SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-1
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SP
SM
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, light brownish gray, dry to moist, very fine to medium grained sand SILTY SAND, dense, dark yellowish brown, moist, fine to medium sand
SILTY SAND, dark yellowish brown, moist, fine to coarse grained sand
SILTY SAND, dense, olive gray, moist, very fine to fine sand Poorly graded SAND, dense, olive brown, moist, fine grained sand SILTY SAND, dense, olive, moist, fine sand
SILTY SAND, medium dense, olive gray, moist, very fine to fine grained sand Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 32 35
50/5"
22 29
47 25
50 36
50/5"
7 13
29 ~1112'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-2
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SP-SM
SC-SM
SA, MD,
EI, CR
CO
B-1
R-1
R-2
R-3
R-3
R-5
Pauba Formation (Qps); SILTY SAND, grayish brown, dry to moist, fine to coarse grained sand, MD=134.5 @ 7.0%, EI=0 SILTY SAND, dense, grayish brown, dry to moist, fine to coarse grained sand SILTY SAND, medium dense, dark yellowish brown, moist, fine to coarse sand, CO=-0.65%
SILTY SAND with GRAVEL, dark yellowish brown, moist, fine to coarse grained sand with fine gravel
SILTY SAND, dense, grayish brown, moist, fine to medium grained sand
Poorly graded SAND with SILT, medium stiff, olive gray, moist, fine grained sand SILTY, CLAYEY SAND, medium dense, olive yellow, moist, fine grained sand Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 31 36
50 14
19 24
15 25
50/5"
6 11
10 10
22 25
~1107.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-3
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SP-SM
SP
R-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand
SILTY SAND, light brownish gray, dry to moist, fine to medium grained sand
SILTY SAND, dense, dark yellowish brown, dry to moist, fine to coarse grained sand
SILTY SAND, dark yellowish brown, moist, fine to coarse grained sand
SILTY SAND, dense, olive brown, moist, fine to medium grained sand, iron oxide staining
Poorly graded SAND with SILT, dense, olive brown, moist, fine grained sand Poorly graded SAND, dense, gray, moist, fine grained sand Total Depth = 20.75' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 34 50/4"'
17 25
40 15
23 38
40 50/3"
~1112'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-4
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
R-1
B-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, yellowish brown, moist, fine to coarse grained sand SILTY SAND, dense, brown, moist, fine to coarse grained sand SILTY SAND, dark yellowish brown, moist, fine to coarse grained sand
SILTY SAND, dense, olive gray, moist, fine to medium grained sand
SILTY SAND, dense, olive gray, moist, very fine to fine grained sand
SILTY SAND, dense, olive, moist, fine to medium grained sand Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 40 50/5"
9 31
45 17
23 43
12 25
30 ~1111'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-5
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SP-SM
B-1 SA
R-1
R-2
R-3
R-4
R-5
Quaternary Alluvium (Qal); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, medium stiff, grayish brown, moist, fine to medium grained sand
SILTY SAND, medium dense, dark brown, moist, fine to medium grained sand
Pauba Formation (Qps); SILTY SAND, dark yellowish brown, moist, very fine to medium grained sand SILTY SAND, dense, olive brown, moist, fine to medium grained sand
SILTY SAND, medium dense, olive gray, moist, fine to medium grained sand
Poorly graded SAND with SILT, dense, light brownish gray, moist, fine grained sand Total Depth = 21.42' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 12 16
18 16
18 17
12 30
36 10
16 32
20 32
50/5"
~1098'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-6
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC-SM
SP-SM
R-1
R-2
R-3
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand SILTY SAND, pale brown, moist, fine to medium grained sand SILTY SAND, dense, dark yellowish brown, moist, fine to coarse grained sand SILTY, CLAYEY SAND, grayish brown, moist, fine to coarse grained sand Poorly graded SAND with SILT, medium dense, grayish brown, moist, fine grained sand, silt in shoe Poorly graded SAND with SILT, dense, light brownish gray, moist, very fine to fine grained sand Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 17 33
39 13
21 19
9 24
29 ~1115'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-7
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SP-SC
SM
B-1
R-1
R-2
R-3
R-4
Quaternary Alluvium (Qal); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel Pauba Formation (Qps); SILTY SAND, dense, light brownish gray, dry to moist, fine to coarse grained sand
SILTY SAND, medium dense, dark yellowish brown, moist, fine to coarse grained sand
SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
Poorly graded SAND with SILT, dense, light brown, moist, fine grained sand, interbedded CLAYEY SAND, dense, moist, olive, fine to medium grained sand SILTY SAND, dense, olive brown, moist, fine grained sand Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 10 22
29 15
17 22
34 22
34 10
28 40
~1105.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-8
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SW-SM
SC
R-1
R-2
R-3
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, grayish brown, moist, fine to medium grained sand SILTY SAND, dense, dark grayish brown, moist, fine to coarse grained sand SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
Well-graded SAND with SILT, medium dense, light gray, moist, fine to coarse grained sand CLAYEY SAND, medium dense, olive gray, moist, fine to medium grained sand
Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 32 30
31 10
18 27
5 8
13 ~1112'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-9
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SP-SM
SM
R-1
R-2
R-3
R-4
Quaternary Alluvium (Qal); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel Pauba Formation (Qps); SILTY SAND, dense, dark reddish
brown, moist, fine to coarse grained sand
SILTY SAND, dense, dark yellowish brown, moist, fine to coarse grained sand SILTY SAND, grayish brown, moist, fine to medium grained sand Poorly graded SAND with SILT, dense, olive brown, moist, fine grained sand SILTY SAND, dense, olive, moist, fine to medium grained sand Total Depth = 16.33' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 22 36
50/4"
40 50/6"
27 37
50/3"
18 34
50/4"
~1103'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-10
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC-SM
SM
R-1 RV
B-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brown, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, yellowish brown, moist, fine to coarse grained sand SILTY SAND, medium dense, dark yellowish brown, moist, fine to coarse grained sand, RV=18
SILTY SAND, olive brown, moist, fine to coarse grained sand SILTY SAND, dense, dark yellowish brown, moist, fine to coarse sand
SILTY, CLAYEY SAND, dense, dark reddish brown, moist, fine to coarse grained sand
SILTY SAND, dense, light reddish brown, moist, fine to medium grained sand, few clay
SILTY SAND, dense, olive brown, moist, fine grained sand Total Depth = 26.0' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 15 18
16 23
28 30
19 24
40 19
25 47
25 50
~1117'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-11
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SW
SW-SM
SM
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND, brown, dry to moist, fine to medium grained sand
SILTY SAND, dense, reddish brown, moist, fine to coarse grained sand
SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND, pale brown, moist, fine to coarse grained sand SILTY SAND, dense, reddish brown, moist, fine to coarse grained sand
Well-graded SAND, medium dense, light brownish gray, dry to moist, fine to coarse grained sand Well-graded SAND with SILT, dense, light gray, dry to moist, fine to coarse grained sand
SILTY SAND, dense, pale brown, moist, fine to medium grained sand
Total Depth = 27.0' bgs, no groundwater encountered, backfilled with cuttings on 08/11/14 25 32
44 27
21 30
18 20
22 23
39 50
25 50
~1122'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-11-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-12
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
CL
ML
CL
CO
B-1
R-1
R-2
R-3
R-4
B-2
R-5
Quaternary Alluvium (Qal); SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand SILTY SAND, dense, grayish brown, dry to moist, fine to medium grained sand
Pauba Formation (Qps); SILTY SAND, dense, dark yellowish brown, moist, fine to medium grained sand
SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
SILTY SAND, medium dense, brown, moist, fine to medium
grained sand, CO=-0.36%
SILTY SAND, dense, dark yellowish brown, moist, fine to medium grained sand, trace clay
SANDY Lean CLAY, dark brown, moist, fine to medium grained sand
SILT with SAND, hard, olive, moist, very fine to fine grained sand Lean CLAY, olive brown, moist
14 29
50/5"
20 25
27 6
10 15
9 23
39 5
14 26
~1096'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-13
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SW-SM
SW-SM
SM
R-6
R-7
R-8
Well-graded SAND with SILT and GRAVEL, dense, light olive brown, moist, fine to coarse grained sand with fine gravel Well-graded SAND with SILT, dense, dark grayish brown, moist to wet, fine to medium grained sand SILTY SAND, dense, dark grayish brown, moist to wet, fine to medium grained sand Total Depth = 51.5' bgs, groundwater encountered @ 48.3' bgs, backfilled with cuttings on 08/12/14 21 35
50 20
30 50/4"
13 20
36 ~1096'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
30 35
40 45
50 55
60 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-13
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SC-SM
ML
SM
R-1
R-2
R-3
R-4
R-5
Quaternary Alluvium (Qal); SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand SILTY SAND, dense, light brownish gray, dry to moist, fine to medium grained sand Pauba Formation (Qps); SILTY SAND, dense, dark yellowish brown, moist, fine to medium grained sand
SILTY, CLAYEY SAND, dark brown, moist, fine to coarse grained sand
SILTY, CLAYEY SAND, dense, dark yellowish brown, moist, fine to coarse grained sand
CLAYEY SILT with SAND, hard, olive, moist, very fine to fine grained sand SILTY SAND, dense, olive, moist, very fine to fine grained sand Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 8 19
47 25
32 25
15 26
50 9
16 19
16 27
32 ~1103'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-14
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, brown, moist, fine to coarse grained sand
SILTY SAND, dense, dark yellowish brown, moist, fine to coarse grained sand SILTY SAND with GRAVEL, dark yellowish brown, moist, fine to coarse grained sand with fine gravel
SILTY SAND, dense, olive brown, moist, fine to coarse grained sand
SILTY SAND, medium dense, olive brown, moist, very fine to fine grained sand SILTY SAND, dense, olive, moist, fine grained sand
SILTY SAND, dense, olive brown to light olive gray, moist, fine grained sand Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 15 32
45 18
38 50/5"
14 16
26 32
35 50/5"
9 14
45 ~1110'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-15
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SC
SM
B-1
R-1
R-2
R-3
R-4
Quaternary Alluvium (Qal); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel Pauba Formation (Qps); SILTY SAND, dense, light brownish gray, dry to moist, fine to medium grained sand, roots
SILTY SAND, dense, dark grayish brown, moist, fine to coarse grained sand SILTY SAND, dark yellowish brown, moist, fine to coarse grained sand
CLAYEY SAND, medium dense, olive brown, moist, fine to
medium grained sand
SILTY SAND, dense, olive brown to olive, moist, fine grained sand Total Depth = 17.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 30 50
20 29
33 7
20 26
11 30
50 ~1099'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-16
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
CL
R-1
B-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand
SILTY SAND, grayish brown, dry to moist, fine to coarse grained sand
SILTY SAND, dense, brown, moist, fine to coarse grained sand SILTY SAND, olive brown, moist, fine to medium grained sand, trace clay SILTY SAND, medium dense, olive, moist, very fine to medium grained sand
SILTY SAND, dense, dark grayish brown, moist, fine grained sand SANDY Lean CLAY, stiff, olive, moist, fine to medium grained sand
Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 13 43
50/4"
6 10
21 18
38 50/5"
3 6
10 ~1111.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-17
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SP-SM
SM
ML
SM
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND, grayish brown, dry to moist, fine to coarse grained sand SILTY SAND, yellowish brown, moist, fine to coarse grained sand SILTY SAND, medium dense, grayish brown, dry to moist, fine to coarse grained sand
SILTY SAND, olive brown, moist, fine to medium grained sand Poorly graded SAND with SILT, dense, light olive gray, dry to moist, fine grained sand SILTY SAND, dense, olive brown, moist, fine to medium grained sand
SANDY SILT, medium stiff, olive, moist, very fine to fine grained sand
SILTY SAND, medium dense, olive, moist, fine to medium grained sand
Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 17 19
24 37
50 15
32 50
3 5
8 5
13 20
~1106'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-18
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM-ML
SM
R-1 CO
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, yellowish brown, moist, fine to medium grained sand
SILTY SAND, medium dense, dark yellowish brown, moist, fine to coarse grained sand, CO=-0.63%
SILTY SAND, yellowish brown, moist, fine to medium grained sand
SILTY SAND to SANDY SILT, medium dense to hard, olive brown to light olive gray, moist, fine grained sand
SILTY SAND, dense, dark yellowish brown to olive, moist, fine to coarse grained sand
SILTY SAND, dense, dark yellowish brown to light gray, moist, fine grained sand SILTY SAND, medium dense, olive brown, moist, fine to medium grained sand
Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 13 14
9 12
13 26
23 37
35 25
50/4.5"
6 16
30 ~1111'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-19
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC
ML
SM
SW
SW-SM
SM-ML
R-1 EI
B-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel CLAYEY SAND, grayish brown, moist, fine to medium grained sand
SANDY SILT, hard, light olive brown, moist, very fine to fine grained sand, elastic, EI=106 SANDY SILT, olive brown, moist, fine to medium grained sand SILTY SAND, dense, light gray, moist, very fine to fine grained sand, iron oxide staining
Well-graded SAND with GRAVEL, dense, light gray, dry to moist, fine to coarse grained sand with fine gravel Well-graded SAND with SILT, dense, yellowish brown, moist, fine to coarse grained sand
SILTY SAND to SANDY SILT, dense to hard, olive gray, moist, very fine to fine grained sand Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 4 10
31 10
21 39
20 41
50/5"
27 50/5"
6 16
38 ~1115'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-20
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC
SC-SM
CL
SC-SM
SA, MD,
CR
B-1
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND, light gray, dry to moist, fine to coarse grained sand, MD=133.5 @ 7.0% SILTY SAND, medium dense, grayish brown, dry to moist, fine to medium grained sand SILTY SAND, dense, dark yellowish brown, moist, fine to medium grained sand
CLAYEY SAND, dark brown, moist, fine to medium grained sand SILTY, CLAYEY SAND, dense, light brown, moist, fine to coarse grained sand SANDY Lean CLAY, very stiff, olive, moist, fine to medium grained sand
SILTY, CLAYEY SAND with GRAVEL, dense, olive brown to
dark yellowish brown, moist, fine to coarse grained sand with fine gravel
Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 8 17
27 16
33 43
8 20
27 7
12 15
5 13
40 ~1111.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-21
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
ML
SM
SW-SM
SM
CL
SM
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, light brownish gray, dry to moist, fine to medium grained sand, trace clay
SILTY SAND, dense, light olive gray, moist, fine grained sand, caliche nodules SANDY SILT, olive brown, moist, fine to medium grained sand SILTY SAND, dense, olive brown, moist, fine grained sand Well-graded SAND with SILT, dense, light brown, moist, fine to coarse grained sand, trace clay
SILTY SAND, medium dense, light olive gray, moist, very fine to fine grained sand
SANDY Lean CLAY, hard, olive brown, moist, fine to medium grained sand
SILTY SAND, dense, brown, moist, fine to medium grained sand Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/12/14 13 43
50/5"
13 28
50 22
30 35
17 22
18 6
26 27
~1115'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
H - 140lb - Autohammer - 30" Drop Soil Class.
