
14.08
0.929
0.290
5
10.99
0.909
0.289
6
9.01
0.889
0.222
7
7.64
0.869
0.219
8
6.63
0.849
0.219
9
5.86
0.829
0.218
10
5.24
0.809
0.211
11
4.75
0.789
0.205
12
4.34
0.769
0.205
13
3.99
0.749
0.203
14
3.70
0.729
0.200
15
3.44
0.709
0.196
16
3.22
0.690
0.192
17
3.03
0.670
0.192
18
2.85
0.650
0.186
19
2.70
0.630
0.180
20
2.56
0.610
0.180
21
2.44
0.590
0.174
22
2.32
0.570
0.173
23
2.22
0.550
0.170
24
2.13
0.530
0.165
25
2.04
0.510
0.165
26
1.96
0.490
0.162
27
1.89
0.470
0.160
28
1.82
0.450
0.159
29
1.75
0.430
0.157
30
1.70
0.410
0.156
31
1.64
0.390
0.156
32
1.59
0.370
0.156
33
1.54
0.350
0.151
34
1.49
0.330
0.150
35
1.45
0.310
0.146
36
1.41
0.291
0.142
37
1.37
0.271
0.135
38
1.33
0.251
0.134
39
1.30
0.231
0.130
40
1.27
0.211
0.129
41
1.24
0.191
0.128
42
1.21
0.171
0.127
43
1.18
0.151
0.126
44
1.15
0.131
0.125
45
1.12
0.111
0.122
46
1.10
0.091
0.117
47
1.08
0.071
0.115
48
1.05
0.051
0.112
49
1.03
0.031
0.102
50
1.01
0.011
0.490
100.00
0.990
0.414
50.00
0.980
0.347
25.00
0.960
0.273
10.00
0.900
0.259
8.00
0.875
0.223
5.00
0.800
0.165
2.00
0.500----
0.135
1.30
0.231
15 i x --i ,ry�c _.-'Acres
�, � . Vi/4 des � ►� .
e s,r -6o arc, Poe 4,�e eA r -el road -;o s F I i 4 i n hal
r n, 0 I
KCRTS Program... File DireCtory:
C:\KC_SWDM\KC_DATA\
[C] CREATE a new Time Series
ST
0.00 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0.00 0.00 0.000000 Till Grass
0.00 0.00 0.000000 outwash Forest
0.00 0.00 0.000000 outwash Pasture
0,00 0.00 0.000000 outwash Grass
0.00 0.00 0.000000 wetland
0.34 0.00 0.000000 Impervious
devl5rd.tsf
F
1.00000
F
[T Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
devl5rd.tsf
devl5rd.pks
(RRETURN to Previous Menu
[XI eXit KCRTS Program
i N PJ T 'I)Pc t o
APPENDIX C-3
EROSION CONTROL FACILITIES DESIGN
EC Pond Calculations
Project: Fleuve des Voiles & Cogger Plats
Date: 4 -.Jun -08
Q2 = 2.48 cfs (from KCRTS flow frequency analysis)
Q,o = 4.09 cfs (from KCRTS flow frequency analysis)
Q,00 = 8.42 cfs (from KCRTS flow frequency analysis)
Determine Pond Geometry
SA = 2080*Q2
SAW 5158 sf
Size Discharge Mechanisms
- Principal Spillway
Must be at least 15" diameter to pass 010 @ 1' head(from KCSWOM Fig 5.3.4.H)
=> If permanent control structure is used for EC, then riser must be increased to 15"
- Emergency Overflow Spillway - iterative solution below
L=((Q 10013.21 *H"(312))-(2.4*H)
H
L
0.2
28.8
0.3
15.2
0.4
9.4
0.5
6.2
0.6
4.2
0.7
2.8
0.8
1.7
To maintain 6" freeboard (6" depth), 7' length is req'd
- Dewatering Orifice
Ao=4.81 *(10-6)*Ao*sgrt(h)
AO= 0.02 sf
D=13.54*sgrt(AO)
D = 1.79 in
Drainage Cales FV.xls EC Calcs
7/7/2008
SECTION 5.3 DETENTION FACILITIES
Riser Overflow
The nomograph in Figure 5.3AH may be used to determine the head (in feet) above a riser of given
diameter and for a given flow (usually the 100 -year peak flow for developed conditions).
100
si
Qlo ` Lj,(Y cP
FIGURE 5.3A.H RISER INFLOW CURVES ,
HEAD IN FEET (measured from crest of riser)
Qweir=9.739 DH"'
Qorifice-
-3.782 D2H112
Q in efs, D and H in feet
Slope change occurs at weir -orifice transition
1/2412005 2005 Surface Water Design Manual
5.48
KCRTS Program...File
Directory:
C:\KC_SWDM\KC_DATA\
[C] CREATE a
new Time
series
ST
0.00
0.00
0.000000
Till Forest
0.00
0.00
0.000000
Till Pasture
2.13
0.00
0.000000
Till Grass
0.00
0.00
0.000000
Outwash Forest
0.00
0.00
0.000000
Outwash Pasture
0.00
0.00
0.000000
Outwash Grass
0.00
0.00
0.000000
wetland
4.87
0.00
0.000000
Impervious
devl5.tsf
F
1.00000
F
[T] Enter the
Analysis
TOOLS Module
[P] Compute PEAKS
and
Flaw Frequencies
devl5.tsf
devl5.pks
[R] RETURN to
Previous
Menu
[X] eXit KCRTS
Program
ri re- rieUV(f 4
min
r C--( 1-
Flaw Frequency Analysis LagPearson III Coefficients
Time Series File:devl5.tsf Mean= 0.427 StdDev= 0.155
Project Location:sea-'Tac Skew= 1.294
---Annual
Flow Rate
(CFS)
3.56
4.66
2.28
2.53
1.89
2.09
1.86
2.80
2.42
2.31
3.06
3.00
2.49
2.25
2.07
1.70
2.31
1.61
2.74
5.49
2.47
1.48
1.78
3.65
2.21
2.54
2.90
1.89
1.83
3.20
4.42
2.93
3.03
6.05
2.60
1.98
1.86
2.74
3.24
2.67
2.49
3.41
2.49
1.95
2.36
2.37
2.78
2.95
9.66
4.86
Peak Flow Rates--- -----Flow Frequency
Rank Time of Peak - - Peaks - - Rank
8 2/16/49
5 3/03/50
35 8/27/51
25 10/17/51
42 9/30/53
38 12/19/53
44 7/30/55
18 10/04/55
30 12/09/56
33 1/16/58
12 10/18/58
14 10/10/59
26 2/14/61
36 8/04/62
39 12/01/62
48 6/05/64
34 4/20/65
49 1/05/66
21 11/13/66
3 8/24/68
29 10/20/68
50 1/13/70
47 12/06/70
7 12/08/71
37 4/18/73
24 11/28/73
17 8/17/75
43 10/29/75
46 8/23/77
11 9/17/78
6 9/08/79
16 12/14/79
13 9/21/81
2 10/05/81
23 10/28/82
40 1/02/84
45 6/06/85
20 10/27/85
10 10/25/86
22 5/13/88
28 8/21/89
9 1/09/90
27 4/03/91
41 1/27/92
32 6/09/93
31 11/17/93
19 6/05/95
15 7/19/96
1 12/29/96
4 10/04/97
Computed Peaks
computed Peaks
Computed Peaks
computed Peaks
Computed Peaks
Computed Peaks
Computed Peaks
computed Peaks
Analysis -------
Return Prob
Period
Tj
Jevef0CC4 5�1+C-5
l5-MIn -krv-t c�S
1
2
(CFS)
17:45
9.66
15:00
6.05
18:00
5.49
7:15
4.86
3:00
4.66
17:30
4.42
21:15
3.65
10:00
3.56
12:45
3.41
10:00
3.24
19:45
3.20
22:00
3.06
20:15
3.03
13:15
3.00
20:15
2.95
15:00
2.93
19:30
2.90
15:00
2.80
17:45
2.78
15:D0
2.74
12:00
2.74
20:45
2.67
7:00
2.60
17:15
2.54
9:30
2.53
8:00
2.49
23:00
2.49
7:00
2.49
14:30
2.47
1:00
2.42
13:45
2.37
20:00
2,36
8:00
2.31
22:15
2.31
16.00
2.28
23:30
2.25
21:15
2.21
10:45
2.09
22:45
2.07
17:30
1.98
16:00
1.95
5:30
1.89
20:15
1.89
15:00
1.86
12:1 5
1.86
16:45
1.83
17:00
1.78
19:30
1.70
11:45
1.61
14:15
1.48
0.470
8.42
28
6.94
0.450
5.68
29
4.32
4.09
0.430
3.46
30
2.48
0.410
2.03
Analysis -------
Return Prob
Period
Tj
Jevef0CC4 5�1+C-5
l5-MIn -krv-t c�S
1
2
89.50
32.13
0.989
0.969
4 n
3
19.58
0.949
4
14.08
0.929
5
10.99
0.909
6
9.01
0.889
7
7.64
0.869
8
6.63
0.849
9
5.86
0.829
10
5.24
0.809
11
4.75
0.789
12
4.34
0.769
13
3.99
0.749
14
3.70
0.729
15
3.44
0.709
16
3.22
0.690
17
3.03
0.670
18
2.85
0.650
19
2.70
0.630
20
2.56
0.610
21
2.44
0.590
22
2.32
0.570
23
2.22
0.550
24
2.13
0.530
25
2.04
0,510
26
1.96
0.490
27
1.89
0.470
28
1.82
0.450
29
1.75
0.430
30
1.70
0.410
31
1.64
0.390
32
1.59
0.370
33
1.54
0.350
34
1.49
0.330
35
1.45
0.310
36
1.41
0.291
37
1.37
0.271
38
1.33
0.251
39
1.30
0.231
40
1.27
0.211
41
1.24
0.191
42
1.21
0.171
43
1.18
0.151
44
1.15
0.131
45
1.12
0.111
46
1.10
0.091
47
1.08
0.071
48
1.05
0.051
49
1.03
0.031
50
1.01
0.011
100.00
0.990 4�
50.00
0.980
25.00
0.960
10.00
0.9o04 -
.9004--'"8.00
B. OG
0.875
5.00
0.800
2.00
0.500^
1.30
0.231
9EY-.? � C(
4'ccs,
Flow Frequencyy analysis
LogPearson III Coefficients
Time Series
File:escchnl5.tsf
Mean=
-0.142 Stdbev=
0.156
Project
Location:5ea-Tac
Skew= 1.302
----annual
Peak
Flow Rates---
-----Flow
Frequency
analysis -------
Flow Rate
Rank
Time of
Peak
_ - Peaks
- - stank
Return
Prob
(cFs)
(CFS)
Period
0.964
8
2/16/49
17:45
2.62
1
89.50
0.989
1..26
5
3/03/50
15:00
1.64
2
32.13
0.969
0.614
35
8/27/51
18:00
1.48
3
19.58
0.949
0.684
25
10/17/51
7:15
1.32
4
14.08
0.929
0.509
43
9/30/53
3:00
1.26
5
10.99
0.909
0.564
38
12/19/53
17:30
1.19
6
9.01
0.889
0.501.
44
7/30/55
21:15
0.988
7
7.64
0.869
0.754
18
10/04/55
10:00
0.964
8
6.63
0.849
0.657
30
12/09/56
12:45
0.926
9
5.86
0.829
0.625
33
1/16/58
10:00
0.873
10
5.24
0.809
0.826
12
10/18/58
19:45
0.862
11
4.75
0.789
0.810
14
10/10/59
22:00
0.826
12
4.34
0.769
0.674
26
2/14/61
20:15
0.814
13
3.99
0.749
0.604
36
8/04/62
13:15
0.810
14
3.70
0.729
0.560
39
12/01/62
20:15
0.793
15
3.44
0.709
0.458
48
6/05/64
15:00
0.792
16
3.22
0.690
0.625
34
4/20/65
19:30
0.781
17
3.03
0.670
0.436
49
1/05/66
15:OD
0.754
18
2.85
0.650
0.740
20
11/13/66
17:45
0.748
19
2.70
0.630
1.48
3
8/24/68
15:00
0.740
20
2.56
0.610
0.668
29
10/20/68
12:00
0.739
21
2.44
0.590
0.401
50
1/13/70
20:45
0.718
22
2.32
0.570
0.482
47
12/06/70
7:00
0.701
23
2.22
0.550
0.988
7
12/08/71
17:15
0.688
24
2.13
0.530
0.596
37
4/18/73
9:30
0.684
25
2.04
0.510
0.688
24
11/28/73
8:00
0.674
26
1.96
0.490
0.781
17
8/17/75
23:00
0.673
27
1.89
0.470
0.510
42
10/29/75
7:00
0.668
28
1.82
0.450
0.491
46
8/23/77
14:30
0.668
29
1.75
0.430
0.862
11
9/17/78
1:00
0.657
30
1.70
0.410
1.19
6
9/08/79
13:45
0.637
31
1.64
0.390
0.792
16
12/14/79
20:00
0.636
32
1.59
0.370
0.814
13
9/21/81
8:00
0.625
33
1.54
0.350
1.64
2
10/05/81
22:15
0.625
34
1.49
0.330
0.701
23
10/28/82
16:00
0.614
35
1.45
0.310
0.534
40
1/02/84
23:30
0.604
36
1.41
0.291
0.501
45
6/06/85
21:15
0.596
37
1.37
0.271
0.739
21
10/27/85
10:45
0.564
38
1.33
0.251
0.873
10
10/25/86
22:45
0.560
39
1.30
0.231
0.718
22
5/13/88
17:30
0.534
40
1.27
0.211
0.668
28
8/21/89
16:00
0.528
41
1.24
0.191
0.926
9
1/09/90
5:30
0.510
42
1.21
0.171
0.673
27
4/03/91
20:15
D.509
43
1.18
0.151
0.528
41
1/27/92
15:00
0.501
44
1.15
0.131
0.637
31
6/09/93
12:15
0.501
45
1.12
0.111
0.636
32
11/17/93
16:45
0.491
46
1.10
0.091
0.748
19
6/05/95
17:00
0.482
47
1.08
0.071
0.793
15
7/19/96
19:30
0.458
48
1.05
0.051
2.62
1
12/29/96
11:45
0.436
49
1.03
0.031
1.32
4
10/04/97
14:15
0.401
50
1.01
0.011
Computed
Peaks
2.28
100.00
0.990
computed
Peaks
1.88
50.00
0.980
computed
Peaks
1.54
25.00
0.960
Computed
Peaks
1.17
10.00
0.900
computed
Peaks
1.10
8.00
0.875
computed
Peaks
0.934
5.00
MOO
Computed
Peaks
0.669
2.00
0.500
Computed
Peaks
0.547
1.30
0.231
0.00 0.00 0.000000 outwash Grass
0.00 0.00 0.000000 wetland
1.31 0.00 0.000000 Impervious
escchnl5.tsf
F
1.00000
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
escchnl5.tsf
escchnl5.pks
[R] RETURN to Previous Menu
[X] eXit KCRTS Program
L-Ock- L@ uVOC S� Ca-, e ,G en c- f. G►
k6 1
E. F6 S 1 UW1 I ' 9 1 `7 , -j 1% k LJ. a,"
rh
0 T C✓1 F
! �wd
Li./ r PD"t
KCRTS Program...File Directory:
C:\KC_
pY
P
[C] CREATE a new
Time Series
5T 0.00
0.00
0.000000
Till Forests
0.00
0.00
0.000000
Till Pasture
0.50
0.00
0.00
0.00
0.000000
0.000000
Till Grass
outwash Forest
1�j— PA {V)
41N.Y
0.00
0.00
0.000000
outwash Pasture
a
0.00 0.00 0.000000 outwash Grass
0.00 0.00 0.000000 wetland
1.31 0.00 0.000000 Impervious
escchnl5.tsf
F
1.00000
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
escchnl5.tsf
escchnl5.pks
[R] RETURN to Previous Menu
[X] eXit KCRTS Program
L-Ock- L@ uVOC S� Ca-, e ,G en c- f. G►
k6 1
E. F6 S 1 UW1 I ' 9 1 `7 , -j 1% k LJ. a,"
rh
0 T C✓1 F
! �wd
1f1.
i A?