8-12-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.001
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-22
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SC-SM
SM
SP-SM
ML
SM
SW-SM
SM
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY, CLAYEY SAND, dark grayish brown, dry to moist, fine to coarse grained sand
SILTY SAND, olive brown, moist, fine to medium grained sand Poorly graded SAND with SILT, medium stiff, olive brown, moist, fine grained sand SILT with SAND, olive brown, moist, very fine to fine grained sand SANDY SILT, hard, olive brown, moist, very fine to fine grained sand
SILTY SAND, dense, olive brown, moist, fine grained sand Well-graded SAND with SILT, dense, light brown, moist, fine to coarse grained sand, trace clay
SILTY SAND, medium dense, olive brown, moist, fine to medium grained sand
Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 11 21
24 11
24 30
22 37
50/5"
22 38
50 6
16 21
~1114.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-23
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SW
SW-SM
ML
B-1
R-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND, dark grayish brown, dry to moist, fine to coarse grained sand
SILTY SAND, light brownish gray, moist, fine to medium grained sand
SILTY SAND, dense, olive brown, moist, fine to medium grained sand, caliche
SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND, dense, olive brown, moist, fine grained sand, iron oxide staining
Well-graded SAND with GRAVEL, dense, light gray, dry to moist, fine to coarse grained sand with fine gravel Well-graded SAND with SILT and GRAVEL, dense, light brown, moist, fine to coarse grained sand with fine gravel, few clay SANDY SILT, stiff, olive gray, moist, very fine to fine grained sand, few clay, caliche nodules
Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 16 27
33 16
30 50
15 30
37 28
50/5"
5 10
15 ~1114'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-24
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SW
ML
R-1
B-1
R-2
R-3
R-4
R-5
Pauba Formation (Qps); SILTY SAND, grayish brown, dry to moist, fine to medium grained sand SILTY SAND, yellowish brown, moist, fine to coarse grained sand SILTY SAND, dense, olive brown, moist, fine grained sand, manganese oxide nodules SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND, dense, olive brown, moist, fine grained sand SILTY SAND, dense, olive brown, moist, fine grained sand Well-graded SAND, dense, light brown, dry to moist, fine to coarse grained sand SANDY SILT, stiff, olive brown to olive gray, moist, very fine to fine grained sand, caliche nodules
Total Depth = 26.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 12 26
44 10
24 40
18 21
50/5"
20 26
40 4
7 14
~1115'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-25
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SC
SM
SM-ML
R-1
R-2
R-3
Artificial Fill (Af); SILTY SAND, dark grayish brown, dry to moist, fine to coarse grained sand Pauba Formation (Qps); SILTY SAND, light brownish gray, dry to moist, fine to medium grained sand
CLAYEY SAND, medium dense, dark yellowish brown, moist, fine to coarse grained sand
SILTY SAND, yellowish brown, moist, fine to medium grained sand
SILTY SAND, medium dense, olive brown, moist, fine grained sand SILTY SAND to SANDY SILT, dense to hard, light olive gray, moist, very fine to fine grained sand Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 11 16
29 10
14 26
12 27
35 ~1115.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-26
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
B-1
R-1
R-2
R-3
R-4
Artificial Fill (Af); SILTY SAND, grayish brown, dry to moist, fine to coarse grained sand Pauba Formation (Qps); SILTY SAND, dense, grayish brown, dry to moist, fine to coarse grained sand
SILTY SAND, dense, dark grayish brown, moist, fine to coarse grained sand SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
SILTY SAND, dense, dark yellowish brown, moist, fine to medium grained sand
SILTY SAND, medium dense, olive brown, moist, fine grained sand Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 12 33
50 16
27 36
17 37
50/5"
11 20
23 ~1096'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-27
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC-SM
SC
SW-SM
SM
R-1
R-2
R-3
R-4
Quaternary Alluvium (Qal); SILTY SAND, grayish brown, dry to moist, fine to coarse grained sand Pauba Formation (Qps); SILTY, CLAYEY SAND, dense, dark
yellowish brown, moist, fine to coarse grained sand
CLAYEY SAND, medium dense, dark yellowish brown, moist, fine to medium grained sand
CLAYEY SAND, dark yellowish brown, moist, fine to medium grained sand
Well-graded SAND with SILT, dense, brown, moist, fine to coarse grained sand SILTY SAND, dense, olive brown, moist, fine grained sand Drilled to 16.5' Sampled to 16.5' Groundwater not encountered Backfilled with Cuttings 23 38
50 11
14 24
17 28
40 11
17 44
~1095'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-28
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
CO
B-1
R-1
R-2
R-3
R-4
Quaternary Alluvium (Qal); SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand Pauba Formation (Qps); SILTY SAND, dense, dark yellowish brown, dry to moist, fine to coarse grained sand
SILTY SAND, dense, dark grayish brown, moist, fine to medium grained sand
SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
SILTY SAND, medium dense, dark yellowish brown, moist, fine to medium grained sand, few clay SILTY SAND, dense, dark grayish brown to brown, moist, fine to coarse grained sand
Total Depth = 15.92' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 11 24
40 22
37 45
8 15
21 6
50/5"
~1087.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-29
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC
SC-SM
SM
CO
R-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, dense, dark yellowish brown, dry to moist, fine to medium grained sand CLAYEY SAND, dense, dark yellowish brown, moist, fine to medium grained sand CLAYEY SAND, dark yellowish brown, moist, fine to medium grained sand
SILTY, CLAYEY SAND, medium dense, olive brown, moist, fine to coarse grained sand
SILTY SAND, dense, dark yellowish brown, moist, fine to medium grained sand
Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 25 34
44 18
22 28
9 11
15 18
35 50
~1084'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-30
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SW-SM
SM
SW-SM
ML
R-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND with GRAVEL, grayish
brown, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, olive brown, moist, fine to medium grained sand Well-graded SAND with SILT, dense, brown, dry to moist, fine to coarse grained sand
SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND, dense, olive, moist, fine grained sand
Well-graded SAND with SILT, dense, light olive gray, moist, fine to coarse grained sand
SILT with SAND, stiff, olive, moist, very fine to fine grained sand Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 24 50
13 24
50 18
34 50/5"
4 6
8 ~1097'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-31
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC
SM
SC
SW-SM
MD, EI,
RV
R-1
B-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND with GRAVEL, light gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
CLAYEY SAND, dense, dark yellowish brown, dry to moist, fine to coarse grained sand, MD=134.0 @ 7.5%, EI=0, RV=11
SILTY SAND, olive brown, moist, fine to coarse grained sand CLAYEY SAND, dense, dark yellowish brown, moist, fine to coarse grained sand
Well-graded SAND with SILT, dense, light brown, dry to moist, fine to coarse grained sand, difficult drilling from 10-20'
Well-graded SAND with SILT, dense, brown, moist, fine to coarse grained sand Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 34 50
15 22
33 16
28 44
19 27
43 ~1112'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-32
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
R-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND with GRAVEL, light gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, gray, moist, fine to medium grained sand
SILTY SAND, dense, olive brown, moist, fine grained sand SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND, dense, olive brown, moist, fine grained sand SILTY SAND, dense, brown, moist, fine to coarse grained sand SILTY SAND, dense, olive brown, moist, fine grained sand Total Depth = 21.33' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 18 30
34 12
25 40
25 37
32 16
32 50/4"
~1111'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-33
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
R-1
R-2
R-3
Pauba Formation (Qps); SILTY SAND with GRAVEL, grayish
brown, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, pale brown, moist, fine to medium grained sand SILTY SAND, dense, olive brown, moist, fine to medium grained sand
SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND, dense, dark grayish brown, moist, fine grained sand SILTY SAND, medium dense, dark grayish brown, moist, fine to medium grained sand Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/13/14 15 42
50/4"
23 50
8 19
26 ~1099'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-34
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM-ML
SW
R-1
R-2
Pauba Formation (Qps); SILTY SAND with GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND to SANDY SILT, medium dense to stiff, olive, very fine to fine grained sand
SILTY SAND, olive brown, moist, fine to medium grained sand Well-graded SAND, dense, light brown, dry to moist, fine to coarse grained sand Total Depth = 21.5 bgs, no groundwater encountered, backfilled with cuttings on 08/15/14 7 15
25 16
26 38
~1115.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-15-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
CalPac Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-35
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SC-SM
SC-CL
CO
B-1
R-1
R-2
R-3
R-4
Pauba Formation (Qps); SILTY SAND, grayish brown, dry to moist, fine to coarse grained sand SILTY SAND, medium dense, olive brown, moist, fine grained sand SILTY SAND, loose, olive brown, moist, fine grained sand SILTY SAND, olive brown, moist, fine to medium grained sand SILTY, CLAYEY SAND, medium dense, dark yellowish brown, moist, fine to medium grained sand CLAYEY SAND to SANDY CLAY, medium dense to stiff, olive, moist, fine to medium grained sand
Total Depth = 16.5' bgs, no groundwater encountered, backfilled with cuttings on 08/15/14 9 11
15 3
1 3
14 17
31 7
12 19
~1095'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-15-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
CalPac Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-36
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SW-SM
SM
SC
R-1
R-2
R-3
Quaternary Alluvium (Qal); SILTY SAND, light gray, dry to moist, fine to medium grained sand Pauba Formation (Qps); SILTY SAND, olive brown, moist, fine to medium grained sand
Well-graded SAND with SILT and GRAVEL, medium dense, dark grayish brown, moist, fine to coarse grained sand with fine gravel Well-graded SAND with SILT and GRAVEL, dark grayish brown, moist, fine to coarse grained sand with fine gravel SILTY SAND with GRAVEL, medium dense, dark yellowish
brown, moist, fine to coarse grained sand, gravel and cobble to 2" CLAYEY SAND, dense, dark olive brown, moist, fine to medium grained sand
Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/15/14 13 20
22 15
18 20
7 21
38 ~1083.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-15-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
CalPac Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-37
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
SC-SM
SC
SM
SW-SM
CO
B-1
R-1
R-2
R-3
R-4
Quaternary Alluvium (Qal); SILTY SAND, light gray, dry to moist, fine to medium grained sand Pauba Formation (Qps); SILTY SAND, dense, dark yellowish brown, moist, fine to coarse grained sand
SILTY, CLAYEY SAND, medium dense, olive brown, moist, fine to medium grained sand
CLAYEY SAND, dark yellowish brown, moist, fine to medium grained sand
SILTY SAND, medium dense, olive brown, moist, fine grained sand, iron oxide staining
Well-graded SAND with SILT, medium dense, olive brown to dark grayish brown, moist to wet, fine to coarse grained sand Drilled to 16.5' Sampled to 16.5' Groundwater not encountered Backfilled with Cuttings 26 28
33 7
7 12
5 7
11 14
19 13
~1080'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-15-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
CalPac Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-38
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SW-SM
SC-SM
SW-SM
SM
SC-SM
CO
R-1
R-2
R-3
R-4
Quaternary Alluvium (Qal); SILTY SAND, grayish brown, dry to moist, fine to coarse grained sand Pauba Formation (Qps); Well-graded SAND with SILT, olive brown and dark grayish brown, moist, fine to coarse grained sand SILTY, CLAYEY SAND, medium dense, dark yellowish brown, moist, fine to medium grained sand Well-graded SAND with SILT, dark grayish brown, moist, fine to coarse grained sand
SILTY SAND, medium dense, dark yellowish brown, moist, fine to coarse grained sand
SILTY SAND, medium dense, dark yellowish brown, moist, fine to coarse grained sand
SILTY, CLAYEY SAND, medium dense, dark yellowish brown, moist, fine to medium grained sand Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/15/14 6 12
13 6
8 13
10 13
25 5
12 24
~1081'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-15-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
CalPac Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-39
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
R-1
R-2
R-3
Pauba Formation (Qps); SILTY SAND with GRAVEL, pale brown, dry to moist, fine to coarse grained sand SILTY SAND, yellowish brown, moist, fine to medium grained sand
SILTY SAND, dense, light brown, dry to moist, fine to medium grained sand, few caliche
SILTY SAND, olive brown, moist, fine to medium grained sand SILTY SAND, dense, reddish brown, moist, fine to coarse grained sand
SILTY SAND, dense, olive brown, moist, fine grained sand Total Depth = 21.5' bgs, no groundwater encountered, backfilled with cuttings on 08/15/14 14 20
37 19
23 46
15 29
34 ~1112'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-15-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
CalPac Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-40
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SW-SM
SM
P-1
Quaternary Alluvium (Qal); Well-graded SAND with SILT and GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand Total Depth = 4.0' bgs, no groundwater encountered, backfilled after percolation testing on 08/14/14 ~1098.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-1
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
SM
P-2
Quaternary Alluvium (Qal); SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand Pauba Formation (Qps); SILTY SAND, olive brown, moist, fine to medium grained sand
Total Depth = 4.0' bgs, no groundwater encountered, backfilled with cuttings after percolation testing on 08/14/14
~1095'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-2
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SM
P-3 SM
Quaternary Alluvium (Qal); SILTY SAND, light brownish gray, dry to moist, fine to coarse grained sand SILTY SAND, light brownish gray, moist, fine to medium grained sand
Pauba Formation (Qps); SILTY SAND, yellowish brown, moist, fine to medium grained sand Total Depth = 4.0' bgs, no groundwater encountered, backfilled with cuttings after percolation testing on 08/14/14
~1086.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-3
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
SW-SM
SM
P-4
Pauba Formation (Qps); Well-graded SAND with SILT and GRAVEL, light brownish gray, dry to moist, fine to coarse grained sand with fine gravel SILTY SAND, light gray, dry to moist, fine to medium grained sand SILTY SAND, dark yellowish brown, moist, fine to medium grained sand
Total Depth = 4.0' bgs, no groundwater encountered, backfilled after percolation testing on 08/14/14 ~1094.5'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
JTD
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 8-13-14
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Plate 1
Proposed CarMax, Murrieta
10791.002
Drilling Method
8" Sample No. Feet
Hole Diameter Moisture
Ground Elevation
Depth
0 5
10 15
20 25
30 Blows Elevation Per 6 Inches
SAMPLE TYPES:
Martini Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-4
Logged By
Date Drilled
JTD Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
Geotechnical Exploration Report 10791.002
Proposed CarMax Automotive Dealership October 3, 2014
APPENDIX B
RESULTS OF GEOTECHNICAL LABORATORY TESTING
B-1
0 : 66 : 34 Sep-14
Project Name:
PARTICLE - SIZE
DISTRIBUTION
ASTM D 6913
Soil Identification: Silty Sand (SM), brown.