C�
FlFl
�c�c.�f �`�.�' � 1 �.,��.�.:tt S 'ALT ✓
�Atetr " �w S lIS
BACKWATER COMPUTER PRCGRAM FOR OPEN CHANNELS
Channel Data Filename:escswale.bwc
Tailwater Elevation:418.2 feet
Discharge Range:0.5 to 2.5 Step of 0.5 [cfs]
STATION 1000.00: INVERT= 418.00 FT EC=1.15 Q--RATIO=0.00
CROSS-SECTION DATA:
DIST/STAGE IS MEASURED FROM INVERT; N -FAC IS MEASURED BETWEEN STAGES
LEFT(FT)
STAGE(FT) N -FACTOR *
RIGHT(FT)
STAGE(FT)
N -FACTOR
1.00
1.00
0.00
0.030 *
1.00
0.00
0.030
5.00
1.00
0.030 *
5.00
1.00
0.030
0.030
Q(CFS)
Y1(FT)
WS ELEV. * YC --IN
YN-IN Q -TW
TW -HT 14-Y1
A -Y1
WP -Y1
V-YI
WP -Y1
V -Y1
0.50
0.50
0.20
418.20 * 0.13
0.13 0.00
0.20 0.030
0.56
3.65
0.89
1.00
0.20
418.20 0.19
0.18 0.00
0.20 0.030
0.56
3.65
1.79
1.50
0.24
418.24 0.24
0.23 0.00
0.20 0.030
0.71
3.98
2.11
2.00
C.28
418.28 * 0.28
0.26 0.00
0.20 0.030
0.87
4.31
2.29
2.50
D.31
418.31 * 0.31
0.30 0.00
0.20 0.030
1.00
4.56
2.49
****REACH
NO. 1:
LENGTH= 500.00 FT
AVG.GRADE=
2.40% ****
Opened for
Writing:escswale.bwt
STATION 1500.00:
INVERT= 430.00 FT EC=1.15
Q -RATIO -0.00
CROSS-SECTION DATA:
DIST/STAGE IS MEASURED FROM INVERT; N -FAC IS MEASURED BETWEEN STAGES
LEFT (FT) STAGE(FT) N -FACTOR *
RIGHT (FT)
STAGE(FT)
N -FACTOR
1.00
0.00
0.030 *
1.00
0.00
0.030
5.00
1.00
0.030 *
5.00
1.00
0.030
Q(CFS)
Y1(FT)
WS ELEV. * YC -IN
YN-IN
YC -OT
YN-OT N -Y1
A -Y1
WP -Y1
V -Y1
0.50
0.13
430.13 0.13
D.00
0.13
0.13 0.030
0.33
3.07
1.53
1.00
0.18
430.18 * 0.19
0.00
0.19
0.18 0.030
0.49
3.48
2.04
1.50
0.23
430.23 * 0.24
0.00
0.24
0.23 0.030
0.67
3.9C
2.23
2.00
0.26
430.26 * 0.28
0.00
0.28
0.26 0.030
0.79
4.14
2.53
2.50
0.30
430.30 * 0.31
0.00
0.31
C.30 0.030
0.96
4.47
2.60
File
Opened for
Writing:escswale.bwt
Save results to HW/TW file:escswale.bwt
File Opened for Writing:escswale.RS1
Save results to Routing fi]e:escswale.RS1
i 4
s W - w o r k ,7
EG
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
File opened for Reading:escpipe.bwp
File opened for writing:escpipe.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:escpipe.bwp
surcharge condition at intermediate junctions
Tailwater Elevation:390. feet
Discharge Range:].. to 5. step of 1. [cfs]
Overflow Elevation:475. feet
weir:NONE
Upstream velocity:l. feet/sec
PIPE No. 1: 65 LF - 18"CP @ 16.92% OUTLET: 388.DO INLET: 399.00 INTYP: 5
JUNC NO. 1: OVERFLOW -EL: 400.00 BEND: 0 DEG DIA/WIDTH: 2.5 Q -RATIO: 0.33
Q(CFS)
HW(FT)
HW ELEV.
' N -FAC
DC
DN
TW
DO
DE
HWO
HWI
ieiririririeirYr&sYrtTMiriritiririrfrirititri•ridertrtrt4it**ir�rirri•*iert4rtTMlrrtirieirieiririrYr'kirYSYirFiriririrria4iritir*WrttYrai:
**ir�rir
1.00
0.38
399.38
* 0.012
0.38
0.16
2.00
2.00
0.38
*TMrtTMy`
0.38
2.00
0.61
399.61
* 0.012
0.54
0.22
2.00
2.00
0.54
*"rtrtrt
0.61
3.00
0.79
399.79
TM 0.012
0.66
0.26
2.00
2.00
0.66rtrtTM
0.52
0.79
4.00
0.96
399.96
* 0.012
0.77
0.30
2.00
2.00
0.77
***"*
0.96
5.00
1.11
400.11
* 0.01.2
0.87
0.34
2.00
2.00
0.87
0.68
1.1.1.
PIPE NO.
2: 85
LF - 1811CP
@ 18.82%
OUTLET:
399.00
INLET: 415.00 INTYP: 5
)UNC NO.
2: OVERFLOW -EL: 416.00 BEND:
0
DEG
DIA/WIDTH:
2.5
Q -RATIO:
0.50
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
DN
TW
DO
DE
Hw0
HWI
7r lr W9eW RY rtrt*t*rt*it it fr �r 44r Yr ie Pert �i<*ir a4 ie it it it it ie irrtTMrt
TMi<**ir i4*ir it*Yr Cert rthirt it tr i<tr it 9e it Vrtrtrtrthrt****i4
it*rtri
0.75
0.33
415.33
* 0.012
0.33
0.13
0.38
0.38
0.33
rtii*rt
0.29
1.50
0.48
415.48
* 0.012
0.47
0.18
0.61
0.61
0.47
0.48
2.26
0.62
415.62
* 0.012
0.57
0.22
0.79
0.79
0.57
0.62
3.01
0.73
415.73
' 0.012
0.66
0.26
0.96
0.96
0.66
0.73
3.76
0.83
415.83
' 0.012
0.75
0.29
1..11
1.11
0.75
rirt.`*
0.83
PIPE NO. 3: 115 LF - 12"CP @ 21.74% OUTLET: 415.00 INLET: 440.00 INTYP: 5
JUNC NO. 3: OVERFLOW -EL: 441.00 BEND: 0 DEG DIA/WIDTH: 2.5 Q -RATIO: 1.00
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
OC
ON
TW
DO
DE
HWO
HWI
4rrtTMir it it it ie it it ie fr it it fr Yr Vertfthtr irtr***rift it it irrt*hrtirt**dr
ie it
it it it it*Yr�ir
irlr irrt
it it it it it*ri�sY
rt+'r r.
Vii: it �r*fir fr irrt rirt;rrt
0.50
0.30
440.30
* 0.012
0.30
0.1.2
0.33
0.33
0.30
fr**
0.29
1.00
0.47
440.47
0.012
0.43
0.17
0.48
0.48
0.43
0.34
0.47
1.50
0.62
440.62
* 0.012
0.52
0.20
0.62
0.62
0.52
rt ***
0.62
2.01
0.76
440.76
0.012
0.61
0.23
0.73
0.73
0.61
0.48
0.76
2.51
0.89
440.89
0.012
0.68
0.26
0.83
0.83
0.68*riTMrt
0.53
0.89
PIPE NO. 4: 110 LF - 8"CP @ 23.64% OUTLET: 440.00 INLET: 466.00 INTYP: 5
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
DN
TW
DO
DE
HWO
HWI
*rr*�rwritrxrrinrr+rTMTM*-�,t**,t*TM,nw.�ctr�rTMsr�r+r�r�**w�sv,rTM,r*,tTMTMTM�r�rt�tr♦r�w,r,vrtsrTM�rertrrt�
svra,rw,rrrrrTMfr�rr�r**
0.25
0.24
466.24
* 0.012
0.24
0.10
0.30
0.30
0.24
0.23
0.50
0.39
466.39
" 0.012
0.34
0.13
0.47
0.47
0.34
0.39
0.75
0.53
466.53
* 0.012
0.41
0.1.6
0.62
0.62
0.41
0.53
1.00
0.68
466.68
* 0.012
0.48
0.18
0.76
0.76
0.48
"*TMir*
0.68
1.25
0.87
466.87
* 0.012
0.53
0.21
0.89
0.89
0.53
�`*rt*TM
0.87
File
opened
for writing:escpipe.bwt
Save results to HW/TW file.escpipe.bwt
EXit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 6.00
APPENDIX C4
CONVEYANCE FACILITIES DESIGN
N v T R Ln O M C) Ca N O
L() O M N R P- r 0 0
O
M
r
('7
T
NrmM Or Lo0Q
.:+
O Q r O O O O O d O O O
O O Q O O O O r 0
M
A
6
cm
Q
M
IZ
Lo M mt r% -'t O e-- O Lo
N N O t0 = 0 N v O
Q
Lo ["i 1� 6) h t* m T M u) C2
A
e
R R 0 m M tl- i+ CO 'C M N T
L!'J N O r- v , M N r
I
Q7
m
TrTOOQC7OO
D
Q% r
L}
Q N O R R M M O N It Ln Lo
3 N
N
N (D w N m M N co co m w M t()
O M Ln O M (D N v r N
V
h M
(h
N
CY
O O N O D 0 0 O O O O C7 m
O O O C' CD Q O O O r
fD
U) N
cv
47
Q O CD O m O 0 I� v r m
M 00 N O a N M r
a
Co
O7 0) R O R a) Tl- 1,-
07 m R R R
o)
o o c o 0 o d o 0 o La a
Co
F-
F-
U
>
E
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A
191st Street Conveyance calcs
6/11/08
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 6.00
File opened for Reading:191st.bwp
File Opened for writing:191st.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:191st.bwp
surcharge condition at
intermediate junctions
Tailwater Elevation:386.38
feet
Discharge
Range:0.5
to 4. Step of 0.5
[cfs]
overflow Elevation:459.49
feet
weir:NONE
Upstream
Velocity:l.
feet/sec
PIPE NO.
1: 70
LF - 12"CP
@ 6.29% OUTLET:
380.50
INLET: 384.90 INTYP: 5
JUNC NO.
1: OVERFLOW
-EL: 388.00
BEND: 20
DEG
DIA/WIDTH:
2.0
Q -RATIO:
0.00
Q(CFS)
HW(FT)
HW ELEV.
k N -FAC DC
DN
TW
DO
DE
HWO
HWI
*rr�*�**�*w*rrrrartrr**krr*rr*w**rr**rrrr*rr******mart*rtrr��***�**rr**rrrrrrrrrrrrrrrr**rrwrrrrrtrrrrrr�rtxrrrr
0.50
1.50
386.40
* 0.012 0.30
0.16
5.88
5.88
1.50
1.50
0.37
1.00
1.54
386.44
0.012 0.43
0.22
5.88
5.88
1.53
1.54
0.54
1.50
1.62
386.52
0.012 0.52
0.27
5.88
5.88
1.59
1.62
0.68
2.00
1.73
386.63
* 0.012 0.61
0.31
5.88
5.88
1.67
1.73
0.80
2.50
1.87
386.77
* 0.012 0.68
0.35
5.88
5.88
1.77
1.87
0.91
3.00
2.04
386.94
* 0.012 0.75
0.39
5.88
5.88
1.90
2.04
1.01
3.50
2.24
387.14
* 0.012 0.80
0.42
5.88
5.88
2.06
2.24
1.15
4.00
2.48
387.38
* 0.012 0.85
0.45
5.88
5.88
2.23
2.48
1.31
PIPE NO.
2: 73
LF - 12"CP
@ 1.01% OUTLET:
385.00
INLET: 385.74 INTYP: 5
JUNC NO.
2: OVERFLOW
-EL: 389.08
BEND: 90
DEG
DIA/WIDTH:
2.0
Q -RATIO:
0.01
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC DC
DN
TW
DO
DE
HWO
HWI
*�*�**�*rr*rtrrrr*rr*rr***�**rrkrr*rrrr��**�*Yr*rra*rrrrrrrr�*�*�Yrrr**rtkrtrt4�k�***rrkrrkrrrt****err*rrrt
0.50
0.70
386.44
* 0.012 0.30
0.25
1.40
1.40
0.68
0.70
0.40
1.00
0.82
386.56
* 0.012 0.43
0.35
1.44
1.44
0.75
0.82
0.60
1.50
1.00
386.74
* 0.012 0.52
0.44
1.52
1.52
0.68
1.00
0.77
2.00
1.27
387.01
* 0.012 0.61
0.51
1.63
1.63
1.09
1.27
0.95
2.50
1.62
387.36
* 0.012 0.68
0.59
1.77
1.77
1.34
1.62
1.13
3.00
2.06
387.80
* 0.012 0.75
0.66
1.94
1.94
1.64
2.06
1.32
3.50
2.57
388.31
rr 0.012 0.80
0.75
2.14
2.14
2.00
2.57
1.55
4.00
3.16
388.90
* 0.012 0.85
0.85
2.38
2.38
2.42
3.16
1.83
PIPE NO.
3: 36
LF - 12"CP
@ 9.03% OUTLET:
385.84
INLET: 389.09 INTYP: 5
JUNC NO.
3: OVERFLOW
-EL: 392.43 BEND: 12
DEG
DIA/WIDTH:
2.0
Q -RATIO:
0.02
Q(CFS)
HW(FT)
HW ELEV.
N -FAC DC
DN
TW
DO
DE
HWO
*rrY<rt**rrrt**rtrr*rt**�*�*rr*rrrr***��*krrkrrk*rt4rt******Y!Y[Ytrr*rrrr******�Ylrrkrtkrtrt**�*Wrrrt*rtki*
*HWI
0.50
0.35
389.44
* 0.012 0.30
0.15
0.60
0.60
0.30
***
0.35
0.99
0.52
389.61
* 0.012 0.42
0.20
0.72
0.72
0.42
****
0.52
1.49
0.66
389.75
* 0.012 0.52
0.25
0.90
0.90
0.52
*****
0.66
1.98
0.78
389.87
* 0.012 0.61
0.28
1.17
1.17
0.61
*****
0.78
2.48
0.89
389.98
* 0.012 0.68
0.32
1.52
1.52
0.68
*****
0.89
2.97
0.99
390.08
* 0.012 0.74
0.35
1.96
1.96
0.74
*****
0.99
3.47
1.13
390.22
0.012 0.80
0.38
2.47
2.47
0.80
*****
1.13
3.96
1.29
390.38
* 0.032 0.85
0.41
3.06
3.06
0.85
****
1.29
PIPE NO.
4: 118
LF - 12"CP
@ 7.54% OUTLET:
389.19
INLET: 398.09 INTYP: 5
JUNC NO.
4: OVERFLOW
-EL: 405.86 BEND: 5
DEG
DIA/WIDTH:
4.0
Q -RATIO:
1.64
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC DC
DN
DO
DE
HWO
HWI
*Mrrkkrr*4rtrt�*�c***Wdrt**rtrtrt**��*Ye*rrtrrtrtrt�*k**�**rtrtrts*��rrrr*rtrtrtirk****krtrrkkrtrt�**�Yt
rtk*YrTW
0.49
0.36
398.45
rr 0.012 0.29
0.15
0.25
0.25
0.29
*****
0.36
0.97
0.55
398.64
* 0.012 0.42
0.21
0.42
0.42
0.42
**Y'**
0.55
1.46
0.71
398.80
* 0.012 0.52
0.26
0.56
0.56
0.52
****
0.71
1.94
0.86
398.95
* 0.012 0.60
0.29
0.68
0.68
0.60
*****
0.86
2.43
1.01
399.10
* 0.012 0.67
0.33
0.79
0.79
0.67
rt****
1.01
2.91
1.17
399.26
* 0.012 0.74
0.36
0.89
0.89
0.74
Y`**
1.17
3.40
1.37
399.46
rr 0.012 0.79
0.39
1.03
1.03
0.79
**rt**
1.37
3.88
1.59
399.68
rr 0.012 0.84
0.42
1.19
1.19
0.84
*****
1.59
PIPE NO.
5: 38
LF - 12"CP
@ 6.34% OUTLET:
401.79
INLET: 404.20 INTYP: 5
JUNC NO.
5: OVERFLOW -EL: 407.75 BEND: 50
DEG
DIA/WIDTH:
2.0
Q -RATIO:
0.01
QCCFS)
HW(FT)
HW ELEV.
* N -FAC DC
DN
TW
DO
DE
HWO
HWI
kY(kkk�**R**�**Yrrr*krt�rt***krrrrrrkrt�k�***�***hf<rtrtk**�*�*****k*i[**#rrkkrt�*���**YC*rtrtrtrtk
0.18
0.21
404.41
* 0.012
0.18
0.10
O.DO
0.10
0.18
HWO
0.21
0.37
0.31
404.51
* 0.012
0.26
0.14
0.00
0.14
0.26
****
0.31
0.55
0.39
404.59
* 0.012
0.31
0.17
0.00
0.17
0.31
*****
0,39
0.74
0.46
404.66
* 0.012
0.36
0.19
0.00
0.19
0.36
*****
0.46
0.92
0.52
404.72
* 0.012
0.41
0.21
0.00
0.21
0.41
**wi`*
0.52
1.10
0.58
404.78
* 0.012
0.45
0.23
0.00
0.23
0.45
*****
0.58
1.29
0.64
404.84
* 0.012
0.48
0.25
0.00
0.25
0.48
*****
0.64
1.47
0.69
404.89
* 0.012
0.52
0.27
0.00
0.27
0.52
*****
0.69
PIPE NO.
6: 64
LF - 12"CP
@ 13.73%
OUTLET:
404.30
INLET: 413.09 INTYP: 5
JUNC NO.
6: OVERFLOW -EL: 416.92 BEND:
0
DEG
DIA/WIDTH:
2.0
Q -RATIO:
0.77
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
DN
TW
DO
DE
HWO
HWI
0.18
0.18
413.27
* 0.012
0.18
0.08
0.11
0.11
0.18
h****
0.17
0.36
0.27
413.36
* 0.012
0.25
0.11
0.21
0.21
0.25
*****
0.27
0.55
0.35
413.44
* 0.012
0.31
0.14
0.29
0.29
0.31
*****
0.35
0.73
0.42
413.51
* 0.012
0.36
0.16
0.36
0.36
0.36
*****
0.42
0.91
0.49
413.58
* 0.012
0.40
0.18
0.42
0.42
0.40
***i`*
0.49
1.09
0.55
413.64
* 0.012
0.44
0.19
0.48
0.48
0.44
**w**
0.55
1.27
0.61
413.70
* 0.012
0.48
0.21
0.54
0.54
0.48
**wwh
0.61
1.46
0.67
413.76
* 0.012
0.52
0.22
0.59
0.59
0.52
it*wwh
0.67
PIPE NO.
7: 73
LF - 12"CP
@ 14.93%
OUTLET:
413.19
INLET: 424.09 INTYP: 5
JUNG NO.
7: OVERFLOW -EL: 427.93 BEND:
0
DEG
DIA/WIDTH:
2.0
Q -RATIO;
0.05
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
ON
TW
DO
DE
HWO
HWI
0.10
0.14
424.23
* 0.012
0.14
0.06
0.08
0.08
0.14
h****
0.10
0.21
0.19
424.28
* 0.012
0.19
0.09
0.17
0.17
0.19
h****
0.18
0.31
0.23
424.32
* 0.012
0.23
0.10
0.25
0.25
0.23
h****
0.23
0.41
0.28
424.37
* 0.012
0.27
0.12
0.32
0.32
0.27
**^**
0.28
0.51
0.33
424.42
* 0.012
0.30
0.13
0.39
0.39
0.30
*****
0.33
0.62
0.37
424.46
* 0.012
0.33
0.14
0.45
0.45
0.33
*****
0.37
0.72
0.41
424.50
* 0.012
0.36
0.15
0.51
0.51
0.36
rt****
0.41
0.82
0.44
424.53
* 0.012
0.38
0.16
0.57
0.57
0.38
w****
0.44
PIPE NO.
8: 49
LF - 12"CP
@ 6.59%
OUTLET:
424.19
INLET: 427.42 INTYP: 5
JUNC NO.
8: OVERFLOW -EL: 433.50 BEND:
27
DEG
DIA/WIDTH:
4.0
Q -RATIO:
0.20
Q(CFS)
HW(FT)
HW ELEV.
N -FAC
DC
DN
TW
00
DE
HWO
HWI
0.10
0.14
427.56
* 0.012
0.13
0.08
0.04
0.08
0.13
*****
0.14
0.20
0.21
427.63
* 0.012
0.19
0.10
0.09
0.10
0.19
hrthrtrr
0.21
0.29
0.27
427.69
0.012
0.23
0.12
0.13
0.13
0.23
*ww"*
0.27
0.39
0.32
427.74
rr 0.012
0.26
0.14
0.18
0.18
0.26
*w*tl<rt
0.32
0.49
0.36
427.78
w 0.012
0.30
0.16
0.23
0.23
0.30
****w
0.36
0.59
0.40
427.82
w 0.012
0.32
0.17
0.27
0.27
0.32
*wi`*w
0.40
0.69
0.44
427.86
* 0.012
0.35
0.18
0.31
0.31
0.35
i°*i`i`w
0.44
0.78
0.48
427.90
* 0.012
0.37
0.20
0.34
0.34
0.37
i°****
0.48
PIPE NO. 9: 47 LF - 12"CP @ 8.06% OUTLET: 430.36 INLET: 434.15 INTYP: 5
JUNC NO. 9: OVERFLOW -EL: 437.73 BEND: 23 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.43
Q(CFS)
HW(FT)
HW ELEV.
h N -FAC
DC
DN
TW
DO
DE
HWO
HWI
****hwhrthhwrrhrt*****ir*�*�***wwhwhn*�rrrr***�**�*******wwrrw*wrrrthrr**ir****w*****wwwwh
0.08
0.12
434.27
* 0.012
0.12
0.07
0.00
0.07
0.12
*i`***
0.12
0.16
0.18
434.33
* 0.012
0.17
0.09
0.00
0.09
0.17
*****
0.18
0.24
0.24
434.39
* 0.012
0.21
0.11
0.00
0.11
0.21
hw***
0.24
0.33
0.28
434.43
rt 0.012
0.24
0.12
0.00
0.12
0.24
*wrthw
0.28
0.41
0.32
434.47
h 0.012
0.27
0.14
0.00
0.14
0.27
****w
0.32
0.49
0.36
434.51
* 0.012
0.30
0.15
0.00
0.15
0.30
*****
0.36
0.57
0.39
434.54
* 0.012
0.32
0.16
0.00
0.16
0.32
*****
0.39
0.65
0.42
434.57
* 0.012
0.34
0.17
0.00
0.17
0.34
*****
0.42
PIPE NO.10: 78 LF - 12"CP @ 12.36% OUTLET: 434.25 INLET: 443.89 INTYP: 5
JUNC NO.10: OVERFLOW -EL: 447.48 BEND: 30 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.23
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
DN
TW
DO
DE
HWO
HWI
0.06
0.10
443.99
* 0.012
0.10
0.05
0.02
0.05
0.10
*****
0.07
0.11
0.14
444.03
* 0.012
0.14
0.07
0.08
0.08
0.14
*****
0.12
0.17
0.17
444.06
* 0.012
0.17
0.08
0.14
0.14
0.17
****
0.17
0,23
0.20
444.09
* 0.012
0.20
0.10
0.18
0.18
0.20
****
0.20
0.29
0.24
444.13
* 0.012
0.22
0.11
0.22
0.22
0.22
*****
0.24
0.34
0.27
444.16
* 0.012
0.25
0.11
0.26
0.26
0.25
*****
0.27
0.40
0.29
444.18
* 0.012
0.27
0.12
0.29
0.29
0.27
**y**
0.29
0.46
0.32
444.21
* 0.012
0.28
0.13
0.32
0.32
0.28
w****
0.32
PIPE NO.11: 66 LF - 12"CP @ 9.70% OUTLET: 443.99 INLET: 450.39 INTYP: 5
JUNC NO.11: OVERFLOW -EL: 453.79 BEND: 25 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.60
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
DN
Tw
DO
DE
HWO
HWI
>4wwwTM*w�**i<*w*w*�wwi<wTMk�**�*www��wwTM»*ir*k�**i<w****www*wkk***wwi:
0.05
0.09
450.48
* 0.032
0.09
0.05
0.00
0.05
0.09
*ww*}
0.07
0.09
0.13
450.52
* 0.012
0.13
0.07
0.04
0.07
0.13
*ww**
0.12
0.14
0.16
450.55
* 0.012
0.16
0.08
0.07
0.08
0.16
**wTM*
0.16
0.19
0.19
450.58
* 0.012
0.18
0.09
0.10
0.10
0.18
**TMTM*
0.19
0.23
0.22
450.61
* 0.012
0.20
0.10
0.14
0.14
0.20
***k
0.22
0.28
0.25
450.64
* 0.012
0.22
0.11
0.17
0.17
0.22
**wwTM
0.25
0.32
0.27
450.66
* 0.012
0.24
0.12
0.19
0.19
0.24
i°*i wk
0.27
0.37
0.29
450.68
* 0.012
0.26
0.13
0.22
0.22
0.26
****w
0.29
PIPE NO.12: 27
LF - 12"CP
@ 7.19%
OUTLET:
450.49
INLET: 452.43 INTYP: 5
JUNC NO.12: OVERFLOW -EL: 455.86 BEND:
23
DEG
DIA/WIDTH:
2.0
Q -RATIO:
0.62
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
DN
TW
DO
DE
HWO
HWI
w4 Yrkk*****w*ww**wwTMwTMTMk********w4wkkk*TMk******w**whRhTMkkk****wir**w*wwkk*i<******
0.03
0.07
452.50
* 0.012
0.07
0.04
0.00
0.04
0.07
YrTMk**
0.06
0.06
0.10
452.53
* 0.012
0.10
0.06
0.03
0.06
0.10
wTM***
0.10
0.09
0.13
452.56
0.012
0.13
0.07
0.06
0.07
0.13
w°***
0.13
0.12
0.15
452.58
* 4.012
0.14
0.08
0.09
0.09
0.14
wTM***
0.15
0.15
0.17
452.60
* 0.012
0.16
0.09
0.12
0.12
0.16
**"**
0.17
0.17
0.20
452.63
w 0.012
0.18
0.10
0.15
0.15
0.18
*****
0.20
0.20
0.21
452.64
0.012
0.19
0.10
0.17
0.17
0.19
*****
0.21
0.23
0.23
452.66
* 0.012
0.20
0.11
0.19
0.19
0.20
wTM***
0.23
PIPE NO.13: 61 LF - 12"CP @ 6.18% OUTLET: 452.53 INLET: 456.30 INTYP: 5
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DN
TW
DO
DE
HWO
HWI
**DC
0.02
0.06
456.36
* 0.012
0.06
0.04
0.00
0.04
0.06
TMTM***
0.04
0.04
0.08
456.38
* 0.012
0.08
0.05
0.00
0.05
0.08
*****
0.06
0.05
0.10
456.40
0.012
0.10
0.06
0.03
0.06
0.10
TM***
0.08
0.07
0.11
456.41
* 0.012
0.11
0.07
0.05
0.07
0.11
*****
0.10
0.09
0.13
456.43
* 0.012
0.13
0.07
0.07
0.07
0.13**i`*
0.12
0.11
0.14
456.44
0.012
0.14
0.08
0.10
0.10
0.14
***
0.13
0.13
0.15
456.45
0.012
0.15
0.09
0.11
0.11
0.15***
0.15
0.14
0.16
456.46
* 0.012
0.16
0.09
0.13
0.13
0.16
*****
0.16
File
opened
for writing:191st.bwt
Save results to HW/TW file:191st.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
FLEUWE ©ES WOMB o COMER PLA78
1 23HD C 00MYEVQNCE BYSYEM
0 80 100 N
SCALL: 1" = 100 !k
I
123rd street Conveyance Calcs
6/17/08
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 6.00
File opened for Reading:123rd.bwp
File opened for writing:123rd.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:123rd.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:399.66 feet
Dischar a Range:0.5 to 3. step of 0.5 [cfs]
overflow E?evation:462.42 feet
weir:NONE
Upstream velocity:l. feet/sec
PIPE NO. 1: 24 LF - 12"CP @ 12.00% OUTLET: 401.79 INLET: 404.67 INTYP: 5
]UNC NO. 1: OVERFLOW -EL: 408.46 BEND: 27 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.25
Q(CFS) HW(FT) HW ELEV. N -FAC DC DN TW 00 DE HWO HWI
0.50 0.34 405.01 * 0.012 0.30 0.14 0.00 0.14 0.30 **** 0.34
1.00 0.52 405.19 * 0.012 0.43 0.19 0.00 0.19 0.43 ***** 0.52
1.50 0.68 405.35 * 0.012 0.52 0.23 0.00 0.23 0.52 ***** 0.68
2.00 0.82 405.49 * 0.012 0.61 0.27 0.00 0.27 0.61 ****§ 0.82
2.50 0.96 405.63 * 0.012 0.68 0.30 0.00 0.30 0.68 ***** 0.96
3.00 1.10 405.77 * 0.012 0.75 0.33 0.00 0.33 0.75 ***** 1.10
PIPE NO. 2: 98 LF - 12"CP @ 11.60% OUTLET: 404.77 INLET: 416.14 INTYP: 5
JUNC NO. 2: OVERFLOW -EL: 420.07 BEND: 10 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.19
Q(CFS) HW(FT) HW ELEV. N -FAC OC DN TW DO DE HWO HWI
0.40 0.30 416.44 * 0.012 0.27 0.12 0.24 0.24 0.27*** 0.30
0.80 0.46 416.60 * 0.012 0.38 0.17 0.42 0.42 0.38 ***** 0.46
1.20 0.58 416.72 * 0.012 0.47 0.21 0.58 0.58 0.47 ***** 0.58
1.60 0.70 416.84 * 0.012 0.54 0.24 0.72 0.72 0.54 ***** 0.70
2.00 0.81 416.95 * 0.012 0.61 0.27 0.86 0.86 0.61 *i'*** 0.81
2.40 0.91 417.05 * 0.012 0.67 0.29 1.00 1.00 0.67 ***** 0.91
PIPE NO. 3: 136 LF - 12"CP @ 8.57% OUTLET: 416.24 INLET: 427.90 INTYP: 5
JUNG NO. 3: OVERFLOW -EL: 435.88 BEND: 52 DEG DTA/WIDTH: 2.0 Q -RATIO: 0.33
Q(CFS) HW(FT) HW ELEV. * N -FAC DC ON TW DO DE HWO HWI
0.34 0.28 428.18 * 0.012 0.24 0.12 0.20 0.20 0.24 ***** 0.28
0.67 0.43 428.33 * 0.012 0.35 0.17 0.36 0.36 0.35 ***** 0.43
1.01 0.55 428.45 * 0.012 0.43 0.21 0.48 0.48 0.43 ***** 0.55
1.34 0.66 428.56 * 0.012 0.50 0.24 0.60 0.60 0.50 ***** 0.66
1.68 0.77 428.67 * 0.012 0.56 0.27 0.71 0.71 0.56 ***** 0.77
2.02 0.87 428.77 * 0.012 0.61 0.29 0.81 0.81 0.61 ***** 0.87
PIPE NO. 4: 74 LF - 12"CP @ 17.09% OUTLET: 428.00 INLET: 440.65 INTYP: 5
JUNC NO. 4: OVERFLOW -EL: 444.62 BEND: 18 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.62
Q(CFS) HW(FT) HW ELEV. * N -FAC DC ON TW DO DE HWO HWI
0.25 0.21 440.86 * 0.012 0.21 0.09 0.18 0.18 0.21 ***** 0.19
0.51 0.32 440.97 w 0.012 0.30 0.13 0.33 0.33 0.30 ***** 0.32
0.76 0.42 441.07 * 0.012 0.37 0.15 0,45 D.45 0.37 ***** 0.42
1.01 0.51 441.16 * 0.012 0.43 0.18 0.56 0.56 0.43 ***** 0.51
1.26 0.59 441.24 * 0.012 0.48 0.20 0.67 0.67 0.48 f'**** 0.59
1.52 0.67 441.32 * 0.012 0.53 0.21 0.77 D.77 0.53 **w 0.67
PIPE NO. 5: 40 LF - 12"CP @ 10.00% OUTLET: 440.75 INLET: 444.75 INTYP: 5
JUNC NO. 5: OVERFLOW -EL: 448.65 BEND: 90 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.07
Q(CFS) HW(FT) HW ELEV. N -FAC DC ON TW DO DE HWO HWI
0.16 0.17 444.92 0.012 0.17 0.08 0.11 0.11 0.17 ***** 0.17
0.31 0.26 445.01 * 0.012 0.24 0.12 0.22 0.22 0.24 ***** 0.26
0.47 0.34 445.09 * 0.012 0.29 0.14 0.32 0.32 0.29 ***** 0.34
0.62 0.41 445.16 * 0.012 0.33 0.16 0.41 0.41 0.33 ***** 0.41
0.78 0.47 445.22 0.012 0.37 0.18 0.49 0.49 0.37 ***** 0.47
0.94 0.53 445.28 * 0.012 0.41 0.19 0.57 0.57 0.41 ***** 0.53
PIPE NO. 6: 24 LF - 12"CP @ 1.00% OUTLET: 444.85 INLET: 445.09 INTYP: 5
JUNC NO. 6: OVERFLOW -EL: 448.65 BEND: 90 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.17
Q(CFS)
HW(FT)
HW ELEV. * N -FAC DC ON TW DO DE HWO HWI
**w*#*itw whwh*hh**w**Yr*##hh*hwww#wwhhrthhh*w*##wYr###hh*h*ww*wYr##hhhwrtwwwwwi:hhhw*w
0.15
0.21 445.30
* 0.012
0.16
0.14
0.07
0.14
0.16
wwhww
0.21
0.29
0.30
445.39
* 0.012
0.23
0.19
0.16
0.19
0.23
hwirww
0.30
0.44
0.37
445.46
* 0.012
0.28
0.23
0.24
0.24
0.28
i`wwww
0.37
0.58
0.44
445.53
* 0.012
0.32
0.27
0.31
0.31
0.32
**www
0.44
0.73
0.50
445.59
* 0.012
0.36
0.30
0.37
0.37
0.36
*www#
0.5D
0.87
0.55
445.64
* 0.012
0.40
0.33
0.43
0.43
0.40
*wwY`w
0.55
PIPE NO.
7: 122
LF - 12"CP
@ 8.78%
OUTLET:
445.19
INLET: 455.90 INTYP: 5
)UNC NO.
7: OVERFLOW -EL: 459.10 BEND:
34
DEG
DIA/WIDTH:
2.0
Q -RATIO:
0.51
Q(CFS)
HW(FT)
HW ELEV.
* N -FAC
DC
DN
TW
DO
DE
HWO
HWI
*###www##h#hhhw*###ww#w#hhhwww#wwwwwh*how#ww#wwww##hhhhh*###ww##irhh#**w#www#hhw
0.12
0.15
456.05
0.012
0.15
0.08
0.11
0.11
0.15
***ww
0.15
0.25
0.23
456.13
0.012
0.21
0.11
0.20
0.20
0.21
**i`ww
0.23
D.37
0.30
456.20
0.012
0.26
0.13
0.27
0.27
0.26
***ww
0.30
0.50
0.36
456.26
* 0.012
0.30
0.15
0.34
0.34
0.30
wY'*ww
0.36
0.62
0.41
456.31
w 0.012
0.33
0.16
0.40
0.40
0.33
**w##
0.41
0.75
0.46
456.36
* 0.012
0.37
0.18
0.45
0.45
0.37
ww*#*
0.46
PIPE NO.
8: 40
LF - 12"CP
@ 4.38%
OUTLET:
456.00
INLET: 457.75 INTYP: 5
JUNC NO.
8: OVERFLOW
-EL: 460.88 BEND:
18
DEG
DIA/WIDTH:
2.D
Q -RATIO:
1.30
Q(CFS)
HW(FT)
HW ELEV.