SM
GR:SA:FI : (%)
Exploration No.:
Depth (feet): 0 - 5.0
SAND
FINE SILT
HYDROMETER
Carmax Geo
Project No.:
LB-3 Sample No.:
Soil Type :
10791.002
3.0" 1 1/2" 3/4" 3/8" #4 #8 #16 #30 #50 #100 #200U.S. STANDARD SIEVE OPENING U.S. STANDARD SIEVE NUMBER
GRAVEL FINES
COARSE COARSE MEDIUM FINE CLAY
0 102030405060708090
100
100.000 10.000 1.000 0.100 0.010 0.001
PERCENT FINER BY WEIGHT
PARTICLE - SIZE (mm)
"
Sieve; LB-3, B-1 (8-11-14 THRU 8-15-14)
B-1
1 : 55 : 44 Sep-14
Project Name:
PARTICLE - SIZE
DISTRIBUTION
ASTM D 6913
Soil Identification: Silty Sand (SM), brown.
SM
GR:SA:FI : (%)
Exploration No.:
Depth (feet): 0 - 5.0
SAND
FINE SILT
HYDROMETER
Carmax Geo
Project No.:
LB-6 Sample No.:
Soil Type :
10791.002
3.0" 1 1/2" 3/4" 3/8" #4 #8 #16 #30 #50 #100 #200U.S. STANDARD SIEVE OPENING U.S. STANDARD SIEVE NUMBER
GRAVEL FINES
COARSE COARSE MEDIUM FINE CLAY
0 102030405060708090
100
100.000 10.000 1.000 0.100 0.010 0.001
PERCENT FINER BY WEIGHT
PARTICLE - SIZE (mm)
"
Sieve; LB-6, B-1 (8-11-14 THRU 8-15-14)
B-1
0 : 59 : 41 Sep-14
Project Name:
PARTICLE - SIZE
DISTRIBUTION
ASTM D 6913
Soil Identification: Silty Sand (SM), brown.
SM
GR:SA:FI : (%)
Exploration No.:
Depth (feet): 0 - 5.0
SAND
FINE SILT
HYDROMETER
Carmax Geo
Project No.:
LB-21 Sample No.:
Soil Type :
10791.002
3.0" 1 1/2" 3/4" 3/8" #4 #8 #16 #30 #50 #100 #200U.S. STANDARD SIEVE OPENING U.S. STANDARD SIEVE NUMBER
GRAVEL FINES
COARSE COARSE MEDIUM FINE CLAY
0 102030405060708090
100
100.000 10.000 1.000 0.100 0.010 0.001
PERCENT FINER BY WEIGHT
PARTICLE - SIZE (mm)
"
Sieve; LB-21. B-1 (8-11-14 THRU 8-15-14)
Tested By : MRV Date: 9/2/14
Input By : MRV Date: 9/2/14
Depth (ft.) 0 - 5.0
X Moist Mechanical Ram
Dry Manual Ram
Mold Volume (ft³) 0.03320 Ram Weight = 10 lb.; Drop = 18 in. 50 100 150 200
123456
6159 6304 6364 6304
4195 4195 4195 4195 AS REC'D
1964 2109 2169 2109 MOISTURE
1136.4 1162.7 1746.3 1432.2 742.9
1112.3 1122.1 1670.9 1365.4 735.4
417.8 420.7 666.2 672.7 217.8
3.5 5.8 7.5 9.6 1.4
130.4 140.0 144.0 140.0
126.0 132.4 134.0 127.7
134.5 7.0
PROCEDURE USED
x Procedure A
Soil Passing No. 4 (4.75 mm) Sieve
Mold : 4 in. (101.6 mm) diameter
Layers : 5 (Five)
Blows per layer : 25 (twenty-five)
May be used if +#4 is 20% or less
Procedure B
Soil Passing 3/8 in. (9.5 mm) Sieve
Mold : 4 in. (101.6 mm) diameter
Layers : 5 (Five)
Blows per layer : 25 (twenty-five)
Use if +#4 is >20% and +3/8 in. is
20% or less
Procedure C
Soil Passing 3/4 in. (19.0 mm) Sieve
Mold : 6 in. (152.4 mm) diameter
Layers : 5 (Five)
Blows per layer : 56 (fifty-six)
Use if +3/8 in. is >20% and +¾ in.
is <30%
Particle-Size Distribution:
0:66:34
GR:SA:FI
Atterberg Limits:
LL,PL,PI
MODIFIED PROCTOR COMPACTION TEST
ASTM D 1557
Project No.:
Location:
Project Name: Carmax Geo
10791.002
**
TEST NO.
Wet Density (pcf)
Moisture Added (ml)
Silty Sand (SM), brown.
LB-3, B-1
Preparation Method:
Soil Identification:
Sample No. :
Wt. Compacted Soil + Mold (g)
Wet Weight of Soil + Cont. (g)
Dry Weight of Soil + Cont. (g)
Weight of Container (g)
Weight of Mold (g)
Net Weight of Soil (g)
Maximum Dry Density (pcf) Optimum Moisture Content (%)
Dry Density (pcf)
Moisture Content (%)
110.0
115.0
120.0
125.0
130.0
135.0
140.0
0.0 5.0 10.0 15.0 20.
Dry Density (pcf)
Moisture Content (%)
SP. GR. = 2.65
SP. GR. = 2.70
SP. GR. = 2.75
X
X
Compaction A; LB-3, B-1 (8-11-14 THRU 8-15-14)
Tested By : MRV Date: 9/3/14
Input By : MRV Date: 9/4/14
Depth (ft.) 0 - 5.0
X Moist Mechanical Ram
Dry Manual Ram
Mold Volume (ft³) 0.03320 Ram Weight = 10 lb.; Drop = 18 in. 50 100 150 200
123456
6254 6346 6320 6272
4195 4195 4195 4195 AS REC'D
2059 2151 2125 2077 MOISTURE
1664.9 1502.7 1443.2 1352.6 760.1
1619.6 1446.3 1378.5 1260.3 745.1
716.0 672.8 666.2 417.8 214.7
5.0 7.3 9.1 11.0 2.8
136.7 142.8 141.1 137.9
130.2 133.1 129.4 124.3
133.5 7.0
PROCEDURE USED
x Procedure A
Soil Passing No. 4 (4.75 mm) Sieve
Mold : 4 in. (101.6 mm) diameter
Layers : 5 (Five)
Blows per layer : 25 (twenty-five)
May be used if +#4 is 20% or less
Procedure B
Soil Passing 3/8 in. (9.5 mm) Sieve
Mold : 4 in. (101.6 mm) diameter
Layers : 5 (Five)
Blows per layer : 25 (twenty-five)
Use if +#4 is >20% and +3/8 in. is
20% or less
Procedure C
Soil Passing 3/4 in. (19.0 mm) Sieve
Mold : 6 in. (152.4 mm) diameter
Layers : 5 (Five)
Blows per layer : 56 (fifty-six)
Use if +3/8 in. is >20% and +¾ in.
is <30%
Particle-Size Distribution:
0:59:41
GR:SA:FI
Atterberg Limits:
LL,PL,PI
MODIFIED PROCTOR COMPACTION TEST
ASTM D 1557
Project No.:
Location:
Project Name: Carmax Geo
10971.002
**
TEST NO.
Wet Density (pcf)
Moisture Added (ml)
Silty Sand (SM), brown.
LB-21, B-1
Preparation Method:
Soil Identification:
Sample No. :
Wt. Compacted Soil + Mold (g)
Wet Weight of Soil + Cont. (g)
Dry Weight of Soil + Cont. (g)
Weight of Container (g)
Weight of Mold (g)
Net Weight of Soil (g)
Maximum Dry Density (pcf) Optimum Moisture Content (%)
Dry Density (pcf)
Moisture Content (%)
110.0
115.0
120.0
125.0
130.0
135.0
140.0
0.0 5.0 10.0 15.0 20.
Dry Density (pcf)
Moisture Content (%)
SP. GR. = 2.65
SP. GR. = 2.70
SP. GR. = 2.75
X
X
Compaction A; LB-21, B-1 (8-11-14 THRU 8-15-14)
Tested By : MRV Date: 9/3/14
Input By : MRV Date: 9/4/14
Depth (ft.) 5.0 - 10.0
X Moist Mechanical Ram
Dry Manual Ram
Mold Volume (ft³) 0.03320 Ram Weight = 10 lb.; Drop = 18 in. 0 50 100 150
123456
6225 6361 6338 6268
4195 4195 4195 4195 AS REC'D
2030 2166 2143 2073 MOISTURE
1958.3 975.8 958.2 1052.6 1001.6
1909.9 924.5 897.9 990.5 974.5
971.4 217.8 214.7 414.8 419.3
5.2 7.3 8.8 10.8 4.9
134.8 143.8 142.3 137.7
128.2 134.1 130.8 124.3
134.0 7.5
PROCEDURE USED
x Procedure A
Soil Passing No. 4 (4.75 mm) Sieve
Mold : 4 in. (101.6 mm) diameter
Layers : 5 (Five)
Blows per layer : 25 (twenty-five)
May be used if +#4 is 20% or less
Procedure B
Soil Passing 3/8 in. (9.5 mm) Sieve
Mold : 4 in. (101.6 mm) diameter
Layers : 5 (Five)
Blows per layer : 25 (twenty-five)
Use if +#4 is >20% and +3/8 in. is
20% or less
Procedure C
Soil Passing 3/4 in. (19.0 mm) Sieve
Mold : 6 in. (152.4 mm) diameter
Layers : 5 (Five)
Blows per layer : 56 (fifty-six)
Use if +3/8 in. is >20% and +¾ in.
is <30%
Particle-Size Distribution:
GR:SA:FI
Atterberg Limits:
LL,PL,PI
MODIFIED PROCTOR COMPACTION TEST
ASTM D 1557
Project No.:
Location:
Project Name: Carmax Geo
10791.002
**
TEST NO.
Wet Density (pcf)
Moisture Added (ml)
Silty, Clayey Sand (SC-SM), reddish brown.
LB-32, B-1
Preparation Method:
Soil Identification:
Sample No. :
Wt. Compacted Soil + Mold (g)
Wet Weight of Soil + Cont. (g)
Dry Weight of Soil + Cont. (g)
Weight of Container (g)
Weight of Mold (g)
Net Weight of Soil (g)
Maximum Dry Density (pcf) Optimum Moisture Content (%)
Dry Density (pcf)
Moisture Content (%)
110.0
115.0
120.0
125.0
130.0
135.0
140.0
0.0 5.0 10.0 15.0 20.
Dry Density (pcf)
Moisture Content (%)
SP. GR. = 2.65
SP. GR. = 2.70
SP. GR. = 2.75
X
X
Compaction A; LB-32, B-1 (8-11-14 THRU 8-15-14)
One-Dimensional Swell or Settlement
Potential of Cohesive Soils
(ASTM D 4546) -- Method 'B'
Project Name: Tested By: MRV Date: 9/2/14
Project No.: Checked By: JHW Date: 9/4/14
Boring No.: LB-3 Sample Type: IN SITU
Sample No.: R-2 Depth (ft.) 5.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 115.1 Final Dry Density (pcf): 117.4 Initial Moisture (%): 5.9 Final Moisture (%) : 13.4
Initial Height (in.): 0.9940 Initial Void ratio: 0.4642 Initial Dial Reading (in): 0.0500 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.424 Initial Degree of Saturation (%): 34.1
1.050 0.9886 0.00 -0.54 -0.54
2.013 0.9865 0.00 -0.75 -0.75
H2O 0.9801 0.00 -1.40 -1.40
-0.65
Rev. 01-10
Carmax Geo
0.4438
0.0614
0.0635
0.0699
Silty Sand (SM), brown.
10791.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.4563
0.4532
Final Reading
(in) Void Ratio
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 1.00
2.00 3.00
4.00 5.00
0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
One-Dimensional Swell or Settlement
Potential of Cohesive Soils
(ASTM D 4546) -- Method 'B'
Project Name: Tested By: MRV Date: 9/2/14
Project No.: Checked By: JHW Date: 9/4/14
Boring No.: LB-13 Sample Type: IN SITU
Sample No.: R-3 Depth (ft.) 10.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 115.6 Final Dry Density (pcf): 117.3 Initial Moisture (%): 12.4 Final Moisture (%) : 14.6
Initial Height (in.): 1.0010 Initial Void ratio: 0.4577 Initial Dial Reading (in): 0.0500 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.418 Initial Degree of Saturation (%): 73.3
1.050 0.9913 0.00 -0.97 -0.97
2.013 0.9867 0.00 -1.43 -1.43
H2O 0.9831 0.00 -1.79 -1.79
-0.36
Rev. 01-10
Carmax Geo
0.4316
0.0587
0.0633
0.0669
Silty Sand (SM), brown.
10791.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.4436
0.4369
Final Reading
(in) Void Ratio
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 1.00
2.00 3.00
4.00 5.00
0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
One-Dimensional Swell or Settlement
Potential of Cohesive Soils
(ASTM D 4546) -- Method 'B'
Project Name: Tested By: MRV Date: 9/4/14
Project No.: Checked By: JHW Date: 9/4/14
Boring No.: LB-19 Sample Type: IN SITU
Sample No.: R-1 Depth (ft.) 5.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 110.7 Final Dry Density (pcf): 114.8 Initial Moisture (%): 6.3 Final Moisture (%) : 14.7
Initial Height (in.): 0.9970 Initial Void ratio: 0.5228 Initial Dial Reading (in): 0.0500 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.407 Initial Degree of Saturation (%): 32.6
1.050 0.9831 0.00 -1.39 -1.39
2.013 0.9803 0.00 -1.68 -1.68
H2O 0.9741 0.00 -2.30 -2.30
-0.63
Rev. 01-10
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.5016
0.4973
Final Reading
(in) Void Ratio
Carmax Geo
0.4879
0.0669
0.0697
0.0759
Silty Sand (SM), brown.