# N -FAC
DC
DN
TW
DO
DE
HWO
HWI
wwhhhhhwww*wwwwww#hhww*wwwww#i:#h�ww#wwwww##hhhww*wwwwaw##hhh**wwwwwwhhh*w**#www
0.08
0.14
457.89
# 0.012
0.12
0.08
0.05
0.08
0.12
****
0.14
0.17
0.20
457.95
w 0.012
0.17
0.10
0.13
0.13
0.17
*****
0.20
0.25
0.26
458.01
* 0.012
0.21
0.13
0.20
0.20
0.21
#*hhw
0.26
0.33
0.30
458.05
* 0.012
0.24
0.14
0.26
0.26
0.24
#****
0.30
0.41
0.34
458.09
* 0.012
0.27
0.16
0.31
0.31
0.27
*****
0.34
0.50
0.38
458.13
* 0.012
0.30
0.17
0.36
0.36
0.30
h***
0.38
PIPE NO.
9: 99
LF - 12"CP
@ 1.59%
OUTLET:
457.85
INLET: 459.42 INTYP: 5
Q(CFS)
HW(FT)
HW ELEV.
N -FAC
DC
DN
TW
DO
DE
HWO
HWI
hhw*ww*wwi<###hhw#wwYrwwwR##hhhwwwwwwww###hhhwww#wwwww#**h*w*#wwwww##hhw#*wwwwYr*#
0.04
0.08
459.50
h 0.012
0.08
0.07
0.04
0.07
0.08
*****
0.08
0.07
0.12
459.54
* 0.012
0.11
0.09
0.10
0.10
0.11
0.12
0.11
0.16
459.58
* 0.012
0.14
0.11
0.16
0.16
0.14
w#hh*
0.16
0.14
0.19
459.61
w 0.012
0.16
0.12
0.20
0.20
0.16
ww#**
0.19
0.18
0.21
459.63
* 0.012
0.18
0.14
0.24
0.24
0.18
www#
0.21
0.22
0.23
459.65
* 0.012
0.20
0.15
0.28
0.28
0.20
***#w
0.23
File
Opened
for writing:123rd.bwt
Save results to HW/TW file:123rd.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 6.00
124th Street Conveyance Calcs
6/11/08
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 6.00
File opened for Reading:124th.bwp
File opened for writing:124th.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:124th.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:372.8 feet
Dischargge Range:0.5 to 2. Step of 0.5 [cfs]
overflow Elevation:382.93 feet
Weir:NONE
upstream velocity:1. feet/sec
PIPE NO. 1: 208 LF - 12"CP @ 1.67% OUTLET: 371.80 INLET: 375.27 INTYP: 5
JUNC NO. 1: OVERFLOW -EL: 378.37 BEND: 0 DEG DIA/WIDTH: 2.0 Q -RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. * N -FAC DC DN Tw DO DE HWO HWI
0.50 0.39 375.66 * 0.012 0.30 0.22 1.00 1.00 0.30 ***** 0.39
1.00 0.56 375.83 * 0.012 0.43 0.31 1.00 1.00 0.43 **** 0.56
1.50 0.70 375.97 * 0.012 0.52 0.38 1.00 1.00 0.52 **** 0.70
2.00 0.81 376.08 * 0.012 0.61 0.45 1.00 1.00 0.61 ***** 0.81
PIPE NO. 2: 211 LF - 12"CP @ 1.27% OUTLET: 375.37 INLET: 378.04 INTYP: 5
JUNC NO. 2: OVERFLOW -EL: 392.06 BEND: 90 DEG DIA/WIDTH: 4.0 Q -RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. * N -FAC DC DN TW DO DE HWO HWI
0.50 0.40 378.44 * 0.012 0,30 0.23 0.29 0.29 0.30 *** 0.40
1.00 0.60 378.64 * 0.012 0.43 0.33 0.46 0.46 0.43 ***W" 0.60
1.50 0.77 378.81 * 0.012 0.52 0.41 0.60 0.60 0.52 **TMTM" 0.77
2.00 0.95 378.99 * 0.012 0.61 0.48 0.71 0.71 0.61 ***** 0.95
PIPE NO. 3: 174 LF - 12"CP @ 0.50% OUTLET: 378.14 INLET: 379.01 INTYP: 5
JUNC NO. 3: OVERFLOW -EL: 384.41 BEND: 0 DEG DIA/WIDTH: 4.0 Q -RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. N -FAC DC DN TW DO DE HWO HWI
0.50 0.39 379.40 * 0.012 0.30 0.29 0.30 0.30 0.30 **** 0.39
1.00 0.57 379.58 * 0.012 0.43 0.42 0.50 0.50 0.43 ***** 0.57
1.50 0.77 379.78 * 0.012 0.52 0.53 0.67 0.67 0.53 0.77 0.70
2.00 0.87 379.88 0.012 0.61 0.64 0.85 0.85 0.64 0.87 0.82
PIPE NO. 4: 144 LF - 12"CP @ 0.50% OUTLET: 379.11 INLET: 379.83 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N -FAC DC DN TW DO DE HWO HWI
0.50 0.38 380.21 0.012 0.30 0.29 0.29 0.29 0.30 ***** 0,38
1.00 0.58 380.41 * 0.012 0.43 0.42 0.47 0.47 0.43 **rr** 0.58
1.50 0.81 380.64 * 0.012 0.52 0.53 0.67 0.67 0.53 0.81 0.74
2.00 0.96 380.79 * 0.012 0.61 0.64 0.77 0.77 0.64 0.96 0.90
File Opened for writing:124th.bwt
Save results to HW/TW file:124th.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 6.00
APPENDIX D
MAINTENANCE REQUIREMENTS
FOR
PRIVATELY MAINTAINED DRAINAGE FACILITIES
MAINTENANCE AND OPERATIONS MANUAL
FOR PRIVATELY MAINTAINED DRAINAGE FACILITIES
ADDRESS: 12216 SE 192"d Street
Renton, Washington
RETENTION/DETENTION FACILITIES
The purpose of the detention pond is to reduce the rate of runoff from the developed portions of
the property. Water can flow freely into the pond, but orifices in the outflow riser restrict the
outflow. When the inflow exceeds the capacity of the orifice, the excess water is "stored" in the
pond, and released slowly after the storm abates.
In order to function properly, the facility must also be kept free of accumulated sediment. The
outlet and connection pipes also must be kept clean, as even a partial blockage could
significantly impact the ability of the facility to store runoff. The facility should be visually
inspected for sediment accumulation and blockages at least once each year and also after
every major storm greater than or equal to a 1 0 -year return frequency.
WATER QUALITY TREATMENT FACILITIES
The purpose of both the permanently wet portions of the pond and the cartridge filter treatment
catch basins is to reduce the level of contaminants in the runoff water, through filtration and
sedimentation, though the plants in the wetpond will also reduce pollutants though bio -uptake.
It is essential that the water quality pond have calm conditions and be inspected regularly for
accumulation of sediment. The pond should be visually inspected for sediment accumulation
and blockages at least once each year and also after every major storm greater than or equal:
to a 14 -year return frequency. The cartridge filter treatment catch basins should be maintained
in accordance with the manufacturer's recommendations.
CONVEYANCE SYSTEMS
Pipes transport runoff from one place to another, in this case from catch basins to the pond,
then to the downstream drainage system. To work properly, pipes must be kept free of silt and
other debris. If pipes become blocked, surface flooding will usually occur.
CATCH BASINS AND AREA DRAINS
Gatch basins collect surface drainage and direct it into storm conveyance pipes. They help
prevent downstream drainage problems by trapping sediment and other debris that would
otherwise flow downstream with the runoff. It is important to keep catch basins clean so
accumulated silt is not flushed out during a significant storm. Also, if the outflow pipe becomes
blocked with debris, surface flooding will usually occur. All catch basins should be inspected at
least once each year and after major storms.
Area drains convey runoff directly into conveyance pipes. To prevent surface flooding, their
surface grates must be kept free of litter and debris. If dirt or other sediment gets into the pipes
and they become blocked, the pipes will need to be cleaned, either manually or using a Vactor
truck.
The following tables identify maintenance issues, which should be addressed regularly,
describing possible problems with the drainage system and their respective solutions.
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
APPENDIX A
MAINTENANCE REQUIREMENTS FOR FLOW
CONTROL, CONVEYANCE, AND WQ FACILITIES
NO.1 - DETEh
Maintenance
Component
General
(TION PONDS
Defect or Problem Conditions When Maintenance Is !deeded Resufts Expected When
Maintenance Is Performed
Trash & Debris Any trash and debris which exceed 1 cubic foot Trash and debris cleared from site.
per 1,000 square feet (this is about equal to the
amount of trash it would take to fill up one
standard size office garbage can). In general,
there should be no visual evidence of dumping.
Poisonous Vegetation
Any poisonous or nuisance vegetation which may
No danger of poisonous vegetation
or Noxious Weeds
constitute a hazard to County personnel or the
where County personnel or the
public,
public might normally be.
Coordination with Seattle -King
County Health Department
Contaminants and
Oil, gasoline, or other contaminants of one gallon
No contaminants present other than
Pollution
or more, or any amount found that could:
a surface film. (Coordination with
3) cause damage to plant, animal, or marine life;
Seattle/King County Health
2) constitute a fire hazard; or 3) be flushed
Department)
downstream during rain storms.
Unmowed
If facility is located in private residential area,
When mowing is needed,
Grass/Ground Cover
mowing is needed when grass exceeds 18
grass/ground cover should be
inches in height. In other areas, the general
mowed to 2 inches in height.
policy is to make the pond site match adjacent
Mowing of seiected higher use areas
ground cover and terrain as long as there is no
rather than the entire slope may be
interference with the function of the facility.
acceptable for some situations.
Rodent Hoies
Any evidence of rodent holes if facility is acting
Rodents destroyed and dam or berm
as a dam or berm, or any evidence of water
repaired. (Coordination with
piping through dam or bene via rodent holes or
Seattle/King County Health
other causes.
Department)
Insects
When insects such as wasps and hornets
Insects destroyed or removed from
interfere with maintenance activities. Mosquito
site. Mosquito control; Swalfow
complaints accompanied by presence of high
nesting boxes or approved larvicide
mosquito larvae concentrations (aquatic phase).
applied.
Tree Growth
Tree growth threatens integrity of berms acting
Trees do not hinder maintenance
as dams, does not allow maintenance access, or
activities. Harvested trees should
interferes with maintenance activity (i.e., slope
be recycled into mulch or other
mowing, silt removal, vactoring, or equipment
beneficial uses (e.g., alders for
movements). If trees are a threat to berm
firewood).
integrity or not interfering with access, leave
trees alone.
2005 Surface Water Design Manual — Appendix A 1/24/2405
A -i
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES
NO. 1 - DETENTION
PONDS
Maintenance
Defect or Problem
Conditions When Maintenance Is Needed
Results Expected When
Component
Maintenance Is Performed
Side Slopes of Pond
Erosion
Eroded damage over 2 inches deep where cause
Slopes should be stabilized by using
of damage is still present or where there is
appropriate erosion control
potentia€ for continued erosion.
measure(s); e.g., rock
reinforcement, planting of grass,
Any erosion observed on a compacted berm
compaction.
embankment.
If erosion is occurring on compacted
berms a licensed civil engineer
Should be consulted to resolve
source of erosion.
Storage Area
Sediment
Accumulated sediment that exceeds 10% of the
Sediment cleaned out to designed
designed pond depth.
pond shape and depth; pond
reseeded if necessary to control
erasion.
Liner Damage
Liner is visible and has more than three/4-inch
Liner repaired or replaced.
(If Applicable)
holes in it.
Pond Berms (Dikes)
Settlement
Any part of berm that has settled 4 inches lower
Dike should be built back to the
than the design elevation. Settling can be an
design elevation.
indication of more severe problems with the berm
or outlet works. A licensed civil engineer should
be consulted to determine the source of the
settlement.
Emergency
Tree Growth
Tree growth on emergency spillways create
Trees should be removed. If root
Overflow/Spillway
blockage problems and may cause fakure of the
system is small (base less than 4
and Berms over 4
berm due to uncontrolled overtopping.
inches) the root system may be left
feet in height.in
Tree growth on berms over 4 feet in height may
place. Otherwise the roots should
be removed and the berm restored.
lead to piping through the berm which could lead
A licensed civil engineer should be
to failure of the berm.
consulted for proper bermispillway
restoration,
Emergency
Rock Missing
Only one layer of rock exists above native soil in
Replace rocks to design standards,
Overflow/Spillway
area five square feet or larger, or any exposure
of native soil at the top of out flow path of
spillway. Rip -rap on inside slopes need not be
replaced.
P24/2005 2005 Surface Water Design Manual — Appendix A
A-2
APPENDIX A MAIAITENANCE REQUIREMENTS FOR FLOW CONTROL, CONIVEYANCE, AND WQ FACILITIES
NO.4 - CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance
Component
Defect or Problem
Condition When Maintenance is Needed
Results Expected When
Maintenance is Performed
General
Trash and Debris
Distance between debris build-up and bottom of
All trash and debris removed.
(Includes Sediment)
orifice plate is less than 1.5 feet,
Structural Damage
Structure is not securely attached to manhole
wall and outlet pipe structure should support at
Structure securely attached to wall
and outlet pipe.
least 1,0001bs of up or down pressure.
Structure is not in upright position (allow up to
Structure in correct position.
10% from plumb),
Connections to outlet pipe are not watertight and
show signs of rust.
Connections to outlet pipe are water
tight; structure repaired or replaced
and works as designed.
Any holes --other than designed holes—in the
structure.
Structure has no holes other than
designed holes.
Cleanout Gate
Damaged or Missing
Cleanout gate is not watertight or is missing.
Gate is watertight and works as
designed.
Gate cannot be moved up and down by one
Gate moves up and down easily and
maintenance person.
is watertight.
Chain/rod leading to gate is missing or damaged.
Chain is in place and works as
designed.
Gate is rusted over 50% of its surface area.
Gate is repaired or replaced to meet
design standards.
Orifice Plate
Damaged or Missing
Control device is not working properly due to
missing, out of place, or bent orifice plate.
Plate is in place and works as
designed.
Obstructions
Any trash, debris, sediment, or vegetation
blocking the plate.
Plate is free of all obstructions and
works as designed.
Overflow Pipe
Obstructions
Any trash or debris blocking (or having the
potential of blocking) the overflow pipe.
Pipe is free of all obstructions and
works as designed.
Manhole
See "Detention Tanks
and Vaults"
See "Detention Tanks and Vaults" Table No. 3
See "Detention Tanks and Vaults"
Table No, 3
2045 Surface Water Design Manual – Appendix A 112412005
A-5
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES
NO.5 - CATCH BASINS
Maintenance
Component
Defect or Problem
Conditions When Maintenance is Needed
Results Expected When
Maintenance is performed
General
Trash & Debris
(Includes Sediment)
Trash or debris of more than '/s cubic foot which
is located immediately in front of the catch basin
opening or is blocking capacity of the basin by
No Trash or debris located
immediately in front of catch basin
opening.
more than 10%.
Trash or debris (in the basin) that exceeds 'Y3 the
No trash or debris in the catch
depth from the bottom of basin to invert the
basin,
lowest pipe into or out of the basin.
Trash or debris in any inlet or outlet pipe blocking
more than 113 of its height.
Inlet and outlet pipes free of trash or
debris.
[Dead animals or vegetation that could generate
odors that could cause complaints or dangerous
No dead animals or vegetation
present within the catch basin.
gases (e.g., methane).
Deposits of garbage exceeding 1 cubic foot in
volume.
No condition present which would
attract or support the breeding of
insects or rodents.
Structure Damage to
Comer of frame extends more than % inch past
Frame is even with curb,
Frame and/or Top
curb face into the street (if applicable).
Slab
Top slab has holes larger than 2 square inches
Tap slab is free of holes and cranks,
or cracks wider than '/. inch (intent is to make
sure all material is running into basin).
Frame not sitting flush on top slab, i.e.,
Frame is sitting Flush on top slab.
separation of more than'/, inch of the frame from
the top slab.
Cracks in Basin
Walls/Bottom
Cracks wider than'/. inch and longer than 3 feet,
any evidence of soil particles entering catch
Basin replaced or repaired to design
standards.
basin through cracks, or maintenance person
judges that structure is unsound.
Cracks wider than'/� inch and longer than 1 foot
No cracks more than 114 inch wide at
at the joint of any inlet outlet pipe or any
the joint of inlet/outlet pipe.
evidence of soil particles entering catch basin
through cracks.
Settlement/
Misalignment
Basin has settled more than 1 inch or has rotated
more than 2 inches out of alignment.
Basin replaced or repaired to design
standards.
Fire Hazard
Presence of chemicals such as natural gas, oil
No flammable chemicals present.
and gasoline.
Vegetation
Vegetation growing across and blocking more
than 10% of the basin opening.
No vegetation blocking opening to
basin.
Vegetation growing in inletloutlet pipe joints that
No vegetation or root growth
is more than 6 inches tall and less than 6 inches
present.
apart.
Pollution
Nonflammabie chemicals of more than '/2 cubic
foot per three feet of basin length.
No pollution present other than
surface film.
Catch Basin Cover
Cover Not in Place
Cover is missing or only partially in place. Any
Catch basin cover is closed
open catch basin requires maintenance.
Locking Mechanism
Mechanism cannot be opened by on
Mechanism opens with proper toois.
Not Working
maintenance person with proper tools. Bolts into
frame have less than'/� inch of thread.
Cover Difficult to
Remove
One maintenance person cannot remove lid after
applying 80 lbs. of lift; intent is keep cover from
Cover can be removed by one
maintenance person.
sealing off access to maintenance.
Ladder
Ladder Rungs Unsafe
Ladder is unsafe due to missing rungs,
misalignment, rust, cracks, or sharp edges,
Ladder meets design standards and
allows maintenance person safe
access.
1/24/2005 2005 Surface Water Design Manual — Appendix A
A-6
APPENDIX A MAINTENANCE REQVIREMEN S FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES
NO.5 --- CATCH BASINS
Maintenance Detect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is performed
Metal Grates Unsafe Grate Grate with opening wider than 718 inch. Grate opening meets design
(If Applicable) Opening standards.
Trash and Debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surface.
Damaged or Missing, Grate missing or broken member(s) of the grate. Grate is in place and meets design
standards.
NO.6 - DEBRIS BARRIERS (E.G., TRASH RACKS)
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed.
General
Trash and Debris
Trash or debris that is plugging more than 20%
Barrier clear to receive capacity
Missing or Moved
Rock
Only one layer of rock exists above native soil in
area five square feet or larger, or any exposure
of the openings in the barrier.
flow.
Metal
Damaged/Missing
Bars are bent out of shape more than 3 inches.
Bars in place with no bends more
Pipe Plugged with
Sediment
Bars.
Pipe cleanedMushed so that it
matches design.
than'/. inch.
Bars are missing or entire barrier missing.
Bars in place according to design.
Bars are loose and rust is causing 50%
Repair or replace barrier to design
Perforations Plugged.
Over 1/2 of perforations in pipe are plugged with
deterioration to any part of barrier.
standards.
NO.7 - ENERGY DISSIPATERS
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed.
External:
Rock Pad
Missing or Moved
Rock
Only one layer of rock exists above native soil in
area five square feet or larger, or any exposure
Replace rocks to design standards.
of native soil.
Dispersion Trench
Pipe Plugged with
Sediment
Accumulated sediment that exceeds 20% of the
design depth,
Pipe cleanedMushed so that it
matches design.
Not Discharging
Water Properly
Visual evidence of water discharging at
concentrated points along trench (normal
condition is a "sheet flow" of water along trench).
Trench must be redesigned or
rebuR to standards.
Intent is to prevent erosion damage.
Perforations Plugged.
Over 1/2 of perforations in pipe are plugged with
Clean or replace perforated pipe.
debris and sediment,
Water Flows Out Top
of "Distributor" Catch
Maintenance person observes water flowing out
during any storm less than the design storm or
Facility must be rebuilt or
redesigned to standards.
Basin.
its causing or appears likely to cause damage.
Receiving Area Over-
Water in receiving area is causing or has
No danger of landslides.
Saturated
potential of causing landslide problems.
Internal:
Manhole/Chamber
Worn or Damaged
Post. Baffles, Side of
Structure dissipating flow deteriorates to Y� or
original size or any concentrated worn spot
Replace structure to design
standards.
Chamber
exceeding one square foci which would make
structure unsound.
2005 Surface Water Design Manual — Appendix A 1/24/2005
A-7
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES
NO, S - FENCING
Maintenance
Component
Defect or Problem
Conditions When Maintenance is Needed
Results Expected When
Maintenance is Performed
General
Missing or Broken
Parts
Any defect in the fence that permits easy entry to
a facility.
Parts in place to provide adequate
security.
Erosion
Erosion more than 4 inches high and 12-18
inches wide permitting an opening under a fence.
No opening under the fence that
exceeds 4 inches in height.
Wire Fences
Damaged Parts
Post out of plumb more than 6 inches.
Post plumb to within 1 %z inches.
Top rails bent more than 6 inches.
Top rail free of bends greater than
person.
Gate is out of plumb more than 6 inches and
Gate is aligned and vertical.
1 inch.
more than 1 foot out of design alignment.
Any part of fence (including post, top rails, and
fabric) more than 1 foot out of design alignment.
Fence is aligned and meets design
standards.
Missing or loose tension wire.
Tension wire in place and holding
fabric.
See "Fencing" Table No. 8
See "Fencing' Table No, 8
Missing or loose barbed wire that is sagging
more than 2'/s inches between posts.
Barbed wire in place with less than
3/4 inch sag between post.
Extension arm missing, broken, or bent out of
shape more than 1 % inches.
Extension arm in place with no
bends larger than 1% inch.
Deteriorated Paint or
Protective Coating
Part or parts that have a rusting or scaling
condition that has affected structural adequacy.
Structurally adequate posts or parts
with a uniform protective coating.
Openings in Fabric
Openings in fabric are such that an 8 -inch
No openings in fabric.
diameter bell could fit through.
NO.9 - GATES
Mafntenance Defect or. Problem
Component
Conditions When Maintenance is Needed
Results Expected When
Maintenance is Performed
General Damaged or Missing
Missing gate or locking deuces.
Gates and Locking devices in place.
Members
Broken or missing hinges such that gate cannot
Hinges intact and lubed. Gate is
be easily opened and closed by a maintenance
working freely,
person.
Gate is out of plumb more than 6 inches and
Gate is aligned and vertical.
more than 1 foot out of design alignment.
Missing stretcher bar, stretcher bands, and ties.
Stretcher bar, bands, and ties in
place.
Openings in Fabric
See "Fencing" Table No. 8
See "Fencing' Table No, 8
1/24/2005 2005 Surface Water Design Manual -- Appendix A
A-8
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLAW CONTROL, CONVEYANCE, AND WQ FACILITtES
NO. 10 -CONVEYANCE PIPES AND DITCHES
Maintenance
Component
Defect or Problem
Conditions When Maintenance is Needed
Results Expected When
Maintenance is Performed
Pipes
Sediment & Debris
Accumulated sediment that exceeds 20% of the
diameter of the pipe.
Pipe cleaned of all sediment and
debris.
noxious)
Vegetation
Vegetation that reduces free movement of water
through pipes,
Alt vegetation removed so water
flows freely through pipes.
Damaged
Protective coating is damaged; rust is causing
more than 50% deterioration to any part of pipe.
Pipe repaired or replaced.
Area clear of litter.
Any dent that decreases the cross section area
Pipe repaired or replaced.
only) of 1,000 square feet.
Trees and Shrubs Damaged
Limbs or parts of trees or shrubs that are split or
broken which affect more than 25% of the total
of pipe by more than 20%.
Open Ditches
Trash & Debris
Trash and debris exceeds 1 cubic foot per 1,000
square feet of ditch and slopes.
Trash and debris cleared from
ditches.
Sediment
Accumulated sediment that exceeds 20% of the
design depth.
Ditch cleanedlflushed of all
sediment and debris so that it
matches design.
Trees or shrubs which are not adequately
Vegetation
Vegetation that reduces free movement of water
Water flows freely through ditches.
supported or are leaning over, causing exposure
of the roots.
adequately supported; remove any
dead or diseased trees.
through ditches.
Erosion Damage to
See "Detention Ponds" Table No. 1
See "Detention Ponds" Table No. 1
Slopes
Rock Lining Out of
Maintenance person can see native soil beneath
Replace rocks to design standards.
Place or Missing (if
the rock lining.
Applicable).
NO. 11 - GROUNDS (LANDSCAPING)
Maintenance Defect or Problem
Component
Conditions When Maintenance Is Needed
Results Expected When
Maintenance is Performed
General Weeds
(Nonpoisonous, not
Weeds growing in more than 20% of the
landscaped area (trees and shrubs only).
Weeds present in less than 5% of
the landscaped area.
noxious)
Any presence of poison ivy or other poisonous
vegetation.
No poisonous vegetation present in
landscaped area.
Safety Hazard
Paper, cans, bottles, totaling more than 1 cubic
foot within a landscaped area (trees and shrubs
Area clear of litter.
Trash or fitter
only) of 1,000 square feet.
Trees and Shrubs Damaged
Limbs or parts of trees or shrubs that are split or
broken which affect more than 25% of the total
Trees and shrubs with less than 5%
of total foliage with split or broken
foliage of the tree or shrub.
limbs.
Trees or shrubs that have been blown down or
Tree or shrub in place free of injury,
knocked over.
Trees or shrubs which are not adequately
Tree or shrub in place and
supported or are leaning over, causing exposure
of the roots.
adequately supported; remove any
dead or diseased trees.
2005 Surface Water Design Manual — Appendix A L�24I"LUUo
A-9
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES
NO. 12 - ACCESS ROADS
Maintenance
Component
Defect or Problem
Condition When Maintenance is Needed
Results Expected When
Maintenance is Performed
General
Trash and Debris
Trash and debris exceeds 1 cubic foot per 1,000
square feet (i.e., trash and debris would fill up
Roadway free of debris which could
damage tires.
one standards size garbage can).
Blocked Roadway
Debris which could damage vehicle tires (glass
or metal),
Roadway free of debris which could
damage tires.
Any obstruction which reduces clearance above
road surface to less than 14 feet.
Roadway overhead clear to 14 feet
high.
Any obstruction restricting the access to a 10- to
12 -foot width for a distance of more than 12 feet
Obstruction removed to allow at
Least a 12 -foot access.
or any point restricting access to less than a 10 -
foot width.
Road Surface
Settlement, Potholes,
Mush Spots, Ruts
When any surface defect exceeds 6 inches in
depth and 6 square feet in area. In general, any
surface defect which hinders or prevents
Road surface uniformly smooth with
no evidence of settlement, potholes,
mush spots, or ruts.
maintenance access.
Vegetation in Road
Surface
Weeds growing in the road surface that are more
than 6 inches tall and less than 6 inches tall and
less than 6 inches apart within a 400 -square foot
Road surface free of weeds taller
than 2 inches.
area.
Modular Grid
Pavement
Build-up of sediment mildly contaminated with
petroleum hydrocarbons.
Removal of sediment and disposal
in keeping with Health Department
recommendations for miUy
contaminated soils or catch basin
sediments.
Shoulders and
Ditches
Erosion Damage
Erosion within 1 foot of the roadway more than 8
inches wide and 6 inches deep.
Shoulder free of erosion and
matching the surrounding road.
Weeds and Brush
Weeds and brush exceed 18 inches in height or
hinder maintenance access.
Weeds and brush cut to 2 inches in
height or cleared in such a way as to
allow maintenance access.
1/24/2005 2405 Surface Water Design Manual — Appendix A
A-10
APPENDIX A MAINTENANCE REQUMEMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES
NO. 16 - WETPOND
Maintenance
Component
Defect or Problem
Condition When Maintenance is Needed
Recommended Maintenance to
Correct Problem
Pond Area
Water Level
f=irst cell empty, doesn't hold water.
Line the first cell to maintain at least
4 feet of water. Although the second
cell may drain, the first cell must
remain full to control turbulence of
the incoming flow and reduce
sediment resuspension.
Defective Vegetation
Vegetation such as grass and weeds need to be
mowed when it starts to impede aesthetics of
pond. Mowing is generally required when height
exceeds 18 inches. Mowed vegetation should be
Vegetation should be mowed to 4 to
5 inches in height. Trees and
bushes should be removed where
they are interfering with pond
removed from areas where it could enter the
maintenance activities; that is, at the
pond, either when the pond level rises, or by
inlet, outlet and near engineered
rainfall runoff.
structures.
Algae Mats
When algae mats develop over more than 10%
of the water surface, they should be removed.
Algae mats that cover more than
10% of the surface of any cell
Also remove mats in the late summer before fall
should be removed. A rake or
rains, especially in Sensitive Lake Protection
Areas. Excessive algae mats interfere with
dissolved oxygen content in the water and pose a
threat to downstream lakes if excess nutrients
mechanical device should be used
to remove the algae. Removed
algae can be left to dry on the pond
slope above the 100 -year water
are released.
surface.
Trash and Debris
Accumulation that exceeds 1 cubic foot per 1000
square foot of pond area.
Trash and debris removed from
pond.
Sediment
Sediment accumulations in pond bottom that
Removal of sediment from pond
Accumulation
exceeds the depth of sediment zone plus 6
bottom.
inches, usually in the first cell.
Oil Sheen on Water
Prevalent and visible oil sheen.
Remove oil from water by use of oil -
absorbent pads or by vactor truck.
Refer problem to locate source and
correct. If chronic low levels of oil
persist, plant wetland plants such as
Juncus etfusus (soft rush) which
can uptake small concentrations of
oil.
Erosion
Erosion of the pond's side slopes andlor
scouring of the pond bottom, that exceeds 6
Slopes should be stabilized by using
proper erosion control measures,
inches, or where continued erosion is prevalent.
and repair methods,
Pond Dike/Berm
Settlement
Any part of these components that has settled 4
inches or lower than the design elevation, or
Dike/berm is repaired to
specifications.
inspector determines dskelberm is unsound.
Internal Berm
Concentrated Flow
Berm dividing cells should be level.
Build up low areas of berm or lower
high areas so that the berm surface
is level and water flows evenly over
the entire length of the berm from
the first cell to the second.
InletlOutlet Pipe
Sediment and Debris
Inlet/Outlet pipe clogged with sediment and/or
debris material.
No clogging or blockage to the inlet
and outlet piping.
Overflow Spillway
Rock Missing
Rock is missing and soil is exposed at top of
Replace rocks to specifications.
spillway or outside slope.
2005 Surface Water Design Manual — Appendix A 1/24/2005
A -l3
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES
NO. 20 - STORMFILTER°
Maintenance Defect or Problem
Condition When Maintenance is Needed Recommended Maintenance to
Maintenance Defect or Problem
Condition When Maintenance is Needed
Recommended Maintenance to
Component
Correct Problem
Media Section Sediment
Sediment depth exceeds 0.25 inches.
No sediment deposits that would
Accumulation on
Short Circuiting
impede permeability of the compost
Media.
Pipe repaired and/or replaced.
media.
Trash/Debris
Trash and debris accumulated on compost filter
Trash and debris removed from the
Accumulation
bed.
compost filter bed.
First Chamber Sediment
Sediment depth exceeds 6 inches in first
No sediment deposits in vault
Accumulation
chamber.
bottom of first chamber.
Drain Pipes Clean-
Sediment
When drain pipes, clean -outs, become full with
Remove the accumulated material
Outs
Accumulation
sediment and/or debris.
from the facilities.
NO. 21 - STORMFILTERa (CARTRIDGE
TYPE)
Maintenance Defect or Problem
Condition When Maintenance is Needed Recommended Maintenance to
Component
Correct Problem
Compost Media Plugged
Drawdown of water through the media takes Replace media cartridges.
longer than 1 hour, and/or overflow occurs
frequently.
Flows do not properly enter filter cartridges.
Replace filter cartridges.
Short Circuiting
Pipes Damaged
Any part of the pipes that are crushed, damaged
Pipe repaired and/or replaced.
due to corrosion and/or settlement.
Access Cover Damaged/Not
Cover cannot be opened, one person cannot
Cover repaired to proper working
Working
open the cover, corrosion/deformation of cover.
specifications or replaced.
Vault Structure Damage to Wall,
Cracks wider than 1/2 -inch and any evidence of
Vault replaced or repaired to design
Frame, Bottom,
soil particles entering the structure through the
specifications.
and/or Top Slab
cracks, or maintenance/inspection personnel
determines that the vault is not structuralky
sound.
Damaged Pipe Joints
Cracks wider than V inch at the joint of any
No cracks more than Y, -inch wide at
lnletlout}et pipe or any evidence of soil particles
the joint of the inlet/outlet pipe.
entering the vault through the walls.
Baffles
Damaged
Baffles corroding, cracking warping, and/or
Repair or replace baffles to
showing signs of failure as determined by
specification.
maintenanceAnspection person.
Access Ladder
Damaged
Ladder is corroded or deteriorated, not
Ladder replaced or repaired and
functioning properly, missing rungs, cracks, and
meets specifications, and is safe to
misaligned,
use as determined by inspection
personnel.
2005 Surface Water Design. Manual — Appendix A 1/24/2005
A-17
APPENDIX E
BOND QUANTITIES WORKSHEETS
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APPENDIX F
RETENTIONIDETENTION FACILITY
SUMMARY SHEET & SKETCH
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
STORMWATER FACILITY SUMMARY SHEET DDES Permit Number_�d�0�
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location) os -T 00yo
Overview: I ��w¢
Project Name �(.�' ,�Z t Date -7-2-63
Downstream Drainage Basins
Major Basin Name L-aj�� lAkIlli,ng�kr)
Immediate Basin NameSonya fr- 1(
Flow Control:
Flow Control Facility Narne/Number L
Facility Location See b - — C�a� e h s o� V h �� % S!
If none, p g To , /—C I, f
Flaw control provided in re nal hared facilit (give location) /1� t)rt'1��
No flow control required Exemption number
General Facility Information:
Type/Number of detention facilities;
ponds
vaults
tanks
Type/Number of infiltration facilities:
ponds
tanks
trenches
Control Structure Location l L�Ur" f an
Type of Control Structure r 7 Number of Orifices/Restrictions
Size of Orifice/Restriction
No. 1 . 3121
No, 2 !;JK
No.3
Na. 4 �.
Flow Control Performance Standard + ►mss t (lP 'G�P fi or
Live Storage Volume Depth Volume Factor of Safety
Number of Acres Served
Number of Lots t
Dam Safety Regulations (Washington State Department of Ecology)
Reservoir Volume above natural grade -1y 719 1 el
Depth of Reservoir above natural grade
Facility Summary Sheet Sketch
All detention, infiltration and water quality facilities must include a detailed sketch-
(11
ketch_(11 "x17" reduced size plan sheets may be used)
2005 Surface Water Design Manual 111105
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
Water Quality-
Type/Number of water quality facilitiesBMPs:
biofiltration swale
(regular/wet/ or continuous inflow)
_J_ _ combined detention/wetpond
(wetpond portio basic or large)
combined detention/wetvault
filter strip
flow dispersion
farm management plan
landscape management plan
oil/water separator
(baffle or coalescing plate)
sand filter (basic or large)
sand filter, linear (basic or large)
sand filter vault (basic or large)
sand bed depth (inches)
stormwater wetland
storm filter
wetpond (basic or large)
wetvault
Is facility Lined?