10791.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 1.00
2.00 3.00
4.00 5.00
0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
Project Name: Tested By: MRV Date: 9/2/14
Project No. : Checked By: JHW Date: 9/4/14
Boring No.: Depth (ft.) 0 - 5.0
Sample No. : Location:
Sample Description:
Dry Wt. of Soil + Cont. (gm.)
Wt. of Container No. (gm.)
Dry Wt. of Soil (gm.)
Weight Soil Retained on #4 Sieve
Percent Passing # 4
in distilled water for the period of 24 h or expansion rate < 0.0002 in./h.
Rev. 03-08
9/3/14 0.4958
0 1390
Expansion Index (EI meas) = ((Final Rdg - Initial Rdg) / Initial Thick.) x 1000 6:00
1450 0.4958
-4.1
Expansion Index ( Report ) = Nearest Whole Number or Zero (0) if Initial Height is > than Final Height 0 Add Distilled Water to the Specimen
Wt. of Container (gm.)
118.8
0.5000
10 0.4999
SPECIMEN INUNDATION
Time
9/3/14 7:00
1.0 1.0
9/2/14 6:50 1.0
1.0 Total Porosity
9/2/14
118.9
Moisture Content (%)
Date
6:40
Void Ratio
Pore Volume (cc)
Degree of Saturation (%) [ S meas]
Before Test After Test
Wet Wt. of Soil + Cont. (gm.)
7 0.411
Dry Density (pcf)
Wet Density (pcf)
Specific Gravity (Assumed)
Specimen Height (in.)
99.8 4.01
2.70 1324.2
0.0 612.5
1324.2
2.5 0.9958
629.7
EXPANSION INDEX of SOILS
ASTM D 4829
**
Carmax Geo
10791.002
LB-3
B-1
Silty Sand (SM), brown.
MOLDED SPECIMEN
4.01 1.0000
Container No. 7
Specimen Diameter (in.)
Wt. Comp. Soil + Mold (gm.)
188.6
2.70 Wt. of Mold (gm.)
394.3
188.6
11.9 0.291
60.1 188.6
629.7
127.9
496.9
0.417
132.9
Elapsed Time
(min.)
Dial Readings
(in.)
48.5 77.9
Pressure
(psi)
217.8
0.294
60.9 Dry Wt. of Soil + Cont. (gm.)
7.5 517.8
Project Name: Tested By: MRV Date: 9/2/14
Project No. : Checked By: JHW Date: 9/4/14
Boring No.: Depth (ft.) 5.0 - 10.0
Sample No. : Location:
Sample Description:
Dry Wt. of Soil + Cont. (gm.)
Wt. of Container No. (gm.)
Dry Wt. of Soil (gm.)
Weight Soil Retained on #4 Sieve
Percent Passing # 4
in distilled water for the period of 24 h or expansion rate < 0.0002 in./h.
Rev. 03-08
39.1 0.347
71.8 Dry Wt. of Soil + Cont. (gm.)
10.0 339.1 646.9
121.1
311.8
0.531
134.8
Elapsed Time
(min.)
Dial Readings
(in.)
50.9 88.2
Pressure
(psi)
365.1
199.3
22.6 0.409
93.6 199.3
MOLDED SPECIMEN
4.01 1.0000
Container No. 8
Specimen Diameter (in.)
1.1053
646.9
EXPANSION INDEX of SOILS
ASTM D 4829
**
Carmax Geo
10791.002
LB-20
B-1
Elastic Silt (MH), yellowish brown.
Wt. Comp. Soil + Mold (gm.)
199.3
2.70 Wt. of Mold (gm.)
Specific Gravity (Assumed)
Specimen Height (in.)
100.0
4.01 2.70
3125.3
0.0 600.9
3125.3
0.0 Before Test After Test
Wet Wt. of Soil + Cont. (gm.)
8 0.692
Dry Density (pcf)
Wet Density (pcf)
1.0 Total Porosity
9/2/14
110.1
Moisture Content (%)
Date
10:50
Void Ratio
Pore Volume (cc)
Degree of Saturation (%) [ S meas]
Time
9/3/14 7:00
1.0 1.0
9/2/14 11:00 1.0
Expansion Index ( Report ) = Nearest Whole Number or Zero (0) if Initial Height is > than Final Height 106 Add Distilled Water to the Specimen
Wt. of Container (gm.)
110.0
0.5000
10 0.4998
SPECIMEN INUNDATION
9/3/14 0.6053
0 1140
Expansion Index (EI meas) = ((Final Rdg - Initial Rdg) / Initial Thick.) x 1000 6:00
1200 0.6053
105.5
Project Name: Tested By: MRV Date: 9/3/14
Project No. : Checked By: JHW Date: 9/4/14
Boring No.: Depth (ft.) 5.0 - 10.0
Sample No. : Location:
Sample Description:
Dry Wt. of Soil + Cont. (gm.)
Wt. of Container No. (gm.)
Dry Wt. of Soil (gm.)
Weight Soil Retained on #4 Sieve
Percent Passing # 4
in distilled water for the period of 24 h or expansion rate < 0.0002 in./h.
Rev. 03-08
419.3
0.291
60.3 Dry Wt. of Soil + Cont. (gm.)
7.5 719.3 634.1
128.5
698.4
0.411
133.6
Elapsed Time
(min.)
Dial Readings
(in.)
49.3 78.4
Pressure
(psi)
396.2
190.7
11.9 0.291
60.2 190.7
MOLDED SPECIMEN
4.01 1.0000
Container No. 4
Specimen Diameter (in.)
0.9997
634.1
EXPANSION INDEX of SOILS
ASTM D 4829
**
Carmax Geo
10791.002
LB-32
B-1
Silty, Clayey Sand (SC-SM), reddish brown.
Wt. Comp. Soil + Mold (gm.)
190.7
2.70 Wt. of Mold (gm.)
Specific Gravity (Assumed)
Specimen Height (in.)
100.0
4.01 2.70
3542.3
0.0 616.6
3542.3
0.0 Before Test After Test
Wet Wt. of Soil + Cont. (gm.)
4 0.410
Dry Density (pcf)
Wet Density (pcf)
1.0 Total Porosity
9/3/14
119.5
Moisture Content (%)
Date
12:15
Void Ratio
Pore Volume (cc)
Degree of Saturation (%) [ S meas]
Time
9/4/14 5:00
1.0 1.0
9/3/14 12:25 1.0
Expansion Index ( Report ) = Nearest Whole Number or Zero (0) if Initial Height is > than Final Height 0 Add Distilled Water to the Specimen
Wt. of Container (gm.)
119.4
0.5000
10 0.4999
SPECIMEN INUNDATION
9/4/14 0.4997
0 935
Expansion Index (EI meas) = ((Final Rdg - Initial Rdg) / Initial Thick.) x 1000 4:00
995 0.4997
-0.2
R-VALUE TEST RESULTS
CT 301
Project Name: Date: 9/2/14
Project Number: 10791.002 Technician: MRV
Boring Number: LB-11 Depth (ft.): 5.0 - 10.0
Sample Number: B-1 Sample Location:
Sample Description: Silty Sand with Trace Gravel (SM), brown.
TEST SPECIMEN A B C
MOISTURE AT COMPACTION % 8.3 9.9 11.4
HEIGHT OF SAMPLE, Inches 2.54 2.56 2.62
DRY DENSITY, pcf 131.0 130.1 124.4
COMPACTOR AIR PRESSURE, psi 175 105 25
EXUDATION PRESSURE, psi 438 326 167
EXPANSION, Inches x 10exp-4 12 0 0
STABILITY Ph 2,000 lbs (160 psi) 100 118 150
TURNS DISPLACEMENT 3.62 3.91 4.31
R-VALUE UNCORRECTED 29 19 4
R-VALUE CORRECTED 29 20 5
DESIGN CALCULATION DATA a b c
GRAVEL EQUIVALENT FACTOR 1.0 1.0 1.0
TRAFFIC INDEX 5.0 5.0 5.0
STABILOMETER THICKNESS, ft. 1.13 1.28 1.52
EXPANSION PRESSURE THICKNESS, ft. 0.45 0.00 0.00
EXPANSION PRESSURE CHART EXUDATION PRESSURE CHART
R-VALUE BY EXPANSION: 38
R-VALUE BY EXUDATION: 18
EQUILIBRIUM R-VALUE: 18
Rev. 08-04
Carmax Geo
**
0.00 0.50
1.00 1.50
2.00 2.50
3.00 3.50
4.00 COVER THICKNESS BY EXPANSION in feet
0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00
COVER THICKNESS BY STABILOMETER in
feet
0 10
20 30
40 50
60 70
80 90
800 700 600 500 400 300 200 100 0
R-VALUE
EXUDATION PRESSURE (psi)
R-VALUE TEST RESULTS
CT 301
Project Name: Date: 9/3/14
Project Number: 10791.002 Technician: MRV
Boring Number: LB-32 Depth (ft.): 5.0 - 10.0
Sample Number: B-1 Sample Location:
Sample Description: Silty Clayey Sand (SC-SM), reddish brown.
TEST SPECIMEN A B C
MOISTURE AT COMPACTION % 9.1 10.1 11.2
HEIGHT OF SAMPLE, Inches 2.47 2.61 2.56
DRY DENSITY, pcf 131.5 127.2 124.8
COMPACTOR AIR PRESSURE, psi 150 75 25
EXUDATION PRESSURE, psi 597 375 229
EXPANSION, Inches x 10exp-4 35 0 0
STABILITY Ph 2,000 lbs (160 psi) 106 125 147
TURNS DISPLACEMENT 3.35 3.91 4.03
R-VALUE UNCORRECTED 28 15 5
R-VALUE CORRECTED 28 16 5
DESIGN CALCULATION DATA a b c
GRAVEL EQUIVALENT FACTOR 1.0 1.0 1.0
TRAFFIC INDEX 5.0 5.0 5.0
STABILOMETER THICKNESS, ft. 1.16 1.34 1.52
EXPANSION PRESSURE THICKNESS, ft. 1.32 0.00 0.00
EXPANSION PRESSURE CHART EXUDATION PRESSURE CHART
R-VALUE BY EXPANSION: 25
R-VALUE BY EXUDATION: 11
EQUILIBRIUM R-VALUE: 11
Rev. 08-04
Carmax Geo
**
0.00 0.50
1.00 1.50
2.00 2.50
3.00 3.50
4.00 COVER THICKNESS BY EXPANSION in feet
0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00
COVER THICKNESS BY STABILOMETER in
feet
0 10
20 30
40 50
60 70
80 90
800 700 600 500 400 300 200 100 0
R-VALUE
EXUDATION PRESSURE (psi)
Geotechnical Exploration Report 10791.002
Proposed CarMax Automotive Dealership October 3, 2014
APPENDIX C
2013 CBC SEISMIC PARAMETERS & PAVEMENT DESIGN CALCULATIONS Design Maps Summary Report
IIUSGS Design Maps Summary Report
User-Specified Input
Report Title CarMax Murrieta
Man August 18, 2014 20:27 :05 UTC
Building Code Reference Document ASCE 7-10 Standard
(which utilizes USGS hazard data available in 2008)
Site Coordinates 33.55249°N, 117.18971 °W
Site Soil Classification Site Class D - "Stiff Soil"
Risk Category 1/II/III
f== l-----, 2mi '-----==-----' 5000m
mapquest
USGS-Provided Output
Ss = 2.060 g
51= 0.840 g
Me<;,=J de ,Ia
Punta
9 SMs = 2.060 g
SM1 = 1.260 g
®204.2 ~
Sos = 1.373 g
So1 = 0.840 g
For information on how the 55 and 51 values above have been calculated from probabilistic (risk-targeted) and deterministic ground motions in the direction of maximum horizontal response, please return to the application and select the "2009 NEHRP" building code reference document. -;,
II
Ill
MCE" Response Spectrum
2.10 l.B~
1. ~B
1. 47
1. 2(;
1. 05
0. 94
~3
0. 42
0. 21
0. 00 -l---l--+--+--+--+--+--+-+------1f------1 0. 00 0. 20 0.40 O.GO O.SO 1.00 1.20 1.40 l.GO 1.80 2. 00 Period, T (sec)
iii
Ill
Ill
For PGAM, TL, c.s, and c., values, please view the detajled reoort.
Design Response Spectrum
1. 40
1.2(;
1.12 0.98
0.84 0. 70
0,5(;
0.42 0.29
0.14 0.00 +---1---1- +---t--+-~1--+--+--t---i
0. 00 0.20 0.40 O. tiO O.BO 1.00 L 20 1. 40 l. tiO l.BO 2.00 Period, T (sec)
http://ehp3-earthquake.wr.usgs.gov/designmaps/us/summary.php?template=minimal&latit... 8/18/2014 Design Maps Summary Report Page 2 of2
Although this information is a product of the U.S. Geological Survey, we provide no warranty, expressed or implied, as to the accuracy of the data contained therein . This tool is not a substitute for technical subject-matter knowledge. http:/ /ehp3-earthquake. wr. usgs.gov/designmaps/us/ summary .php ?template=minimal&latit... 8/18/2014 Design Maps Detailed Report
EIJSGS Design Maps Detailed Report
ASCE 7-10 Standard (33.55249°N, 117.18971°W)
Site Class D -"Stiff Soil", Risk Category I/II/III
Section 11.4.1 - Mapped Acceleration Parameters
Note: Ground motion values provided below are for the direction of maximum horizontal spectral response acceleration. They have been converted from corresponding geometric mean ground motions computed by the USGS by applying factors of 1.1 (to obtain Ss) and
1.3 (to obtain S1). Maps in the 2010 ASCE-7 Standard are provided for Site Class B.
Adjustments for other Site Classes are made, as needed, in Section 11.4.3.
From Figure 22-1 [lJ Ss = 2.060 g
From Figure 22-2 £
21 51= 0.840 g
Section 11.4.2- Site Class
The authority having jurisdiction (not the USGS), site-specific geotechnical data, and/or the default has classified the site as Site Class D, based on the site soil properties in accordance with Chapter 20.
Table 20.3-1 Site Classification
Site Class Nor Nch - Vs Su
A. Hard Rock >5,000 ft/S N/A N/A
B. Rock 2,500 to 5,000 ft/s N/A N/A
C. Very dense soil and soft rock 1,200 to 2,500 ft/s >50 >2,000 psf D. Stiff Soil 600 to 1,200 ft/s 15 to 50 1,000 to 2,000 psf E. Soft clay soil <600 ft/s <15 <1,000 psf
Any profile with more than 10 ft of soil having the characteristics :
--- F. Soils requiring site response
analysis in accordance with Section
21.1 • Plasticity index PI> 20,
• Moisture content w <::: 40%, and
• Undrained shear strength Su < 500 psf
See Section 20.3.1
For SI: lft/s = 0.3048 m/s llb/ft2 = 0.0479 kN/m 2
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Section 11.4.3 - Site Coefficients and Risk-Targeted Maximum Considered Earthquake C.M.~S.I!) Spectral Response Acceleration Parameters
Table 11.4-1: Site Coefficient F.