If so, what marker is used above
Liner?
. catch basin inserts: Manufacturers
pre -settling pond
pre -settling structure: Manufacturer
high flow bypass structure (e.g., flow -splitter catch basin)
source controls
Design Information
Water Quality design flow
Water Quality treated volume (sandfilter)
Water Quality storage volume (wetpool) -26,103 Crr
If
Facility Summary Sheet Sketch
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x17" reduced size plan sheets may be used)
111105 2005 Surface Water Design Manual
2
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APPENDIX G
GEOTECH REPORT
Date
To
From
Subject
Project
Subdivision
Permit 0
Owner
Location
Lots
Sensitive Areas:
SCS Soil Class.:
Zoning .
Size
RRIpose
Geo Trendsflnc-
Mar. 20, 2004
Rink Boston
Boston Design & Development, LLC
13425 E. Lake Kathleen Dr. SE
Renton, WA 98059
Steve Pappajobn, Geologist
Geotech Report
Sons Creek Plat
AA03P0296
N.A.
Boston Design & Development, LLCWM (see attached ma
SE SW Sec. 33, Twp. 23N, Rng. 5E,
1-32 see attached lat
Erosion Hazard (King County Map Folio, Dee. 1990 -see attached maR)
Alderwood (AgD) — SCS King Co., Nov. 1973 see attached ma
King County R6
6.2 acres.
The purpose of this report is to characterize certain geotechnical aspects
property especially in respect to slopes stability and soil permeability. An erosion
possible based on the available reference.
of the above -captioned
hazard is indicated as
Summa
2043. The
A site visit was made to the I natural anerty and d exijoining properties on December 3
sting conditions of the property to make
purpose of the visit was to inspect
observations regarding soil profiles, ground water conductivity, slope stability and other salient factors e
location and suitability of building sites. Existing topographical information was also used in the
characterization_ D, property, to Cher important
Research and interviews were conducted to dbto detterhistory
t� �� of
srof a�salient aspects of the
information about previous activity on the property,
property that may effect its development. Preliminary site plans were also reviewed.
From surface conditions, local geology, and observations from adjacent developed and undeveloped
' soil areas, foirecords. CharacteristicAlderwood
Wil conditions appear to be consistent with mapped _iA are
associations consisting .of wooded upuents confirm tnd terraces and lopes, composed of erraaes of less than 6°acial grade to laterally areas of up
continuous and consistent. Slope meas
to 28% grade. All areas contained characteristic stable surface conditions with no evidence of sliding, mass
wasting, or creep.see attached to o ma
No evidence of water -bearing or —directing horizons (springs) was observed at the surface or along
the slope. Characteristic Douglas fir -Alder forest, with typical fern and scrub understory prevails on and
adjacent to the parcel. The Soos Creek drainage is to the east of the eastern boundary of the property.
Gealo
Vashon glacial till deposits and post -glacial stratified terrace drift dominate surface geology at the
site_ soils in this region consist mostly of well -sorted sandy and gravelly loam above a substratum of
compacted till designated as Alderwood Soils in this portion of King County. In the Puget Soured regin,
o
deposits of this type
are thought to have occurred at, and proximal to, the retreating front of the Puget glacial
lobe by large ice -marginal melt -water streams during the most recent ice -age.
GeoTrenasginc.
Infiltration Tes
tests
� detexmine etre
Throe (3) test °g-1, 2, ) were ahoser► for for water in *e am where
damurimm on itre east side of the prop° led in depth from 3.5, tog 0 fed deep and
� -�' on faalft a �°- IU � y welt drained and °11� in all
were each 24r wide (� l)' 302003 and or► March 3 2004 to
Tests were conducted on Dmemb� uuy aid
pits, sm soil 1profil&
&Nft Jan
encs : c
s+as'M The pets +'"�ans during fdt p. and �c�old and vM wet with the
Febnwry showed tdueo of heavy ram (and snow to Dw mba) uP to the
sons in gesweral ..
day of test. T� holes were
County Falling Head Pea�tf� Test � ii with �4
Tests were ooh � ICang ��� to be designed. Due m �Y
probable of Qn was not dome but maple tests verified a consist Mt g"
CIO, and theme t W �U 9l1 , a wft ba �P). p�"W'on
result. Ttro�i
frown the bottom of the pit and refilled as ed ft Y
rate, noted as follows wass aft., a stabilised cwjMnt rate owed"
Falling Head Percolation Test Results (minutesrmh)
Amately 373 ele°vatim
i 1.
nm water table elevadw M dais low area of the site to � °� #4 (O=Miwwal short
over the 2 month wet p�
.� was baud On dation of several pits at ale v 374} and #7 (standing water' at
duration water at eiev 373N #5 (PO wat all saline lies at apP�d y the 37x4 elevation tine.
37 S. and natmg that the wct� delineefion litre
S oe
Bottom
tion nate
Pit Locatiowt
-10
EiCvat+�un
Tlev><tioa
min /inch
#i Ceram, 260''e of
4.0 fat
�
4p2
.0
eatline
175
3.5 feet
-3
7_i min I inch
#2 5E carne',
of east line
376.5
8.0 min 1 inch
#3 130 fed West9S
fact
of ems liwwe
S_4 mim 1 inch
Amately 373 ele°vatim
i 1.
nm water table elevadw M dais low area of the site to � °� #4 (O=Miwwal short
over the 2 month wet p�
.� was baud On dation of several pits at ale v 374} and #7 (standing water' at
duration water at eiev 373N #5 (PO wat all saline lies at apP�d y the 37x4 elevation tine.
37 S. and natmg that the wct� delineefion litre
Geo TrenilSox �
Laud Ade and sbM FAoes
sl es via on site visual inson and analysis of the topo$mp�c
The site was reviewed for steep � Evag� kion. Seuvcyin&
nt
caams (at 2' iac cnt s) =WW by
lateau at '
Tteis site basan en roll stop ,to f r (1001/612'). The weaern edge Upper P
awer valley flat gree is 7.3% ( �'� a"d e
elevation 476 is about 4% (4 f tQE) }, 44f 1- a 5y. (3 MG,) siopc- The min
two ed g� above
beech in the at e 430xs ro ' as #cF bwasiid-
and below the bewh are Mud* 20 to 25 % slaps thus Fcgwcons j s
tm8
Landslide is as meas ovar ISVO, wised of stilt � � � off
f= ares revealed that saw an slopes
� � � vys�er. Test pits Of slides vrrece noted anywb� � the site. Itis
saredlr loaxrt over a dem glacial til[. No indica#xat� � kcating failings on ti» solid bay. Also
r�reneereded Haat fad � tleru tLe sal at the glacier! full level, tbes it is
�� waters lin at the Up of" site (western edge) such that offsite
me ded first this surfim water Llt� site. Vieththese reonenmarAab`ons
age (which flows or>to the sits)
cia be routed to byposs implemcat d, flora is no jjWflenud of landsrdes_
on tia3
-Steep aloW, duetted as ificH s over 40% � � M tecp s� "e that these
topographic ,Nota shad B, naftrW but were mmud by man
range betweeea 10 and 20 fbt in toes[ rise. Nate else dart these are not level the tower valley and rooter' l h for homes
made carts (likay evade in the 1970s or la3WAO
and yard arcs).
�'Ls are sable WA rise ter 20 fed vefU�Y- Thm a
Cade allows fot' An exem s� was . As per the sails portion of fiefs report the
related to arability
carafiai revievr �tl� B��X was. Review was made of
dying glacial tx"il is very stable and wall drams in 1pc�e a cuts. Nnba also dot these
� v�tioee, and size and. suraw"Iess of the trees; er indicated less tl:sse 369�a
as IAOW. Mess MMM* with the ireclineYnxet are barely 40% over
slopa am oray � of the to xeup, indicated some select areas lit
p°� affect wsfl occur � t�
10 foot rise (noes steeper. 'fb� the cmwbx Wu is that ere: sdverae
tlae areas from setback rerlairev"la ff regvbvd.
'' ed site plan (lot lay") and
This ccxtoWon is further s� by c�reVCr cad fixe proposed were
corstruetise p as by the tlevewper- code, �S pied if these
formed due to mar► made gmdin& they vvoe. with sliglrt rergra�n8 � will be red:►raxl to
-In seas A and C � the slope � is l 2 to 14 fad,fpr daylight
daylight -non slope'; it is n�ri that the site plan (lot layout} ' s d
es�homes =ffigared for this.led with the slope cut of area A it
*Area B is not in itself "stomp sib" in is 20%) but when il�el by ze
so and. � a rise of 20 fed. When this Iowa area A is re.gradc d 0 Y
fining the old excavation) tM bringing the A + B ovaull slope to 32% it is no IOnW a "MecP
slope" classification- to 1etaincd as OrCO
the
D sorathern slope rise is l C fed. T is end the rise is 12 feet- This
exegion forem seek slsatrid be aped here. At the rrtomes ellpmutatin8 flee "
is to be re-� sUo* a A to
1� for the �
slope" classification in this am&
Geo Tffrends,.�
Refe-- — K �, � ^ 1965' � Geoiagic Survey
Gealogie MBP Of the Rfawn � ai 'y � ° 5cr►ice
Sail Survey, King �` A:e� 1iV��'' 1933, �+ e�l�l � $uiL 78
g W� Wn Wl�� S� Water' Supply Paper 1352
Waw R� � , IVa - Naslaan ternbe r 1990
Ki ng GountY Sensitive .Areas tee 9614, King County,
itkm aad
ll' }'aIbisrepmt m t� is � solely W tokoe f orals and
and is for use Only by qualifiedOpinions,
other ripe of the sedi p�Y is t be � a M snm � nduags,
officials- Any nth
or r� a-e,3Oi�"s, mad on the l
�est
judgme�ms and � i� in this �ly � +esra�I #�maices,
information available as � in the &K as � VwYmftc� pre w the nature Of
and as reviewed by OtlVWqwate untwwPVthLable,
iinvesti:Me
and tl�eor od=-wise
l ,, aondMoas
wed �iftOM ea f� >�, ori;. 'r 6wdif� of � �. !iift muy cW= Qrei xp °r
lterem.a Orsi � .t arebeyond �te of this �• -No�3' of =Y
randite
implied, is included herein.
Sincerely,
!80111 ..AYE.. f+
I~a. ST � AY IS1-
z2�i11 84TH
1 iAA
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SOIL ASSOCIATIONS Sans
Alderwaod association- Moderately well drained, undulating to hilly Solis
that have dense, very slowly permeable glacial till at a depth of 20 to 40 Creek
inches; on uplands and terraces
Oridia-Seattle-Woodinville associPtion: Somewhat poorly drained and very
poorly drained, nearly level sails; in major stream valleys
Buckley-Alderwood association- Poorly drained and moderately well drained,
iffy,; nearly level to rolling soils that have dense, slowly permeable and very
r% ;, slowly permeable glacial till at a depth of 20 to 40 inches; on glacial. till
plains and uplands
Everett association: Somewhat excessive)y drained, gravelly, gently un-
dulating soils underlain by sand and gravel; on terraces
Beausite-Aldefwood association: Well drainednd moderate`y welfidrained,
gently roiling to very steep sons that have sandstone - shake or dg ,
very slowly permeable glacial till at a depth of'20 to 40 inches; on uplands
Alderwood-Kitsap-Indianola association: Moderately well drained, nearly
level to steep soils that have very slowly permeable glacial till or glacial
lake deposits at a depth of 16 to 44 inches, and sornewhat excessively
drained; rolling, deep sandy soils; on uplands and terraces
�..; Puget-Earlmont-Snohomish association: Poorly drained and somewhat
poar�y drained nearly level soils that have layers of peat within a low
feet of the suflace; in major stream valleys
i
I£lFiC COUNTY, WASHING' 0pq, SURFACE WATER DESIGN MANUAL
FERE�� E
FALLING HEAD pERCOLATION TEST : PROCEDURE
Source: EPA, owite wastewater Tint and Disposal Systems, 1.980_
Number and Locatltln of Tests
A minimum of three Nests shall be performed wit1� the area prnpa� an domption systc�
'They shall be sped u niformly throiighOut ft area Ff soil tlitzans are highly viable, rn€rre
tests may be required.
Preparation of Test Hole
The diameter of each test hale is 6 inches, dug or bored to the proposed depths of the absorption
to the most limiEting soil horizon. To expose a natural soil surface; the sides of the rola
systems or rial is removed from the bottom
Y are scratched with a sharp pointed instrrtxr�ett arRd 1 ho% to Protea
battrrm from
of the test hole. Two inches Of 'h- to Winch rack arc FI
a=d in the scouring when the crater is added -
Soaking Peried
•hole is carefully filled with at least 1 Inches of clear wales-. The depth oft. d er shouW be
funnel with referabl overnight if clay sells arep
maintained for at least 4 hours anal preferably
Y vent wales from washing down the sides of the
attached hose or similar device may be used to I automatically maintain the water
hole. Auto nano siphons or float valves
may be emP that the soil be showed to soak for a
level during the soaking period- it is extreenmly important
sufficiently long prod of time to allow the soil to swell if accurate results are to be obtained.
In sandy soils with little or no clay, soaking is not necessary. if, after filling the hole twice with 1�
inches of water, the water seeps completely away in less than ten minutes, the test can Proceed
immediately.
91
19;8 sut'face Wata D*5
i� Y.vtra HlTr�ti ?E�t, SURFACE WATER DESIGN MANUAL
KIN U
Measurement of the percolatioti Rate
ts are made l� hartrs but no t1� 30
Exempt for sandy sails, peaIation rate co dxc tale dtng €#� gg
hers after the � pertud �- 'may sod. that sIOUgIledi.nche
period is removed and the water level : adjusted
to 5 inches above the gravel (or S incYies above
the bottom of the hole). At no time during the test is the water Ievel allowed to ase more than G
inches above the gravel,
mediately after adjt;sttxtcnt, the water level is measured from reference
ccessivewater le
rwapoint
vel
nearest 1llb�' inch at 3D-mir to intafc. The test is continueduntil
gra s
drops do not vary by more titan U16 inch with a Wqninuft Period-
After h ttrerr=nt, ft water level is readjusted to the 6 level dro
-inch level. The last water p
is used to calculate the percolation rete.
In sandy sods or sobs in which tt fuer &ice' of waw' added .after the sig � RFs away
in less than 34 minute, w level are madam .at 1!1<-rn..ta iateals fora 1-lrcrtr
period. The last water level drop is used to calculate the percolation rate.
Caladaflon of the PemlaUQn Rate
test hole b dividing the time ipwvai used between
The ger olatian r is calculated
for
each �' This akalation results in a
mearemen, magttitu� of
the last water level dr°F- anon rate for the area, the rates
percaiation rate in. tarts of minotesf�h f t �� � P�
tests in � area vary by mom bran 2{i rninut3esli.nch,
obtal,d frorn each hole = &Mair nation rates should not be
variations in soil type are i�scated. Under these circzm�st�s, Pe
3Yeraged.)
Example:, if the last measured drop iu water level after 30 rninutes is 518 -inch, then:
Percolationrate = (30nr,tes!(19 inch
) = 48 minutesTinch.
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From: Bill Taylor, P -E.
To: City of Renton
Attn: Rocale Timmons
Date:
November 2, 2012
Project:
Fleuve des Voiles & Cogger Plats
Parcel Nos.:
6199000240, 6199000260,
TEC Proj.:
294-JMA & 341 -CSC
Topic:
Minor Revision to Preliminary Plats
TIR ADDENDUM
Ni'i' ' R irJi/
This addendum amends and updates the TIR prepared for the Fleuve des Voile and Cogger
preliminary plats, as approved by King County in 2007.
The approved 2007 preliminary plat included a looped road. This minor modification revises the
road layout to a cul-de-sac at the northwest corner of the plat, with enhanced traffic flow
through the middle of the plat and continuing to a connection with the proposed Wehrman Plat
to the north.
This revision is proposed in order to reduce the earthwork quantities and land disturbance, as
well as the proposed impervious surface area.
Including necessary off-site improvements, the original layout included approximately 6,41
acres of impervious surfaces as shown on page 10 of the TIR. The proposed minor revision
includes only 6.27 acres of impervious surfaces. The net difference is a reduction of 0.14 acres
of impervious surface for this minor revision.
The drainage design is vested under the 2007 King County approval, and since this proposed
minor revision reduces the impervious surface area, the existing detention volume is now
conservative under the vested code. The hydraulic analysis can be updated during final plat
engineering review to optimize the detention system performance.
485 Rainier Blvd N, Ste. 102 . PO Box 1787 • Issaquah, wA 98027 • tel. (425) 391-1415 + fax (425) 391-1551 a www.teccivil.com
ATTACHMENT A
PROPOSED MINOR REVISION PLAT LAYOUT
EXISTING (SF): PROPOSED SF).
SITE SITE
BUILDING: 295 (0.01 AC)
PAVEMENT: 1,516 (0.03 AC)
FOREST: 316,831 (7.27 AC)_
SUBTOTAL: 318,347 (7.31 AC)
124TH AVE SE
PAVEMENT: 7,064 (0.16 AC)
PASTURE: 4,749 (0.11 AC)
FOREST: 3.329 (0.08 AC)
SUBTOTAL: 15,142 (0.35 AC)
TOTAL: 333,459 (7.66 AC)
BUILDINGS: 147,655 (3.39 AC)
PAVEMENT: 58,423 (1.34 AC)
SIDEWALK: 6,523 (0.15 AC)
POND: 10,395 (0.24 AC)
LANDSCAPE: 95,351 (2.19 AC)
SUBTOTAL: 318,347 (7.31 AC)
BY-PASS (124TH AVE SE)
PAVEMENT:12,681 (0.29 AC)
SIDEALK: 2.461 (0,06 AC)
SUBTOTAL: 15,142 (0.35 AC)
TOTAL: 333,489 (7.661 AC)
0 75 150
"�mi
SCALE: 1" = 150 ft.