Site Class Mapped MCE R Spectral Response Acceleration Parameter at Short Period Ss :::; 0.25 Ss = 0.50 Ss = 0.75 Ss = 1.00 Ss ~ 1.25
A 0.8 0.8 0.8 0.8 0.8
B 1.0 1.0 1.0 1.0 1.0
c 1.2 1.2 1.1 1.0 1.0
D 1.6 1.4 1.2 1.1 1.0
E 2.5 1.7 1.2 0.9 0.9
F See Section 11.4. 7 of ASCE 7
Note: Use straight-line interpolation for intermediate values of Ss For Site Class = D and Ss = 2.060 g, F. = 1.000
Table 11.4-2: Site Coefficient F.
Site Class Mapped MCE R Spectral Response Acceleration Parameter at 1-s Period 51:::; 0.10 51= 0.20 51= 0.30 51 = 0.40 51~ 0.50
A 0.8 0.8 0.8 0.8 0.8
B 1.0 1.0 1.0 1.0 1.0
c 1.7 1.6 1.5 1.4 1.3
D 2.4 2.0 1.8 1.6 1.5
E 3.5 3.2 2.8 2.4 2.4
F See Section 11.4. 7 of ASCE 7
Note: Use straight-line interpolation for intermediate values of S1 For Site Class= D and 5 1 = 0.840 g, F.= 1.500
http:/ /ehp3 -earthquake. wr. usgs. gov /designmaps/us/report. php ?template=minimal&latitude... 8/18/2014 Design Maps Detailed Report
Equation {11.4-1): SMs = F.Ss = 1.000 X 2.060 = 2.060 g Equation (11.4-2): SMl = fvSl = 1.500 X 0.840 = 1.260 Q Section 11.4.4 - Design Spectral Acceleration Parameters Equation (11.4-3): Sos =% SMs =%X 2.060 = 1.373 g
Equation {11.4-4): So1 = % SMl =%X 1.260 = 0.840 g
Section 11.4.5- Design Response Spectrum
From Figure 22-12 [lJ TL = 8 seconds
II
Ill
c
0 'i
..
Ill
'ii
lol
lol
<
Ill
111
c
0 ~
111
Ill
a:
iii
-a
Ill
~
Ill
Figure 11.4- 1: Design Response Spectrum
Scr-, = 1.373
s~ 1 = o.a4o
Ta = 0.122 T, = 0.612 1.000
T < T0 : s. = 506 ( 0.4 + 0.6 T I T0 )
T0 ::!iT::!i T8 : s. =S08
TB < T ::!i TL: s. =so,/ T
Period, T (sec)
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Section 11.4.6 - Risk-Targeted Maximum Considered Earthquake (MCER) Response Spectrum
The MCE. Response Spectrum is determined by multiplying the design response spectrum above by
1.5. Ill
til
c
0 i
..
Ill
'i
s"'S = 2.060
~ 5,.1=1.260 - -----------
<
.,
Ill
c
0 II.
Ill
Ill
a:
ii
..
t
Ill
II.
til
Ts = 0. 612 1. 000
Period, T (sec)
http:/ /ehp3-earthquake. wr. usgs.gov I designmaps/us/report. php ?template=minimal&latitude... 8/18/2014 Design Maps Detailed Report Page 5 of6
Section 11.8.3 -Additional Geotechnical Investigation Report Requirements for Seismic Design Categories D through F
From Figure 22-7 [
41 PGA = 0.837
Equation (11.8-1): PGAM = FPGAPGA = 1.000 X 0.837 = 0.837 g Table 11.8-1: Site Coefficient F PGA
Site Mapped MCE Geometric Mean Peak Ground Acceleration, PGA Class
PGA:::; PGA = PGA = PGA = PGA ~
0.10 0.20 0.30 0.40 0.50
A 0.8 0.8 0.8 0.8 0.8
B 1.0 1.0 1.0 1.0 1.0
c 1.2 1.2 1.1 1.0 1.0
D 1.6 1.4 1.2 1.1 1.0
E 2.5 1.7 1.2 0.9 0.9
F See Section 11.4. 7 of ASCE 7
Note: Use straight-line interpolation for intermediate values of PGA For Site Class= D and PGA = 0.837 g, FPGA = 1.000
Section 21.2.1.1 - Method 1 (from Chapter 21 - Site-Specific Ground Motion Procedures for Seismic Design)
From Figure 22-17 tsJ CRs = 0.902
From Figure 22-18 teJ C Rl = 0.886
http:/ /ehp3-earthquake. wr. usgs. gov/ designmaps/us/report.php ?template=minimal&latitude... 8/18/20 14 Design Maps Detailed Report
Section 11.6 - Seismic Design Category
Table 11.6-1 Seismic Design Category Based on Short Period Response Acceleration Parameter
RISK CATEGORY
VALUE OF Sos
I or II III IV
Sos < 0.167g A A A
0.167g S Sos < 0.33g B B c
0.33g S Sos < O.SOg c c D
O.SOg S Sos D D D
For Risk Category= I and Sos = 1.373 g, Seismic Design Category= D Table 11 6-2 Seismic Design Category Based on 1-S Period Response Acceleration Parameter
RISK CATEGORY
VALUE OF Sol
I or II III IV
Sol< 0.067g A A A
0.067g S Sol < 0.133g B B c
0.133g S So1 < 0.20g c c D
0.20g S Sol D D D
For Risk Category = I and S0 , = 0.840 g, Seismic Design Category = D Note: When S1 is greater than or equal to 0. 75g, the Seismic Design Category is E for buildings in Risk Categories I, II, and III, and F for those in Risk Category IV, irrespective of the above.
Seismic Design Category = "the more severe design category in accordance with Table 11.6-1 or 11.6-2" = E
Note: See Section 11.6 for alternative approaches to calculating Seismic Design Category.
References
1. Figure 22-1:
http:/ /earthquake.usgs.gov /hazards/designmaps/downloads/pdfs/20 10_ASCE-7 _Figure_22-l.pdf
2. Figure 22-2:
http:/ /earthquake. usgs.gov /hazards/desig nmaps/down loads/pdfs/20 1 O_ASCE-7 _Figure_22-2. pdf
3. Figure 22-12: http:/ /earthquake.usgs.gov/hazards/designmaps/downloads/pdfs/20 10_ASCE-7 _Figure_22-
12.pdf
4. Figure 22-7:
http:/ /earthquake.usgs.gov/hazards/designmaps/downloads/pdfs/2010_ASCE-7 _Figure_22-7. pdf
5. Figure 22-17: http:/ /earthquake.usgs.gov /hazards/designmaps/downloads/pdfs/2010_ASCE-7 _Figure_22-
17.pdf
6. Figure 22-18: http:/ /earthquake.usgs.gov /hazards/designmaps/downloads/pdfs/20 10_ASCE-7 _Figure_22-
18.pdf
http://ehp3-earthquake.wr.usgs.gov/designmaps/us/report.php?template=minimal&latitude... 8/18/2014 CaltranPVMT'2layers
Proposed CarMax Automotive Dealership Project No.:
Date:
Design Methodolgy:
DATA:
TRAFFIC INDEX TI = 6.5
NA Tac= 4 inches
GF AC (Table 608.4) GFac= 2.14
GF BASE (Table 608.4) GFba= 1.1
R-VALUE (base) Rba= 80
R-VALUE (subgrade) Rsb= 15
GRAVEL EQUIVALENT
= 1.77 feet
= 0.71 feet
GE for BASE (TOTAL - AC) 1.05 feet
Pavement Section (INCHES)
= 4.0 inches
= 11.5 inches
GE needed for total pavement section
GE=.0032(TI)(100-R)
GE for AC section (Tac*GFac/12)
AC Thickness
BASE Thickness
CALTRAN Highway Design Manual, Chapter 630, May 7, 2012 (assumed)
AC Thickness
(Class II)
(Lab Testing)
PAVEMENT DESIGN CALCULATIONS
Project Name: 10791.002
Location: Murrieta, CA 9/15/2014
CaltranPVMT'2layers
Proposed CarMax Automotive Dealership Project No.:
Date:
Design Methodolgy:
DATA:
TRAFFIC INDEX TI = 5
NA Tac= 4 inches
GF AC (Table 608.4) GFac= 2.54
GF BASE (Table 608.4) GFba= 1.1
R-VALUE (base) Rba= 80
R-VALUE (subgrade) Rsb= 15
GRAVEL EQUIVALENT
= 1.36 feet
= 0.85 feet
GE for BASE (TOTAL - AC) 0.51 feet
Pavement Section (INCHES)
= 4.0 inches
= 5.6 inches
GE needed for total pavement section
GE=.0032(TI)(100-R)
GE for AC section (Tac*GFac/12)
AC Thickness
BASE Thickness
CALTRAN Highway Design Manual, Chapter 630, May 7, 2012 (assumed)
AC Thickness
(Class II)
(Lab Testing)
PAVEMENT DESIGN CALCULATIONS
Project Name: 10791.002
Location: Murrieta, CA 9/15/2014
CaltranPVMT'2layers
Proposed CarMax Automotive Dealership Project No.:
Date:
Design Methodolgy:
DATA:
TRAFFIC INDEX TI = 4.5
NA Tac= 4 inches
GF AC (Table 608.4) GFac= 2.54
GF BASE (Table 608.4) GFba= 1.1
R-VALUE (base) Rba= 80
R-VALUE (subgrade) Rsb= 15
GRAVEL EQUIVALENT
= 1.22 feet
= 0.85 feet
GE for BASE (TOTAL - AC) 0.38 feet
Pavement Section (INCHES)
= 4.0 inches
= 4.1 inches
AC Thickness
BASE Thickness
GE for AC section (Tac*GFac/12)
10791.002
9/15/2014
CALTRAN Highway Design Manual, Chapter 630, May 7, 2012 (assumed)
(Lab Testing)
AC Thickness
(Class II)
PAVEMENT DESIGN CALCULATIONS
Project Name:
Location: Murrieta, CA
GE=.0032(TI)(100-R)
GE needed for total pavement section
Geotechnical Exploration Report 10791.002
Proposed CarMax Automotive Dealership October 3, 2014
APPENDIX D
EARTHWORK AND GRADING SPECIFICATIONS
D-1
A P P E N D I X D
E A R T H W O R K A N D G R A D I N G S P E C I F I C A T I O N S
T A B L E O F C O N T E N T S
Section Page
D-1.0 GENERAL ....................................................................................................................................................2 D-1.1 INTENT .......................................................................................................................................................2 D-1.2 ROLE OF LEIGHTON CONSULTING, INC. .......................................................................................................2 D-1.3 THE EARTHWORK CONTRACTOR ................................................................................................................2 D-2.0 PREPARATION OF AREAS TO BE FILLED.........................................................................................3 D-2.1 CLEARING AND GRUBBING .........................................................................................................................3 D-2.2 PROCESSING ...............................................................................................................................................3 D-2.3 OVEREXCAVATION .....................................................................................................................................4 D-2.4 BENCHING ..................................................................................................................................................4 D-2.5 EVALUATION/ACCEPTANCE OF FILL AREAS................................................................................................4 D-3.0 FILL MATERIAL .......................................................................................................................................4 D-3.1 FILL QUALITY .............................................................................................................................................4 D-3.2 OVERSIZE ...................................................................................................................................................4 D-3.3 IMPORT.......................................................................................................................................................5 D-4.0 FILL PLACEMENT AND COMPACTION .............................................................................................5 D-4.1 FILL LAYERS...............................................................................................................................................5 D-4.2 FILL MOISTURE CONDITIONING ..................................................................................................................5 D-4.3 COMPACTION OF FILL ................................................................................................................................. 5 D-4.4 COMPACTION OF FILL SLOPES.....................................................................................................................6 D-4.5 COMPACTION TESTING ...............................................................................................................................6 D-4.6 COMPACTION TEST LOCATIONS..................................................................................................................6 D-5.0 EXCAVATION ............................................................................................................................................6 D-6.0 TRENCH BACKFILLS ..............................................................................................................................6 D-6.1 SAFETY.......................................................................................................................................................6 D-6.2 BEDDING AND BACKFILL ............................................................................................................................6 D-6.3 LIFT THICKNESS .........................................................................................................................................7
S T A N D A R D D E T A I L S
A - Keying and Benching Rear of Text
B - Oversize Rock Disposal Rear of Text
D - Buttress or Replacement Fill Subdrains Rear of Text E - Transition Lot Fills and Side Hill Fills Rear of Text Retaining Wall Rear of Text
Leighton Consulting, Inc. Earthwork and Grading Guide Specifications D-2
D - 1 . 0 G E N E R A L
D-1.1 Intent
These Earthwork and Grading Guide Specifications are for grading and earthwork shown on the current, approved grading plan(s) and/or indicated in the Leighton Consulting, Inc. geotechnical report(s). These Guide Specifications are a part of the recommendations contained in the geotechnical report(s). In case of conflict, the project-specific recommendations in the geotechnical report shall supersede these Guide Specifications. Leighton Consulting, Inc. shall provide geotechnical observation and testing during earthwork and grading. Based on these observations and tests, Leighton Consulting, Inc. may provide new or revised recommendations that could supersede these specifications or the recommendations in the geotechnical report(s).
D-1.2 Role of Leighton Consulting, Inc.
Prior to commencement of earthwork and grading, Leighton Consulting, Inc. shall meet with the earthwork contractor to review the earthwork contractor’s work plan, to schedule sufficient personnel to perform the appropriate level of observation, mapping and compaction testing.
During earthwork and grading, Leighton Consulting, Inc. shall observe, map, and document subsurface exposures to verify geotechnical design assumptions. If observed conditions are found to be significantly different than the interpreted assumptions during the design phase, Leighton Consulting, Inc. shall inform the owner, recommend appropriate changes in design to accommodate these observed conditions, and notify the review agency where required.
Subsurface areas to be geotechnically observed, mapped, elevations recorded, and/or tested include (1) natural ground after clearing to receiving fill but before fill is placed, (2) bottoms of all "remedial removal" areas, (3) all key bottoms, and (4) benches made on sloping ground to receive fill.
Leighton Consulting, Inc. shall observe moisture-conditioning and processing of the subgrade and fill materials, and perform relative compaction testing of fill to determine the attained relative compaction. Leighton Consulting, Inc. shall provide Daily Field Reports to the owner and the Contractor on a routine and frequent basis.
D-1.3 The Earthwork Contractor
The earthwork contractor (Contractor) shall be qualified, experienced and knowledgeable in earthwork logistics, preparation and processing of ground to receive fill, moisture-conditioning and processing of fill, and compacting fill. The Contractor shall review and accept the plans, geotechnical report(s), and these Guide Specifications prior to commencement of grading. The Contractor shall be solely responsible for performing grading and backfilling in accordance with the current, approved plans and specifications.
Leighton Consulting, Inc. Earthwork and Grading Guide Specifications D-3
The Contractor shall inform the owner and Leighton Consulting, Inc. of changes in work schedules at least one working day in advance of such changes so that appropriate observations and tests can be planned and accomplished. The Contractor shall not assume that Leighton Consulting, Inc. is aware of all grading operations.
The Contractor shall have the sole responsibility to provide adequate equipment and methods to accomplish earthwork and grading in accordance with the applicable grading codes and agency ordinances, these Guide Specifications, and recommendations in the approved geotechnical report(s) and grading plan(s). If, in the opinion of Leighton Consulting, Inc., unsatisfactory conditions, such as unsuitable soil, improper moisture condition, inadequate compaction, adverse weather, etc., are resulting in a quality of work less than required in these specifications, Leighton Consulting, Inc. shall reject the work and may recommend to the owner that earthwork and grading be stopped until unsatisfactory condition(s) are rectified.
D - 2 . 0 P R E P A R A T I O N O F A R E A S T O B E F I L L E D D-2.1 Clearing and Grubbing
Vegetation, such as brush, grass, roots and other deleterious material shall be sufficiently removed and properly disposed of in a method acceptable to the owner, governing agencies and Leighton Consulting, Inc.. Care should be taken not to encroach upon or otherwise damage native and/or historic trees designated by the Owner or appropriate agencies to remain.
Pavements, flatwork or other construction should not extend under the “drip line” of designated trees to remain.
Leighton Consulting, Inc. shall evaluate the extent of these removals depending on specific site conditions. Earth fill material shall not contain more than 3 percent of organic materials (by dry weight: ASTM D 2974-00). Nesting of the organic materials shall not be allowed.
If potentially hazardous materials are encountered, the Contractor shall stop work in the affected area, and a hazardous material specialist shall be informed immediately for proper evaluation and handling of these materials prior to continuing to work in that area. As presently defined by the State of California, most refined petroleum products (gasoline, diesel fuel, motor oil, grease, coolant, etc.) have chemical constituents that are considered to be hazardous waste. As such, the indiscriminate dumping or spillage of these fluids onto the ground may constitute a misdemeanor, punishable by fines and/or imprisonment, and shall not be allowed.
D-2.2 Processing
Existing ground that has been declared satisfactory for support of fill, by Leighton Consulting, Inc., shall be scarified to a minimum depth of 6 inches (15 cm). Existing ground that is not satisfactory shall be overexcavated as specified in the following Section D-2.3. Scarification Leighton Consulting, Inc. Earthwork and Grading Guide Specifications D-4
shall continue until soils are broken down and free of large clay lumps or clods and the working surface is reasonably uniform, flat, and free of uneven features that would inhibit uniform compaction.
D-2.3 Overexcavation
In addition to removals and overexcavations recommended in the approved geotechnical report(s) and the grading plan, soft, loose, dry, saturated, spongy, organic-rich, highly fractured or otherwise unsuitable ground shall be overexcavated to competent ground as evaluated by Leighton Consulting, Inc. during grading. All undocumented fill soils under proposed structure footprints should be excavated
D-2.4 Benching
Where fills are to be placed on ground with slopes steeper than 5:1 (horizontal to vertical units), (>20 percent grade) the ground shall be stepped or benched. The lowest bench or key shall be a minimum of 15 feet (4.5 m) wide and at least 2 feet (0.6 m) deep, into competent material as evaluated by Leighton Consulting, Inc.. Other benches shall be excavated a minimum height of 4 feet (1.2 m) into competent material or as otherwise recommended by Leighton Consulting, Inc..
Fill placed on ground sloping flatter than 5:1 (horizontal to vertical units), (<20 percent grade) shall also be benched or otherwise overexcavated to provide a flat subgrade for the fill.
D-2.5 Evaluation/Acceptance of Fill Areas
All areas to receive fill, including removal and processed areas, key bottoms, and benches, shall be observed, mapped, elevations recorded, and/or tested prior to being accepted by Leighton Consulting, Inc. as suitable to receive fill. The Contractor shall obtain a written acceptance (Daily Field Report) from Leighton Consulting, Inc. prior to fill placement. A licensed surveyor shall provide the survey control for determining elevations of processed areas, keys, and benches.
D - 3 . 0 F I L L M A T E R I A L
D-3.1 Fill Quality
Material to be used as fill shall be essentially free of organic matter and other deleterious substances evaluated and accepted by Leighton Consulting, Inc. prior to placement. Soils of poor quality, such as those with unacceptable gradation, high expansion potential, or low strength shall be placed in areas acceptable to Leighton Consulting, Inc. or mixed with other soils to achieve satisfactory fill material.
D-3.2 Oversize
Oversize material defined as rock, or other irreducible material with a maximum dimension greater than 6 inches (15 cm), shall not be buried or placed in fill unless location, materials and placement methods are specifically accepted by Leighton Consulting, Inc.. Placement operations Leighton Consulting, Inc. Earthwork and Grading Guide Specifications D-5
shall be such that nesting of oversized material does not occur and such that oversize material is completely surrounded by compacted or densified fill. Oversize material shall not be placed within 10 feet (3 m) measured vertically from finish grade, or within 2 feet (0.61 m) of future utilities or underground construction.
D-3.3 Import
If importing of fill material is required for grading, proposed import material shall meet the requirements of Section D-3.1, and be free of hazardous materials (“contaminants”) and rock larger than 3-inches (8 cm) in largest dimension. All import soils shall have an Expansion Index (EI) of 20 or less and a sulfate content no greater than () 500 parts-per-million (ppm). A representative sample of a potential import source shall be given to Leighton Consulting, Inc. at least four full working days before importing begins, so that suitability of this import material can be determined and appropriate tests performed.
D - 4 . 0 F I L L P L A C E M E N T A N D C O M P A C T I O N D-4.1 Fill Layers
Approved fill material shall be placed in areas prepared to receive fill, as described in Section D2.0, above, in near-horizontal layers not exceeding 8 inches (20 cm) in loose thickness. Leighton Consulting, Inc. may accept thicker layers if testing indicates the grading procedures can adequately compact the thicker layers, and only if the building officials with the appropriate jurisdiction approve. Each layer shall be spread evenly and mixed thoroughly to attain relative uniformity of material and moisture throughout.
D-4.2 Fill Moisture Conditioning
Fill soils shall be watered, dried back, blended, and/or mixed, as necessary to attain a relatively uniform moisture content at or slightly over optimum. Maximum density and optimum soil moisture content tests shall be performed in accordance with the American Society of Testing and Materials (ASTM) Test Method D 1557.
D-4.3 Compaction of Fill
After each layer has been moisture-conditioned, mixed, and evenly spread, it shall be uniformly compacted to not less than 90 percent of maximum dry density as determined by ASTM Test Method D 1557. For fills thicker than 15 feet (4.5 m), the portion of the fill deeper than 15 feet below proposed finish grade shall be compacted to 95 percent of the ASTM D 1557 laboratory maximum density. Compaction equipment shall be adequately sized and be either specifically designed for soil compaction or of proven reliability to efficiently achieve the specified level of compaction with uniformity.
Leighton Consulting, Inc. Earthwork and Grading Guide Specifications D-6
D-4.4 Compaction of Fill Slopes
In addition to normal compaction procedures specified above, compaction of slopes shall be accomplished by backrolling of slopes with sheepsfoot rollers at increments of 3 to 4 feet (1 to
1.2 m) in fill elevation, or by other methods producing satisfactory results acceptable to Leighton Consulting, Inc.. Upon completion of grading, relative compaction of the fill, out to the slope face, shall be at least 90 percent of the ASTM D 1557 laboratory maximum density.
D-4.5 Compaction Testing
Field-tests for moisture content and relative compaction of the fill soils shall be performed by Leighton Consulting, Inc.. Location and frequency of tests shall be at our field representative(s) discretion based on field conditions encountered. Compaction test locations will not necessarily be selected on a random basis. Test locations shall be selected to verify adequacy of compaction levels in areas that are judged to be prone to inadequate compaction (such as close to slope faces and at the fill/bedrock benches).
D-4.6 Compaction Test Locations
Leighton Consulting, Inc. shall document the approximate elevation and horizontal coordinates of each density test location. The Contractor shall coordinate with the project surveyor to assure that sufficient grade stakes are established so that Leighton Consulting, Inc. can determine the test locations with sufficient accuracy. Adequate grade stakes shall be provided.
D - 5 . 0 E X C A V A T I O N
Excavations, as well as over-excavation for remedial purposes, shall be evaluated by Leighton Consulting, Inc. during grading. Remedial removal depths shown on geotechnical plans are estimates only. The actual extent of removal shall be determined by Leighton Consulting, Inc. based on the field evaluation of exposed conditions during grading. Where fill-over-cut slopes are to be graded, the cut portion of the slope shall be made, evaluated, and accepted by Leighton Consulting, Inc. prior to placement of materials for construction of the fill portion of the slope, unless otherwise recommended by Leighton Consulting, Inc..
D - 6 . 0 T R E N C H B A C K F I L L S
D-6.1 Safety
The Contractor shall follow all OSHA and Cal/OSHA requirements for safety of trench excavations. Work should be performed in accordance with Article 6 of the California Construction Safety Orders, 2003 Edition or more current.
D-6.2 Bedding and Backfill
All bedding and backfill of utility trenches shall be performed in accordance with the applicable provisions of Standard Specifications of Public Works Construction. Bedding material shall Leighton Consulting, Inc. Earthwork and Grading Guide Specifications D-7
have a Sand Equivalent greater than 30 (SE>30). Bedding shall be placed to 1-foot (0.3 m) over the top of the conduit, and densified by jetting. Backfill shall be placed and densified to a minimum of 90 percent of relative compaction (ASTM D 1557) from 1 foot (0.3 m) above the top of the conduit to the surface. Jetting of the bedding around the conduits shall be observed by Leighton Consulting, Inc. and backfill above the pipe zone (bedding) shall be observed and tested by Leighton Consulting, Inc..
D-6.3 Lift Thickness
Lift thickness of trench backfill shall not exceed those allowed in the Standard Specifications of Public Works Construction unless the Contractor can demonstrate to Leighton Consulting, Inc. that the fill lift can be compacted to the minimum relative compaction by his alternative equipment and method, and only if the building officials with the appropriate jurisdiction approve.
All. SLOPE
PROJECTED PLANE 1: 1
(HORIZONTAL: VERTICAL)
MAXIMUM FROM TOE
OF SLOPE TO
APPROVED GROUND
EXISTING
GROUND SURFACE
Rll. -ovet-cur SLOPE
CUT -ovER-ALl. SLOPE
PROJECTED PLANE
1 TO 1 MAXIMUM
FROM TOE OF SLOPE
TO APPROVED GROUND
KEYING AND BENCHING
REMOVE
UNSUITABLE
MATERIAL
REMOVE
UNSUITABLE
MATERIAL
UT FACE SHALL BE
CONSTRUCTED PRIOR
TO FILL PLACEMENT
BENCHING SHALL BE DONE WHEN SLOPE'S
ANGLE IS EQUAL TO OR GREATER THAN 5: 1.
MINIMUM BENCH HEIGHT SHALL BE 4 FEET
AND MINIMUM FILL WIDTH SHALL BE 9 FEET.
GENERAL EARTHWORK AND GRADING
SPECIFICATIONS
STANDARD DETAILS A Leighton
FINISH GRADE
_____________ - - - - - - "10'- - - - - - - - - - - - COMPACTED FILl_ - - - - - - - - - - - - - - MIN.- - - - - - - - - - - - - - -
------~---------------~-- - --=-=-=-=-=-=-=-=-~-=-=-=-=-=-=-=-=-=-=-=-=-=-=-= _____ ----------- - --=-=-=-=-=~=n-=-=-=-=-=-~0.-=-=-=-=-=-=-="--.J--~ ?--/_------ ______________________ ------------- - ------------------_ _- -_-_-_-_-_-_ ---~----=-~=-7)---_-_-_-_-_-~_-_-_-_- - -_-_-_-_-,C_-_-_\Jo----~-~----_-_-_-_---:J-_/o----_- _-_-_~~~~----/----_-_-_-_-_-_-_ -, . _-:_-!-:----~.~N~--~t.-------- _____ -~ _____ - - - - - 4 MIN. - - - - - - - - -_-_-_-_-_-_-_ ----y-~-------------- ----~---_-_-_-_-_-/\~----_-_-_-_-_-_-_-_- -------- ------- -- ------ ~-....,r--_---------- _-_-_-_-_--7-----_-_-_- _- -_-_-_-_-__ -_-_-_-_-_-_-_-_-_-- - - - 7 - - - - - - - - OVERSIZE - - - - - - - - - - --------_-_-_-_-_-_-_-_-_-WINDROW·_-_-_-_---.
~-~--------------
• Oversize rock is larger than 8 inches
in largest dimension.
• Backfill with approved soil jetted or
flooded in place to fill all the voids.
• Do not bury rock within 10 feet of
finish grade.
• Windrow of buried rock shall be
parallel to the finished slope face.
PROFILE ALONG WINDROW
-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=--:A~ := --:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:=-:= -~ ~-:=-:=-:=-:=-:=-:=-:=-:=--:=-:=-:=-:=-:=-:=-:=-:=-A'~:=-_-:=-:=-:=-:=-:=-:=-:=-:=-:=-~----_-_-_-
JETTED OR FLOODED
APPROVED SOIL
~
f
.li
i ~--------------------~--------------~--------~!