OFF-SITE TRIB. AREA (SF):
IMPERVIOUS: 45,006 (1,03 AC)
PASTURE: 205,029 (4,71 AC)
FOREST: 41.517 (0.96 AC)
TOTAL: 291,852 (6.70 AC)
MENNEN Irl
��E��V�T-1
� moo■ �r r �
i [, ��.a •
TECHNICAL INFORMATION REPORT
for
Fleuve des Voiles Plat and Cogger Short Plat
King County Tax Parcel Nos.
619900-0240, -0241, & -0260
Subdivision File # A03PO286
LSUD File # L04P0002, L06VO040 (Fleuve des Voiles)
LSUD File # L05SO040 (Cogger)
TEC Project No. 294-JMA
Site Addresses:
19100124 th Avenue SE
12216 SE 192 d Street
Renton, Washington
o� ° � �D
FIT /I V
IST
S NAL
Prepared by: Lorna M. Taylor, P.E.
Date: July 8, 2008
Revised: March 18, 2009
205 Front St. S 1 P.O. Box 1787 • tssaquah, WA 98027-0073 6 tel, (425) 391-1415 • fax (425) 391-1551 • www.teccivil.com
Technical Information Report
Fleuve des Volles Plat & Cogger Short Plat
TABLE OF CONTENTS
Section
Description
Page Number
1.
Project Overview ......................... ..............
1
2.
Conditions and Requirements Summary...........
1
3.
Off -Site Analysis ..........................................
8
4.
Flow Control and Water Quality Facility Analysis
Appendix C:
Analysis and Design
andDesign ....................................................
9
5.
Conveyance System Analysis and Design........
11
6,
Special Reports and Studies .........................
11
7.
Other Permits ..............
8.
ESC Analysis and Design .............................
12
9.
Bond Quantities, Facility Summaries, and
Appendix G:
Geotech Report
Declaration of Covenant...... ........................
12
10.
Operations and Maintenance Manual ...............
12
Appendices
Appendix A: Figures
TEC
1. Technical Information Report (TIR) Worksheets
2. Site Location
3. Drainage Basins, Subbasins, & Site Characteristics
4. NRSC Soils Map
Appendix B:
Off-site Analysis Drainage System Table and Map
Appendix B-1:
Drainage Complaint Analysis (includes previously submitted
documents & updates)
Appendix C:
Analysis and Design
Appendix C-1:
Detention Facilities Design
Appendix C-2:
Treatment Facilities Design
Appendix C-3:
Erosion Control Facilities Design
Appendix C-4:
Conveyance Facilities Design
Appendix D:
Maintenance Requirements for Privately Maintained Drainage
Facilities
Appendix E:
Bond Quantities Worksheets
Appendix F:
Retention/Detention Facility Summary Sheet and Sketch
Appendix G:
Geotech Report
TEC
Technical Information Report
Fleuve des Voiles Plat & Cogger Short Plat
SECTION 1
PROJECT OVERVIEW
The 6.74 -acre Fleuve des Voiles project site and the 0.93 -acre Cogger project site comprise 3
existing lots and are located at 19100 124th Avenue SE and 12216 SE 192"d Street in Renton,
Washington. The Fleuve des Voiles project proposes to subdivide two lots into 39 residential
lots, and the Cogger project proposes to subdivide the third lot into 8 lots, providing the required
infrastructure, including access roads, water and sanitary sewer service, storm runoff collection,
conveyance, detention and treatment, and erosion control for each plat during construction.
This Technical Information Report is submitted to the King County DDES in accordance with
the King County Surface Water Design Manual (KCSWDM). It addresses stormwater runoff
from both the Fleuve des Voiles Plat and the Cogger Short Plat. A "Level 1 Technical Design
and Information Report for Preliminary Plat Review", dated January 26, 2004, was previously
submitted for the Fleuve des Voiles site under the title "Soos Creek Plat"; and portions of that
previous report are referenced herein; however, the proposed plat has been significantly
changed and this TIR addresses the currently -proposed plat layout for both the Fleuve des
Voiles plat and the Cogger Short Plat.
The Fleuve des Voiles plat was re -submitted as the "Soos Creek Plat" on September 15, 2004
and is subject to full compliance with the 1998 KDSWDM. Since that time, the plat layout has
been modified somewhat and the drainage facilities re -sized to accommodate the revised layout
and additional runoff from the adjacent Cogger Short Plat, which is subject to full compliance
with the 2005 KCSWDM. This TIR addresses the development of both plat areas and the
requirements of each version of the manual or approved adjustments. A Surface Water Design
Manual Requirements/Standards Adjustment Request has been prepared addressing standard
adjustments to Core Requirements #1 and #3.
Appendix A contains a Technical Information Report (TIR) worksheet for the projects (Figure 1),
as well as a Site Location Map (Figure 2), Drainage Basins, Subbasins, and Site Characteristics
figures (Figure 3a — 3e), and a Soils map (Figure 4). More detailed site information is included
in Appendix C with the existing and developed site runoff model data.
SECTION 2
CONDITIONS AND REQUIREMENTS SUMMARY
Following is the text of the King County Hearing Examiner's Preliminary Conditions of Approval,
dated January 12, 2007. All of the conditions 1 -- 21 either have been addressed, or will be
addressed for the project,
1. Compliance with all platting provisions of Title 19A of the King County Code.
2. All persons having an ownership interest in the subject property shall sign on the face of the final plat a
dedication that includes the language set forth in King County Council Motion No. 5952.
3. The plat shall comply with the base density and minimum density requirements of the R-6 zone
classification. All lots shall meet the minimum dimensional requirements of the R-6 zone classification
or shall be shown on the face of the approved preliminary plat, whichever is larger, except that minor
revisions to the plat which do not result in substantial changes may be approved at the discretion of the
Department of Development and Environment Services.
Any/all plat boundary discrepancy shall be resolved to the satisfaction of DDES prior to the submittal of
the final plat documents. As used in this condition, discrepancy' is a boundary hiatus, an overlapping
boundary or a physical appurtenance which indicates an encroachment, lines of possession or a
conflict of title.
4. All construction and upgrading of public and private roads shall be done in accordance with the King
County Road Standards established and adopted by Ordinance No. 11187, as amended (1993 KCRS).
TEC
Technical Information Report
Fleuve des Voiles Plat & Cogger Short Plat
disperse detained runoff, which should adequately mimic existing conditions, in
accordance with Drainage Adjustment L06VO040 which recognizes that it is
impossible to retain the existing sheet flow discharge condition along the entire east
property line and still comply with Core Requirement #3, Flow Control and Core
Requirement #8, Water Quality. Additionally, the proposed scenario is preferable
because strict compliance with Core Requirement #1 would result in discharge to the
neighboring backyards creating an unacceptable situation for the adjacent property
owners, and would require dispersion of runoff onto the adjacent King County Parks
Department property, which is also not acceptable to the parks department.
2. Off -Site Analysis: A Level 1 offsite analysis was conducted for these plats as described
in Section 3.
3. Flow Control: Runoff from both sites will be controlled to meet the requirements of the
1998 KCSWDM for the Fleuve des Voiles Plat and the 2005 KCSWDM for the Cogger
Short Plat in a single combination detention and treatment pond. This Shared Facility
Plan has been approved (FN L06V0040). Discharges from the facility will be to a
dispersion/energy dissipation facility. The detention facility will also over -detain runoff
to mitigate for the undetained ru l off from the 1241h Avenue SE roadway to the east of
the project site.
Level 1 detention criteria stipulat din the 1998 KCSWDM is proposed for the entire
Fleuve des Voiles site because t e project proposes to tightline all runoff from the upper
hillside down the base of the hill in the level 1 detention area. This has been approved
based on previously established interpretation and policy. The Cogger Short Plat
detention sizing meets the Conservation Flow Control requirements of the 2005
KCSWDM. Appendix C-1 contains the KCRTS input and output.
4, Conveyance System: Pipe conveyance modeling shows that the proposed 12 -inch
storm drain system will be sufficient to convey the 100 -year storm runoff without
flooding. See Section 5.
5. Erosion and Sedimentation Control: Runoff from the grading and trenching
construction areas will be contained by a temporary construction entrance, silt fencing
and a sediment pond in accordance with the KCSWDM during construction. The ESC
facilities will only be removed once all exposed site surfaces have been stabilized.
Other temporary erosion and sedimentation control measures will be installed as
needed. See Section 8.
6. Maintenance and Operations: Until King County assumes responsibility for their
maintenance, the combination detention and treatment pond and cartridge filter
treatment catch basins should be maintained as described in Section 10 and Appendix
D, which includes the KCSWM Maintenance Requirements for Privately Maintained
Drainage Facilities.
7. Financial Guarantees and Liability. See Section 9. The bond quantities worksheet is
included in Appendix E.
8. Water Quality: Treatment of runoff from the 124th Avenue SE roadway will be provided
in two cartridge filter treatment catch basins and the runoff from the remainder of the
site will treated in the dead storage portion of the combination detention and treatment
pond, which was sized according to the KCSWDM for Basic Water Quality Treatment,
Appendix C-2 contains the calculations used to size the treatment facilities.
Special Requirements
1. Other Adopted Area -Specific Requirements:
TEC
Technical Information Report
Fleuve des Voiles Plat & Cogger Short Plat
Shared Facility Drainage Plans (SFDPs): These two projects propose to provide
detention and treatment in a common facility located in the Fleuve des Voiles plat. The
facility sizing took into account the differences in drainage manual requirements for the
two projects. The Fleuve des Voiles project is vested under the 1998 Manual, and the
Cogger Short Plat must comply with the requirements of the 2005 Manual.
In addition, the Fleuve des Voiles site contains both Level 1 and Level 2 Flow Control
areas per the KCSWDM; however, the area designated Level 2 is located within the
steep slope designation. Since the project proposes to convey onsite runoff to the base
of the hill and the Level 1 area, Level 1 Flow Control is proposed for Fleuve des Voiles.
The detention facility is located at the base of the hill and will discharge via dispersion to
a Level 1 Flow Control area. Appendix A contains King County mapping to support this.
2. Floodplain/Floodway Delineation: Not Applicable. The 100 -year floodplain for the
adjacent Soos Creek wetlands does not extend onto the subject property.
3. Flood Protection Facilities: Not Applicable.
4. Source Controls: Not Applicable.
5. Oil Control: Not Applicable.
SECTION 3
OFF-SITE ANALYSIS
The downstream drainage path was documented, King County's IMAP database was consulted,
and the County's Drainage Complaints File was again solicited to make sure no additional
pertinent drainage complaints have been lodged since the original Drainage Complaint
Analysis, dated March 20, 2004, which was produced for the project by Jacques Consulting,
Task 1. Study Area Definition and Maps
The figures in Appendix B show the extent of the study area and the local topography. The first
figure shows that the project site constitutes less than 15 percent of the area tributary to the
point '/ mile downstream from the site; therefore, a % mile downstream analysis is deemed
sufficient. The Site Plan drawings show more detailed topographic information on the project
site.
Task 2. Resource Review
Agency mapping was reviewed and TEC contacted King County regarding documented
drainage complaints in the vicinity. The NRSC soils map identifies site soils in the proposed
development area as Alderwood Gravelly Sandy Loam, 0 — 6% slopes and 15 — 30% slopes.
Task 3. Field Inspection
In accordance with the KCSWDM, the existing site and off-site drainage systems were
inspected on June 15, 2004, and several times since.
Task 4. Drainage System Descriptions and Problem Descriptions
There is only one pertinent report of a drainage problem in the immediate vicinity of the project.
This complaint involved a plugged driveway culvert across 124th Avenue SE at SE 192`,4, and
the problem has been corrected according to the previously submitted Drainage Complaint
Analysis by Jacques Consulting, dated March 20, 2004 (see Appendix B-1). The County's
drainage complaints file was solicited again more recently, and the results of this search are
included in Appendix B. No additional pertinent drainage complaints have been logged in the
interim.
TEC
Technical Information Report
Fleuve des Voiles Plat & Cogger Short Plat
If the proposed drainage system fails, and the detention facility floods, the emergency overflow
path for runoff would be into the adjacent Soos Creek wetlands. These wetlands feed Soos
Creek, which flows south on the King County -owned property to the east of the project property.
Task S. Mitigation of Existing or Potential Problems
To mitigate any water quantity impacts from the project, detention of runoff is proposed meeting
Level 1 and Level 2 flow control requirements for Fleuve des Voiles and Cogger, respectively, in
accordance with the King County Surface Water Design Manual (KCSWDM) and the approved
Standards Adjustment (1-06V0040).
Water quality impacts will be addressed in two Basic Water Quality treatment facilities; a
combination detention and treatment pond and two cartridge filter treatment catch basins. The
pond will treat runoff from the site, and the cartridge filters will treat runoff from 124' Avenue
SE.
The culvert that was documented as plugging in the County Drainage Complaints file will be
replaced in the course of this project.
SECTION 4
FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
The following subsections describe the measurements and criteria used to size the detention
and treatment facilities.
Existing Site Hydrology (Part A)
The drainage on the existing site was analyzed for this project with KCRTS. Figures provided
in the KCSWDM and KCRTS manual were used to determine project location and scale factor
parameters. The figures in Appendix C-1 show the delineation of the areas generating runoff
on the site. The site soils are classified Alderwood Gravelly Sandy Loam, either 0 - 6% or 15 —
30% slopes. Appendix C-1 also contains the data and output from the existing site hydrologic
analysis.
The existing site conditions identified for this project and used in the KCRTS modeling are
summarized below.
Existing Site Conditions used for Hydrologic Modeling
(areas in acres)
Fleuve des Voiles
Cogger
Site Offsite 124th
Site Offsite
Total
Impervious
0.04 0.71 0.16
0.00 0.32
1.23
Pasture
0.00 3.23 0.11
0.00 1.48
4.82
Forest
6.02 0.96 0.08
1.25 0.00
8.31
Subtotal
6.06 4.90 0.35
1.25 1.80
14.36
Developed Site Hydrology (Part B)
The proposed drainage systems will route "site" runoff to a detention pond which will discharge
to a dispersion/energy dissipation facility draining to the adjacent Soos Creek wetlands. Runoff
from 124t' Avenue SE will be controlled as over -detention in the pond and will flow directly to
TEC
Technical Information Report
Fleuve des Voiles Plat & Cogger Short Plat
treatment catch basins prior to discharge to the Soos Creek culvert crossing of SE 192nd Street.
Appendix C-1 contains the data and output from the developed site hydrologic analysis.
The developed site conditions identified for this project and used in the KCRTS modeling are
summarized below,
Developed Site Conditions used for Hydrologic Modeling
(areas in acres)
Fleuve des Voiles
Cogger
Site Offsite I24th
Site Offsite
Total
Impervious
4.22 0.71 0.35
0.81 0.32
6.41
Landscaping
1.84 0.00 0.00
0.44 0.00
2.28
Pasture
0.00 3.23 0.00
0.00 1.48
4.71
Forest
0.00 0.96 0.00
0.00 0.00
0.96
Subtotal
6.06 4.90 0.35
1.25 1.80
1 14.36
Performance Standards (Part C)
The Fleuve des Voiles project is subject to the requirements of the 1998 KCSWDM and
contains both Level 1 and Level 2 Flow Control areas, however the detention facility is located
at the base of the hill and will discharge (via dispersion) to a Level 1 Flow Control area_ The
area designated Level 2 is located within the steep slope designation. Since the project
proposes to pipe all site runoff to the base of the hill and the Level 1 area, Level 1 Flow Control
is proposed for Fleuve des Voiles.
The Cogger project is subject to the requirements of the 2005 KCSWDM, and is subject to
Conservation Flow Control requirements and must meet Historic Site Conditions Level 2 flow
control standards.
Basic water quality treatment is required for both the Fleuve des Voiles Plat and the Cogger
Short Plat project.
Conveyance features must be sized to convey the 25 -year developed runoff and their
performance during the 100 -year event should be checked to be sure that significant flooding
would not occur as a result.
Flow Control System (Part D)
The flow control is provided in a single detention pond, which may look like two separate ponds;
however, the twin 24 -inch diameter culverts crossing SE 191st Street are part of the pond and
serve to connect the two sides. For design purposes, the detention pond volume was
calculated as two different ponds (one level 1 and one Level 2), which were then combined into
a single facility with a stage -storage -discharge relationship that matches the combined stage -
storage -discharges of the two ponds that were sized using the Level 1 and Level 2 detention
criteria in the KCRTS routine. The following table summarizes the sizing requirements for the
Level 1 and Level 2 detention ponds.
10 TEC
Technical Information Report
Fleuve des Voiles Plat & Cogger Short Plat
Detention Pond Req'ments
Fleuve des Voiles
Cogger
Total
Required storage volume
43,751 cf
13,133 cf
56,884 cf
Effective storage depth
4.5 ft
4.5 ft
4.5 ft
Top area @ 1' freeboard
14,307 sf
5,500 sf
19,807 sf
Bottom area
6,891 sf
1,474 sf
8,365 sf
Orifice #1 diameter"
3.02" (3")
1.25" (1-114")
3.27" (31114")
Orifice #2 diameter
2.71" (2-11116")
1.80" (1-314")
Orifice #2 height
3.38 ft
3.10 ft
"An equivalent 3.27" (3-114") single orifice will be used in place of the two bottom orifices.