OVERSIZE ROCK DISPOSAL
GENERAL EARTHWORK AND GRADING
SPEOFICATIONS
STANDARD DETAILS B Leighton
I
E
i
I L_------------------------------------~~------------------------~L-------------------~~ 1'±
OUTLET PIPES
4"+ NON-PERFORATED PIPE,
100' MAX. O.C. HORIZONTALLY
30' MAX. O.C. VERTICALLY
------------------
------------------- ------------------ - ---------------2% MIN.~------ --- I ,15' MIN; I
BACK CUT
SUBDRAIN ALTERNATE B =?J -----======~~~~==========-=--== 0 KEY DEPTH I . K~· ~~~TH I
2' MIN.
SUBDRAIN ALTERNATE A
CAL TRANS QASS 2
FILTER MATERIAL (3FT.3/FT)
H:ONNECTION FROM
COUECTION PIPE TO OUTLET PIPE
POSmvE SEAL SHOULD BE PROVIDED----...
AT THE JOINT
3/4" ROO< (3FT31Ffl------
WRAPPED IN FILTER
• SUBDRAIN INSTALLATION - Subdrain collector pipe shall be installed with perforations down or, unless otherwise designated by the geotechnical consultant. Outlet pipes shall be non-perforated pipe. The subdrain pipe shall have at least 8 perforations uniformly spaced per foot. Perforation shall •
be 1/4" to 1/2" if drilled holes are used. All subdrain pipes shall have a gradient at least 2% towards the outlet.
~ SUBDRAIN PIPE - Subdrain pipe shall be ASTM D2751, ASTM D1527 (Schedule 40) or SDR 23.5 ABS pipe ! or ASTM D3034 (Schedule 40) or SDR 23.5 PVC pipe. -
•
All outlet pipe shall be placed in a trench and, after fill is placed above it, rodded to verify integrity. ~ f------------r----------.----i ~
BUTTRESS OR
REPLACEMENT FILL
SUBDRAINS
GENERAL EARTHWORK AND GRADING
SPECIFICATIONS
STANDARD DETAILS D
.,
Leighton i ~---------------~---------------L---------~~ "
OVERBURDEN
OR UNSUITABLE
MATERIAL
CUT-FILL TRANSITION LOT OVEREXCAVATION
---- ----
REMOVE
UNSUITABLE\_
GROUND \...-
___..
---- ----
----
----
SIDE HILL FILL FOR CUT PAD NATIJRAL
GROUND~ .....-
OVEREXCAVATE
AND RECOMPACT
{REPLACEMENT FILL)
.....-
---- ---- /
/ FINISHED QJT PAD
/
L...:::::::~~..-U<------- SEE STANDARD DETAIL FOR SUBDRAINS ~' Ml~. •I WHEN REQUIRED BY GEOTR:HNICAL CONSULTANT
~ UNWEATHERED BEDROCK OR MATERIAL APPROVED
BY THE GEOTR:HNICAL CONSULTANT
~
t
..Ill
~ :8
~------------------------------------~~------------------------~~------------------~1
TRANSITION LOT FILLS
AND SIDE HILL FILLS
GENERAL EARTHWORK AND GRADING
SPEOFICATIONS
STANDARD DETAILS E Leighton
I
E
i
I ~------------------------------------~~------------------------~~------------------~~ SUBDRAIN OPTIONS AND BACKFILL WHEN NATIVE MATERIAL HAS EXPANSION INDEX OF ~0 OPTION 1: PIPE SURROUNDED WITH
CLASS 2 PERMEABLE MATERIAL OPTION 2: GRAVEL WRAPPED
IN FILTER FABRIC
. LEVEL OR
SLOPE
GENERAL NOTES:
SLOPE
OR LEVEL
12" MINIMUM
CLASS 2 PERMEABLE
FILTER MATERIAL
(SEE GRADATION)
4 INCH DIAMETER
PERFORATED PIPE
(SEE NOTE 3)
WATERPROOFING ----+--1
(SEE GENERAL NOTES)
Class 2 Filter Permeable Material Gradation
Per caltrans Specifications
Sieve Size Percent Passing
1" 100
3/4" 90-100
3/8" 40-100
No.4 25-40
No.8 18-33
No. 30 5-15
No. so 0-7
No. 200 D-3
* Waterproofing should be provided where moisture nuisance problem through the wall is undesirable. * Water proofing of the walls is not under purview of the geotechnical engineer * All drains should have a gradient of 1 percent minimum SLOPE
OR LEVEL
Fll TER FABRIC
(SEE NOTE4)
*Outlet portion of the subdrain should have a 4-inch diameter solid pipe discharged into a suitable disposal area designed by the project engineer. The subdrain pipe should be accessible for maintenance (rodding) *Other subdrain backfill options are subject to the review by the geotechnical engineer and modification of design parameters.
Notes:
1) Sand should have a sand equivalent of 30 or greater and may be densified by water jetting. 2) 1 Cu. ft. per ft. of 1/+ to 1 1/2-inch size gravel wrapped in filter fabric 3) Pipe type should be ASTM 01527 Acrylonitrile Butadiene Styrene (ABS) SDR35 or ASTM 01785 Polyvinyl Chloride plastic (PVC), Schedule 40, Armco A2000 PVC, or approved equivalent. Pipe should be installed with perforations down. Perforations should be 3/8 inch in diameter placed at the ends of a 120-degree arc in two rows at 3-inch on center (staggered) 4) Filter fabric should be Mirafi 140NC or approved equivalent. 5) Weephole should be 3-inch minimum diameter and provided at 10-foot maximum intervals. If exposure is permitted, weepholes should be located 12 inches above finished grade. If exposure is not permitted such as for a wall adjacent to a sidewalk/curb, a pipe under the sidewalk to be discharged through the curb face or equivalent should be provided. For a basement-type wall, a proper subdrain outlet system should be provided.
6) Retaining wall plans should be reviewed and approved by the geotechnical engineer. 7) Walls over six feet in height are subject to a special review by the geotechnical engineer and modifications to the above requirements.
RETAINING WALL BACKFILL AND SUBDRAIN DETAIL
FOR WALLS 6 FEET OR LESS IN HEIGHT
WHEN NATIVE MATERIAL HAS EXPANSION INDEX OF <50 Leighton Figure
Geotechnical Exploration Report 10791.002
Proposed CarMax Automotive Dealership October 3, 2014
APPENDIX E
ASFE - IMPORTANT INFORMATION ABOUT YOUR GEOTECHNICAL REPORT Important Information About Your
Geotechnical Engineering Report
Subsurface problems are a principal cause of construction delays, cost overruns, claims, and disputes.
The following information is provided to help you manage your risks.
Geotechnical Services Are Performed lor
Specific Purposes, Persons, and Projects
Geotechnical engineers structure their services to meet the specific needs of their clients. A geotechnical engineering study conducted for a civil engineer may not fulfill the needs of a construction contractor or even another civil engineer. Because each geotechnical engineering study is unique, each geotechnical engineering report is unique, prepared solely for the client. No one except you should rely on your geotechnical engineering report without first conferring with the geotechnical engineer who prepared it. And no one -not even you -should apply the report for any purpose or project except the one originally contemplated.
Read the Full Report
Serious problems have occurred because those relying on a geotechnical engineering report did not read it all. Do not rely on an executive summary.
Do not read selected elements only.
A Geotechnical Engineering Report Is Based on
A Unique- Set ol Project-Specific Factors
Geotechnical engineers consider a number of unique, project-specific factors when establishing the scope of a study. Typical factors include: the client's goals, objectives, and risk management preferences; the general nature of the structure involved, its size, and configuration; the location of the structure on the site; and other planned or existing site improvements, such as access roads, parking lots, and underground utilities. Unless the geotechnical engineer who conducted the study specifically indicates otherwise, do not rely on a geotechnical engineering report that was:
• not prepared for you,
• not prepared for your project,
• not prepared for the specific site explored, or
• completed before important project changes were made.
Typical changes that can erode the reliability of an existing geotechnical engineering report include those that affect:
• the function of the proposed structure, as when it's changed from a parking garage to an office building, or from a light industrial plant to a refrigerated warehouse,
• elevation, configuration, location, orientation, or weight of the proposed structure,
• composition of the design team, or
• project ownership.
As a general rule, always inform your geotechnical engineer of project changes-even minor ones-and request an assessment of their impact.
Geotechnical engineers cannot accept responsibility or liability for problems that occur because their reports do not consider developments of which they were not informed.
Subsurface Conditions Can Change
A geotechnical engineering report is based on conditions that existed at the time the study was performed. Do not rely on a geotechnical engineering report whose adequacy may have been affected by: the passage of time; by man-made events, such as construction on or adjacent to the site; or by natural events, such as floods, earthquakes, or groundwater fluctuations. Always contact the geotechnical engineer before applying the report to determine if it is still reliable. A minor amount of additional testing or analysis could prevent major problems.
Most Geotechnical Findings Are Professional
Opinions
Site exploration identifies subsurface conditions only at those points where subsurface tests are conducted or samples are taken. Geotechnical engineers review field and laboratory data and then apply their professional judgment to render an opinion about subsurface conditions throughout the site. Actual subsurface conditions may differ-sometimes significantlyfrom those indicated in your report. Retaining the geotechnical engineer who developed your report to provide construction observation is the most effective method of managing the risks associated with unanticipated conditions.
A Report's Recommendations Are 11/ot Final
Do not overrely on the construction recommendations included in your report. Those recommendations are not final, because geotechnical engineers develop them principally from judgment and opinion. Geotechnical engineers can finalize their recommendations only by observing actual subsurface conditions revealed during construction. The geotechnical engineer who developed your report cannot assume responsibility or liability for the report's recommendations if that engineer does not perform construction observation.
A Geotechnical Engineering Report Is Subject to
Misinterpretation
Other design team members' misinterpretation of geotechnical engineering reports has resulted in costly problems. Lower that risk by having your geotechnical engineer confer with appropriate members of the design team after submitting the report. Also retain your geotechnical engineer to review pertinent elements of the design team's plans and specifications. Contractors can also misinterpret a geotechnical engineering report. Reduce that risk by having your geotechnical engineer participate in prebid and preconstruction conferences, and by providing construction observation.
Do Not Redraw the Engineer•s Logs
Geotechnical engineers prepare final boring and testing logs based upon their interpretation of field logs and laboratory data. To prevent errors or omissions, the logs included in a geotechnical engineering report should never be redrawn for inclusion in architectural or other design drawings.
Only photographic or electronic reproduction is acceptable, but recognize that separating logs from the report can elevate risk.
Give Contractors a Complete Report and
Guidance
Some owners and design professionals mistakenly believe they can make contractors liable for unanticipated subsurface conditions by limiting what they provide for bid preparation. To help prevent costly problems, give contractors the complete geotechnical engineering report, but preface it with a clearly written letter of transmittal. In that letter, advise contractors that the report was not prepared for purposes of bid development and that the report's accuracy is limited; encourage them to confer with the geotechnical engineer who prepared the report (a modest fee may be required) and/or to conduct additional study to obtain the specific types of information they need or prefer. A prebid conference can also be valuable. Be sure contractors have sufficient time to perform additional study. Only then might you be in a position to give contractors the best information available to you, while requiring them to at least share some of the financial responsibilities stemming from unanticipated conditions.
Read Responsibility Provisions Closely
Some clients, design professionals, and contractors do not recognize that geotechnical engineering is far less exact than other engineering disciplines. This lack of understanding has created unrealistic expectations that have led to disappointments, claims, and disputes. To help reduce the risk of such outcomes, geotechnical engineers commonly include a variety of explanatory provisions in their reports. Sometimes labeled "limitations" many of these provisions indicate where geotechnical engineers' responsibilities begin and end, to help others recognize their own responsibilities and risks. Read these provisions closely Ask questions. Your geotechnical engineer should respond fully and frankly.
Geoenvironmental Concerns Are Not Covered
The equipment, techniques, and personnel used to perform a geoenvironmental study differ significantly from those used to perform a geotechnical study. For that reason, a geotechnical engineering report does not usually relate any geoenvironmental findings, conclusions, or recommendations; e.g., about the likelihood of encountering underground storage tanks or regulated contaminants. Unanticipated environmental problems have led to numerous project failures. If you have not yet obtained your own geoenvironmental information, ask your geotechnical consultant for risk management guidance. Do not rely on an environmental report prepared for someone else.
Obtain Professional Assistance To Deal with Mold
Diverse strategies can be applied during building design, construction, operation, and maintenance to prevent significant amounts of mold from growing on indoor surfaces. To be effective, all such strategies should be devised for the express purpose of mold prevention, integrated into a comprehensive plan, and executed with diligent oversight by a professional mold prevention consultant. Because just a small amount of water or moisture can lead to the development of severe mold infestations, a number of mold prevention strategies focus on keeping building surfaces dry.
While groundwater, water infiltration, and similar issues may have been addressed as part of the geotechnical engineering study whose findings are conveyed in this report, the geotechnical engineer in charge of this project is not a mold prevention consultant; none of the services performed in connection with the geotechnical engineer's study were designed or conducted for the purpose of mold prevention. Proper implementation of the recommendations conveyed in this report will not of itself be sufficient to prevent mold from growing in or on the structure involved.
Rely, on Your ASH-Member Geotechncial
Engmeer lor Additional Assistance
Membership in ASFE/THE BEST PEOPLE ON EARTH exposes geotechnical engineers to a wide array of risk management techniques that can be of genuine benefit for everyone involved with a construction project. Confer with you ASFE-member geotechnical engineer for more information.
ASFE
THE BEST PEOPLE ON EARTH
8811 Colesville Road/Suite G1 06, Silver Spring, MD 20910 Telephone: 301/565-2733 Facsimile: 301/589-2017
e-mail: [email protected] www.asfe.org
Copyright 2004 by ASFE, Inc. Duplication, reproduction, or copying of this document, in whole or in part, by any means whatsoever, is strictly prohibited, except with ASFE's specific written permission. Excerpting, quoting, or otherwise extracting wording from this document is permitted only with the express written permission of ASFE, and only for purposes of scholarly research or book review. Only members of ASFE may use this document as a complement to or as an element of a geotechnical engineering report. Any other firm, individual, or other entity that so uses this document without being an ASFE member could be committing negligent or intentional (fraudulent) misrepresentation.
IIGER08041.0MRP
Water Quality Management Plan (WQMP)
CarMax Automotive Dealership ‐ Murrieta
‐ 45 ‐
Appendix 4: Historical Site Conditions
Phase I Environmental Site Assessment or Other Information on Past Site Use Water Quality Management Plan (WQMP)
CarMax Automotive Dealership ‐ Murrieta
‐ 46 ‐
Appendix 5: LID Infeasibility
LID Technical Infeasibility Analysis
Water Quality Management Plan (WQMP)
CarMax Automotive Dealership ‐ Murrieta
‐ 47 ‐
Appendix 6: BMP Design Details
BMP Sizing, Design Details and other Supporting Documentation Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
3.5 Bioretention Facility
Description
Bioretention Facilities are shallow, vegetated basins underlain by an engineered soil media.