A 20 percent factor of safety increases the required detention volume to 68,261 cubic feet. As
shown on the plans, the pond will provide 68,449 cubic feet of detention storage. In this
instance, the need for a factor of safety is not very great, because the downstream drainage
system is a large stream and wetland system that will likely absorb any overflow situation that
might occur in the pond, with minimal chance for damage to downstream properties.
Descriptions of the procedures used and calculations and computer output are included in
Appendix C-1. .
Water Quality (Part E)
Runoff from the site will be treated in the dead storage portion of the combination detention and
treatment facility, which was sized for Basic Water Quality Control. Runoff from 124th Avenue
SE will be treated in two cartridge filter treatment catch basins. The following table summarizes
the sizing requirements for the treatment pond.
Treatment Facilities Site Pond 124'' Ave. SE Filters
Required wetpool volume NO 26,103 cf
Wetpool depth 4 ft
Top area 8,056 sf
Qwn _ 0.05 cfslCB
As shown on the plans, the pond will provide 31,453 cubic feet of treatment volume. The
detention/treatment pond has more than a 5:1 length -to -width ratio, and so does not require a
berm; however, the roadway embankment will effectively create a berm and further increase
residence time and encourage sediment to settle in the upstream (south) pond area.
Descriptions of the procedures used and calculations and computer output are included in
Appendix C-2.
SECTION 5
CONVEYANCE SYSTEM ANALYSIS AND DESIGN
The County's backwater routine (KCBW) was used to size conveyance piping. The proposed
12 -inch diameter pipe system will convey the predicted 100 -year peak flows without flooding.
Documentation of the conveyance sizing is included in Appendix C-4.
SECTION 6
SPECIAL REPORTS AND STUDIES
Several studies and reports were conducted and produced for this project and are either
available under separate cover or included in an appendix, as listed below.
11 TEC
Technical Information Report
Fleuve des Voiles Plat & Cogger Short Plat
1. Wetland Evaluation and Delineation Report prepared by H & S Consulting, dated May
13, 2004. Available under separate cover.
2. Traffic Impact Analysis prepared by William Popp Associates, "Draft" dated May 27,
2004. Available under separate cover.
3. Geotech Report prepared by GeoTrends, Inc., dated March 20, 2004. Included in
Appendix G.
4. Conceptual Buffer Mitigation Plan prepared by AC Roth Environmental Services, dated
March 20, 2006. Available under separate cover.
5. Level 1 Technical Design and Information Report for Preliminary Plat Review prepared
by Jacques Consulting, dated January 26, 2004. Available under separate cover.
SECTION 7
OTHER PERMITS
No other permits beyond those required by King County are anticipated to be required for this
project.
SECTION 8
ESC ANALYSIS AND DESIGN
The project proposes to utilize the north portion of the permanent pond location for temporary
sediment retention. The permanent pond area is 12,348 square feet, which is more than
double the 6,158 square feet required for the erosion control pond.
Runoff from the construction site will be collected and conveyed in interceptor swales located
throughout the site. These swales will convey runoff to temporary pipe drains leading to the
ESC pond. The interceptor swales and pipe drains were sized from 8 -inch to 18 -inch diameter
using King County's Backwater Analysis routing to convey the 10 -year, 15 -minute runoff from
the developed site without flooding and with 6 inches of freeboard.
The sizing calculations for the various elements included in the erosion control facilities are
included in Appendix C-3,
SECTION 9
BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
Bond Quantities: The County's standard Bond Quantities Worksheet is included in Appendix E.
Facility Summaries: The County's Facilities Summary Sheet is included in Appendix F.
Declaration of Covenant: Not applicable. All the drainage facilities are located in public rights-
of-way, or dedicated drainage tracts, and will be maintained by the County two years after final
construction approval.
SECTION 10
OPERATIONS AND MAINTENANCE MANUAL
The detention/treatment pond and all drainage and street work within public tracts and rights -of -
ways will become the property of and will be maintained by King County two years after final
construction approval. Until such time, the drainage facilities should be maintained as
described in Appendix D (part of which was excerpted from the KCSWM Maintenance
Requirements for Privately Maintained Drainage Facilities).
12 TEC
APPENDIX A
FIGURES
1. Technical Information Report (TIR) Worksheets
2. Site Location Map
3. Drainage Basins, Subbasins, & Site Characteristics
4. SCS Soils Map
King County Department of Development
Subdivison
and Environmental Services
TECHNICAL INFORMATION
❑
REPORT (TIR) WORKSHEET
❑
Commercial
❑
Other
❑
E -
PRf�J-ECT �i"l G iR
❑
❑
D"���Lc(Yl ■ { .i p 5 4'YF '�"'"`Ct ff P
1
.....:
Other
�''� kld,
;
Project Owner ,
Project Name
_Prove des ,%'Old
Location
&,??�
Address
&, e -IA41 // -
Township
Phone
Range
ZD to -� SZ� _ �
Section3
Project Engineer
(_c/�itC.
Company
Address/Phone !
e?,?v27
`
Subdivison
❑
Short Subdivision
❑
Grading
❑
Commercial
❑
Other
❑
DFW HPA
❑
Shoreline Management
❑
COE 404
❑
Rockery
❑
DOE Dam Safety
❑
Structural Vaults
❑
❑
FEMA Floodplain
COE Wetlands
Other
�''� kld,
4
Part S1T{CO1!»hilTAt�li]?RAINAGE
Community
Drainage Basin
&j (? e �C
❑ River
{� Stream 5009 e k
❑ Critical Stream Reach
❑ Depression s/Swa I es.
Lake
�I Steep Slopes 410 Y _
❑ Floodplain [
® Wetlands ,�noS Creek—e2dIaf,:2iT
❑ Seeps/Springs
❑ High Groundwater Table
❑ Groundwater Recharge
❑ Other
Soil Type
Slopes
-.3y
Erosion Potential
Erosive Velcoties
JK Additional Sheets Attached,�eP (tlec,4
REFERENCE
Ch 4 — Downstream Analysis
❑ Additional Sheets Attached
MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION
® Sedimentation Facilities
Stabilized Construction Entrance
® Perimeter Runoff Control
Clearing and Graing Restrictions
Cover Practices
Construction Sequence
❑ Other
LIMITATION/SITE CONSTRAINT
MINIMUM ESC REQUIREMENTS
AFTER CONSTRUCTION
© Stabilize Exposed Surface
Remove and Restore Temporary ESC Facilities
® Clean and Remove All Silt and Debris
® Ensure Operation of Permanent Facilities
Flag Limits of SAO and open space
preservation areas
❑ Other
❑
Grass Lined
❑
Tank
❑
Infiltration
❑
Channel
]
Vault
❑
Depression
Pipe System
n
Energy Dissapator
.©
Flow Dispersal
❑
Open Channel
❑
Wetland
❑
Waiver
❑
Dry Pond
❑
Stream
❑
Regional
Wet Pond
Detention
U
Brief Description of System Operation -h C6* 49r �
Facility Related Site Limitations�f�S at2� �0(�'di ecs /✓�'r�,
Reference Facility Limitation
❑
Cast in Place Vault
Retaining Wail
❑
Rockery > 4' High
❑
Structural on Steep Slope
❑
Other
❑ Drainage Easement
❑ Access Easement
❑ Native Growth Protection Easement
Tract
❑ Other
1 or a civil engineer under my supervision my supervision have visited the site. Actual site
conditions as observed were incorporated into this worksheet and the attachments. To the best of
my knowledge the information provided here is accurate.
-?- 2- D -S
KING COUNTY, WASIIINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Project Owner &1q,40 -le 5
Phone 24 -nti
Address a Ale AJC
Project Engineer 60-44 1kf- r_
Company :�' /,n,-
Phone
ncPhone Z - f 5��
W Landuse Services
Subdivison <Mrt ubd / UPD
❑ Building Services
MIF / Commerical / SFR
❑ Clearing and Grading
❑ Right -of -Way Use
❑ Other
Project Name Awce C4,s / fel
DDES Permit # 4Qri�f o D
Location Township
Range
Section
Site Address /2212 -.Ji -z 192444V
Parl:'� 'pTi�l~R 7�EVIEW.S AND f'E�MiT�
❑ DFW HPA ❑ Shoreline
❑ COE 404 Management
❑ DOE Dam Safety ® Structural
Rockery/Vault/
LJ Floodplain LlESA Section 7
❑ COE Wetlands
❑ Other otS �4
2005 Surface Water Design Manual 1 1/1/05
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Monitoring Required: Yes 1 No
Start Date:
Completion Date:
Community Plan: 106,12
Special District Overlays:
Drainage Basin: Sbos &-ee C
Stormwater Requirements:
❑ River/Stream
❑ Lake
❑ Wetlands
❑ Closed Depression
❑ Floodplain
❑ Other
Describe:
LA Steep Slope��
❑ Erosion Hazard
❑ Landslide Hazard
❑ Coal Mine Hazard
❑ Seismic Hazard
❑ Habitat Protection
Ll
Soil Type Slopes
/�-0
❑ High Groundwater Table (within 5 feet) ❑ Sole Source Aquifer
❑ Other ❑ Seeps/Springs
Erosion Potential
Additional Sheets Attached Se,- L4),,aA,, eeC oe,4 r rtdwr SPP-r6',4e- aveK-
2005 Surface Water Design Manual 2 111105
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
REFERENCE
121 Core 2 - Offsite Analysis
❑ Sensitive/Critical Areas
❑ SEPA
❑ Other
El
❑ Additional Sheets Attached
LIMITATION 1 SITE CONSTRAINT
Dart 12- T1R. SUMMARY SHl=ET. .-
--77777777-777-77
rov6 orae"TIR Summa, Sheet er: Threshold li€schar e Area
'threshold Discharge Area:
name or description)
Core Requirements (all 8 apply)
Discharge at Natural Location
Number of Natural Discharge Locations:
Offsite Analysis
Level: CD 2 / 3 dated: 'gyp 2,0 - ZQb!
u Z.L%0
Flow Control
Level: 1 /(V 3 or Exemption Number
incl. facility summa sheet
Small Site BMPs
Conveyance System
Spill containment located at:
Erosion and Sediment Control
ESC Site Supervisor:
Contact Phone:
After Hours Phone:
Maintenance and Operation
Responsibility: Privateu lc
If Private, Maintenance Log Required: Yes / No
Financial Guarantees and
Provided: Yes 1 No
Liability
Water Quality
Type: Basic Sens. Lake / Enhanced Basicm /Bag
(include facility summary sheet)
or Exemption o.
Landscape Management Plan: Yes / No
Special Requirements as applicable)
Area Specific Drainage
Type: CDA I SDO / MDP / BP / LMP /Shared Fac. /None
Requirements
Name:
Flood plain/Floodway Delineation
Type: Major / Minor / Exemption / None
100 -year Base Flood Elevation (or range):
Datum:
Flood Protection Facilities
Describe:
Source Control
Describe landuse:
(comm./industrial landuse)
Describe any structural controls:
2005 Surface Water Design Manual 3 111105
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Oil Control High -use Site: Yes / No
Treatment BMP:
Maintenance Agreement: Yes / No
with whom?
Other Drainage Structures
Describe:
Part 13 _EROS] ON-, AN DSEDIMENT CONTROL -R EQU IR IFMENT&;J',,',�
MINIMUM ESC REQUIREMENTS MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION AFTER CONSTRUCTION
Clearing Limits Stabilize Exposed Surfaces
Cover Measures ❑ Remove and Restore Temporary ESC Facilities
Perimeter Protection ❑ Clean and Remove All Silt and Debris Ensure
Traffic Area Stabilization Operation of Permanent Facilities
❑ Sediment Retention LJ Flag Limits of SAO and open space
preservation areas
Surface Water Control
J Other
Dust Control
❑ Construction Sequence
Part :1 STORMWATE.,,
FACILITY DESCRIPTIONS' Note:, Include Facility..Summar )(_arnOKetcn),.
Flow Control
Type/Des�n tion
Water Quality
�Te/Description
❑ Detention
❑ Infiltration
❑ Regional Facility
❑ Shared Facility
LJ Small Site BMPs
J Other
❑Biofiltration.
Wetpool
❑ Media Filtration
LJ Oil Control
L) Spill Control
LJ Small Site BMPs
L) Other
W/ rleuve dv- r
V64 le S
2005 Surface Water Design Manual 111105
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
I, or a civil engineer under my supervision, have visited the site. Actual site conditions as observed were
incorporated into this worksheet and the attached Technical Information Report. To the best of my
knowledge the information provided h re is accurate.
2005 Surface Water Design Manual - 1/] 105
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Soil Map—King County Area, Washington
Map Unit Legend
Fleuve des Voiles 8. Cogger - Figure 4
�` � t✓ - : r �' ✓ �, r v �" Cz F ';`� '"� r r ' E SiC ' a - Y s
snxy ISrigodfntyz raa, WashlrigtonVIfA693}
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Jalap_ C�ntt SyrnGol t
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31.6
59.7%
0 to 6 percent slopes
AgD
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8.6
16.3%
15 to 30 percent slopes
_
EvB
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3.1
5.9%
to 5 percent slopes
No
Norma sandy loam
9.2
17,4%
Sk
Seattle muck
0.4
0.7%
Totals for Area of Interest (AOI)
USDA Natural Resources Web Soil Survey 2.0
Rim— Conservation Service National Cooperative Soil Survey
52.9
411812008
Page 3 of 3
APPENDIX B
OFF-SITE ANALYSIS
DRAINAGE SYSTEM TABLE AND MAP
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1976.0110
C
DRNG
13038
SE 188TH PL
{d BLVD LN
666G2
1977-0072
C
FLDG
12202
SE 192ND ST
686F2
1977-0074
C
FLDG
13210
SIS 192ND ST
9LL/DRXN WAY
68662
1976-0080
C
PONDING
19248
121ST PL SE
EAST OF BENSON HWY
688F2
1978-0081
C
DRNG
19248
121ST PL SE
666F2
'1981-0225
C
FLDG
13210
SE 192ND ST
DRAIN WAY FILLED
686GZ
1952-0539
C
FLDG
12600
SE 192ND ST
EAST KENT AREA
666F2
1984-0313
R
FLDG
13250
SE 192ND ST
TO ROADS DIVA
686F2
1954-0314
C
FLDG
73250
SE 192ND ST
SE 192ND ST/134TH AVE SE
686F2
1985-0534
X
DRNG
13250
SE
102ND ST
LTR TO COMPLAINT
686G2
1985-0617
C
DRNG
1$432
$E
167TH ST
FLDG ON SIDEWALK
686G2
1988.0818
C
FLDG
13440
SE
192ND $T
REF:86-0632 NESPER 87-0770
688G2
1986.0616
ER
FLDG
13340
SE
192ND ST
(REF:86-0632 NESPER) PVT PROS,
686G2
1986.1276
CL
CLAIM 410373
688G2
1967-0770
C
FLDG
13440
SE
192ND ST
FAIRWOOD SEE 86-0816
6$8G2
1967-1049
C
TO RD COORD 04127197.
688F2
1988.0118
X
DRNG
13250
SE
192ND ST
SEE 86-1278 NESPERICL-FORSESTTRAi
666G2
1988-0238
0
FLDG
16431
120TH AVE
SE NEW DRIVEWAY W ILL IT FLOOD
689F2
1968.0238
ER
PIPF
18431
120TH AVE
SE NEED EXTENSION OF 42" CULVERT
666F2
1988-0305
C
BLOCKAGE
12716
SE
188TH PL
EASEMENT-FAIRWOOD/WALL CONSTRUC 686G2
1989-0003
C
ARNG
18812
120TH AVE
SE INCREASED RUNOFF/CHANNEL
686F2
1989-0192
C
DRNG
18612
120TH AVE
SE X PIPE NOT WORKING
686F2
1989-0550
C
EROSION
1SI19
130TH AVE
SE OLD EASEMENT CHANNEL MAINTENANCE 686G2
1989.0665
C
DRNG
13308
SE
184TH PL
WATER IN BASEMENTNARD DRAIN CLOG
666G2
1990-0056
C
FLDG
12700
SE
187TH PL
UTILITY EA•SEMT CLOGGED 90-0259
686G2
1990.0259
C
FLDG
12700
SE
187TH PL
PVT DITCH OVERFLOW
66602
1994.1106
C
DRNG
13517
SE
189TH PL
CULVERT BLEW TRASH RACK/ CEDAR ES
686G2
1990.1106
NDA
DRNG
13517
SIE
169TH PL
CULVERT BLEW TRASH RACW CEDAR ES
688G2
1950-1155
C
DRNG
1'3421
SE
189TH PLACE
13517 SE 189TH PL
WG2
1990.1955
NDA
DRNG
13421
$E
189TH PLACE
REF 90-1106
686G2
1990-1156
C
DRNG
'13429
SE
189TH PLACE
13517 SE 199TH PL
686G2
1990-1156
NDA
DRNG
13429
SE
1897H PLACE
REF 9D-1'106
666G2
1990.1157
C
DRNG
13435
SE
189TH PLACE
13517 SE 1897H PL
686G2
1993.1157
NDA
DRNG
13435
SE
189TH PLACE
FIEF 90-1106
686G2
1990.1158
C
DRNG
18917
SE
189TH PLACE
13517 SE 189TH PL
686G2
1990-1158
NDA
DRNG
18917
SE
189TH PLACE
REF 90-1106
688G2
19SD-1159
C
QRNG
13523
Sr;
189TH PLACE
13517 SE 169TH PL
68602
Page 1 of 3