Healthy plant and biological activity in the root zone maintain and renew the macro‐pore space in the soil and maximize plant uptake of pollutants and runoff. This keeps the Best Management Practice (BMP) from becoming clogged and allows more of the soil column to function as both a sponge (retaining water) and a highly effective and self‐maintaining biofilter.
In most cases, the bottom of a Bioretention Facility is unlined, which also provides an opportunity for infiltration to the extent the underlying onsite soil can accommodate. When the infiltration rate of the underlying soil is exceeded, fully biotreated flows are discharged via underdrains. Bioretention Facilities therefore will inherently achieve the maximum feasible level of infiltration and evapotranspiration and achieve the minimum feasible (but highly biotreated) discharge to the storm drain system.
Siting Considerations
These facilities work best when they are designed in a relatively level area. Unlike other BMPs, Bioretention Facilities can be used in smaller landscaped spaces on the site, such as:
Parking islands
Medians
Site entrances
Landscaped areas on the site (such as may otherwise be required through minimum landscaping ordinances), can often be designed as Bioretention Facilities. This can be accomplished by:
Depressing landscaped areas below adjacent impervious surfaces, rather than elevating those areas
Grading the site to direct runoff from those impervious surfaces into the Bioretention Facility, rather than away from the landscaping
Sizing and designing the depressed landscaped area as a Bioretention Facility as described in this Fact Sheet
Type of BMP LID – Bioretention
Treatment Mechanisms Infiltration, Evapotranspiration, Evaporation, Biofiltration Maximum Drainage Area This BMP is intended to be integrated into a project’s landscaped area in a distributed manner. Typically, contributing drainage areas to Bioretention Facilities range from less than 1 acre to a maximum of around 10 acres.
Other Names Rain Garden, Bioretention Cell, Bioretention Basin, Biofiltration Basin, Landscaped Filter Basin, Porous Landscape Detention
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
Bioretention Facilities should however not be used downstream of areas where large amounts of sediment can clog the system. Placing a Bioretention Facility at the toe of a steep slope should also be avoided due to the potential for clogging the engineered soil media with erosion from the slope, as well as the potential for damaging the vegetation.
Design and Sizing Criteria
The recommended cross section necessary for a Bioretention Facility includes:
Vegetated area
18' minimum depth of engineered soil media
12' minimum gravel layer depth with 6' perforated pipes (added flow control features such as orifice plates may be required to mitigate for HCOC conditions) While the 18‐inch minimum engineered soil media depth can be used in some cases, it is recommended to use 24 inches or a preferred 36 inches to provide an adequate root zone for the chosen plant palate. Such a design also provides for improved removal effectiveness for nutrients. The recommended ponding depth inside of a Bioretention Facility is 6 inches; measured from the flat bottom surface to the top of the water surface as shown in Figure 1.
Because this BMP is filled with an engineered soil media, pore space in the soil and gravel layer is assumed to provide storage volume. However, several considerations must be noted:
Surcharge storage above the soil surface (6 inches) is important to assure that design flows do not bypass the BMP when runoff exceeds the soil’s absorption rate. In cases where the Bioretention Facility contains engineered soil media deeper than 36 inches, the pore space within the engineered soil media can only be counted to the 36‐ inch depth.
A maximum of 30 percent pore space can be used for the soil media whereas a maximum of 40 percent pore space can be use for the gravel layer.
Figure 1: Standard Layout for a Bioretention Facility
BIORETENTION FACILITY BMP FACT SHEET
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
Engineered Soil Media Requirements
The engineered soil media shall be comprised of 85 percent mineral component and 15 percent organic component, by volume, drum mixed prior to placement. The mineral component shall be a Class A sandy loam topsoil that meets the range specified in Table 1 below. The organic component shall be nitrogen stabilized compost1, such that nitrogen does not leach from the media.
Table 1: Mineral Component Range Requirements
Percent Range Component
70‐80 Sand
15‐20 Silt
5‐10 Clay
The trip ticket, or certificate of compliance, shall be made available to the inspector to prove the engineered mix meets this specification.
Vegetation Requirements
Vegetative cover is important to minimize erosion and ensure that treatment occurs in the Bioretention Facility. The area should be designed for at least 70 percent mature coverage throughout the Bioretention Facility. To prevent the BMP from being used as walkways, Bioretention Facilities shall be planted with a combination of small trees, densely planted shrubs, and natural grasses. Grasses shall be native or ornamental; preferably ones that do not need to be mowed. The application of fertilizers and pesticides should be minimal. To maintain oxygen levels for the vegetation and promote biodegradation, it is important that vegetation not be completely submerged for any extended period of time. Therefore, a maximum of 6 inches of ponded water shall be used in the design to ensure that plants within the Bioretention Facility remain healthy.
A 2 to 3‐inch layer of standard shredded aged hardwood mulch shall be placed as the top layer inside the Bioretention Facility. The 6‐inch ponding depth shown in Figure 1 above shall be measured from the top surface of the 2 to 3‐inch mulch layer.
Curb Cuts
To allow water to flow into the Bioretention Facility, 1‐foot‐wide (minimum) curb cuts should be placed approximately every 10 feet around the perimeter of the Bioretention Facility. Figure 2 shows a curb cut in a Bioretention Facility. Curb cut flow lines must be at or above the VBMP water surface level.
1 For more information on compost, visit the US Composting Council website at: http://compostingcouncil.org/
BIORETENTION FACILITY BMP FACT SHEET
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
Figure 2: Curb Cut located in a Bioretention Facility
To reduce erosion, a gravel pad shall be placed
at each inlet point to the Bioretention Facility.
The gravel should be 1‐ to 1.5‐inch diameter in
size. The gravel should overlap the curb cut
opening a minimum of 6 inches. The gravel pad
inside the Bioretention Facility should be flush
with the finished surface at the curb cut and
extend to the bottom of the slope.
In addition, place an apron of stone or concrete,
a foot square or larger, inside each inlet to
prevent vegetation from growing up and
blocking the inlet. See Figure 3.
Terracing the Landscaped Filter Basin
It is recommended that Bioretention Facilities be level. In the event the facility site slopes and lacks proper design, water would fill the lowest point of the BMP and then discharge from the basin without being treated. To ensure that the water will be held within the Bioretention Facility on sloped sites, the BMP must be terraced with nonporous check dams to provide the required storage and treatment capacity.
The terraced version of this BMP shall be used on non‐flat sites with no more than a 3 percent slope. The surcharge depth cannot exceed 0.5 feet, and side slopes shall not exceed 4:1. Table 2 below shows the spacing of the check dams, and slopes shall be rounded up (i.e., 2.5 percent slope shall use 10' spacing for check dams).
Table 2: Check Dam Spacing
6” Check Dam Spacing
Slope Spacing
1% 25'
2% 15'
3% 10'
Figure 3: Apron located in a Bioretention Facility
BIORETENTION FACILITY BMP FACT SHEET
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
Roof Runoff
Roof downspouts may be directed towards Bioretention Facilities. However, the downspouts must discharge onto a concrete splash block to protect the Bioretention Facility from erosion.
Retaining Walls
It is recommended that Retaining Wall Type 1A, per Caltrans Standard B3‐3 or equivalent, be constructed around the entire perimeter of the Bioretention Facility. This practice will protect the sides of the Bioretention Facility from collapsing during construction and maintenance or from high service loads adjacent to the BMP. Where such service loads would not exist adjacent to the BMP, an engineered alternative may be used if signed by a licensed civil engineer.
Side Slope Requirements
Bioretention Facilities Requiring Side Slopes
The design should assure that the Bioretention Facility does not present a tripping hazard.
Bioretention Facilities proposed near pedestrian areas, such as areas parallel to parking spaces or along a walkway, must have a gentle slope to the bottom of the facility. Side slopes inside of a Bioretention Facility shall be 4:1. A typical cross section for the Bioretention Facility is shown in Figure 1.
Bioretention Facilities Not Requiring Side Slopes
Where cars park perpendicular to the Bioretention Facility, side slopes are not required. A 6‐ inch maximum drop may be used, and the Bioretention Facility must be planted with trees and shrubs to prevent pedestrian access. In this case, a curb is not placed around the Bioretention Facility,
but wheel stops shall be used to prevent vehicles from entering the Bioretention Facility, as shown in Figure 4.
Figure 4: Bioretention Facility Layout without Side Slopes
BIORETENTION FACILITY BMP FACT SHEET
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
Planter Boxes
Bioretention Facilities can also be placed above ground as planter boxes. Planter boxes must have a minimum width of 2 feet, a maximum surcharge depth of 6 inches, and no side slopes are necessary. Planter boxes must be constructed so as to ensure that the top surface of the engineered soil media will remain level. This option may be constructed of concrete, brick, stone or other stable materials that will not warp or bend. Chemically treated wood or galvanized steel, which has the ability to contaminate stormwater, should not be used. Planter boxes must be lined with an impermeable liner on all sides, including the bottom. Due to the impermeable liner, the inside bottom of the planter box shall be designed and constructed with a cross fall, directing treated flows within the subdrain layer toward the point where subdrain exits the planter box, and subdrains shall be oriented with drain holes oriented down. These provisions will help avoid excessive stagnant water within the gravel underdrain layer. Similar to the in‐ground Bioretention Facility versions, this BMP benefits from healthy plants and biological activity in the root zone. Planter boxes should be planted with appropriately selected vegetation.
Figure 5: Planter Box
Source: LA Team Effort
Overflow
An overflow route is needed in the Bioretention Facility design to bypass stored runoff from storm events larger than VBMP or in the event of facility or subdrain clogging. Overflow systems must connect to an acceptable discharge point, such as a downstream conveyance system as shown in Figure 1 and Figure 4. The inlet to the overflow structure shall be elevated inside the Bioretention Facility to be flush with the ponding surface for the design capture volume (VBMP) as shown in Figure 4. This will allow the design capture volume to be fully treated by the Bioretention Facility, and for larger events to safely be conveyed to downstream systems. The overflow inlet shall not be located in the entrance of a Bioretention Facility, as shown in Figure
6. BIORETENTION FACILITY BMP FACT SHEET
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
Underdrain Gravel and Pipes
An underdrain gravel layer and pipes shall be provided in accordance with Appendix B – Underdrains.
Figure 6: Incorrect Placement of an Overflow Inlet.
Inspection and Maintenance Schedule
The Bioretention Facility area shall be inspected for erosion, dead vegetation, soggy soils, or standing water. The use of fertilizers and pesticides on the plants inside the Bioretention Facility should be minimized.
Schedule Activity
Ongoing
Keep adjacent landscape areas maintained. Remove clippings from landscape maintenance activities.
Remove trash and debris
Replace damaged grass and/or plants
Replace surface mulch layer as needed to maintain a 2‐3 inch soil cover.
After storm events Inspect areas for ponding
Annually Inspect/clean inlets and outlets
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
Bioretention Facility Design Procedure
1) Enter the area tributary, AT, to the Bioretention Facility. 2) Enter the Design Volume, VBMP, determined from Section 2.1 of this Handbook. 3) Select the type of design used. There are two types of Bioretention Facility designs: the standard design used for most project sites that include side slopes, and the modified design used when the BMP is located perpendicular to the parking spaces or with planter boxes that do not use side slopes.
4) Enter the depth of the engineered soil media, dS. The minimum depth for the engineered soil media can be 18' in limited cases, but it is recommended to use 24' or a preferred 36' to provide an adequate root zone for the chosen plant palette. Engineered soil media deeper than 36' will only get credit for the pore space in the first 36'. 5) Enter the top width of the Bioretention Facility.
6) Calculate the total effective depth, dE, within the Bioretention Facility. The maximum allowable pore space of the soil media is 30% while the maximum allowable pore space for the gravel layer is 40%. Gravel layer deeper than 12' will only get credit for the pore space in the first 12'.
a. For the design with side slopes the following equation shall be used to determine the total effective depth. Where, dP is the depth of ponding within the basin. dሺftሻ ൌ 0.3 ൈ ቂ൫wሺftሻ ൈdୗሺftሻ൯ 4൫dሺftሻ൯
ଶ
ቃ 0.4 ൈ 1ሺftሻ dሺftሻൣ4dሺftሻ ൫wሺftሻ െ 8dሺftሻ൯൧ wሺftሻ
This above equation can be simplified if the maximum ponding depth of 0.5’ is used. The equation below is used on the worksheet to find the minimum area required for the Bioretention Facility:
dሺftሻ ൌ ሺ0.3 ൈ dୗሺftሻ 0.4 x 1ሺftሻሻ െቆ0.7 ሺftଶሻ
wሺftሻ ቇ 0.5ሺftሻ
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
b. For the design without side slopes the following equation shall be used to determine the total effective depth:
dሺftሻ ൌdሺftሻ ሾሺ0.3ሻ ൈdୗሺftሻ ሺ0.4ሻ ൈ 1ሺftሻሿ
The equation below, using the maximum ponding depth of 0.5', is used on the worksheet to find the minimum area required for the Bioretention Facility:
dሺftሻ ൌ 0.5 ሺftሻ ሾሺ0.3ሻ ൈdୗሺftሻ ሺ0.4ሻ ൈ 1ሺftሻሿ
7) Calculate the minimum surface area, AM, required for the Bioretention Facility. This does not include the curb surrounding the Bioretention Facility or side slopes.
Aሺftଶሻ ൌ Vሺftଷሻ
d ሺftሻ
8) Enter the proposed surface area. This area shall not be less than the minimum required surface area.
9) Verify that side slopes are no steeper than 4:1 in the standard design, and are not required in the modified design.
10) Provide the diameter, minimum 6 inches, of the perforated underdrain used in the Bioretention Facility. See Appendix B for specific information regarding perforated pipes.
11) Provide the slope of the site around the Bioretention Facility, if used. The maximum slope is 3 percent for a standard design.
12) Provide the check dam spacing, if the site around the Bioretention Facility is sloped. 13) Describe the vegetation used within the Bioretention Facility.
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012
References Used to Develop this Fact Sheet
Anderson, Dale V. "Landscaped Filter Basin Soil Requirements." Riverside, May 2010.
California Department of Transportation. CalTrans Standard Plans. 15 September 2005. May 2010 <http://www.dot.ca.gov/hq/esc/oe/project_plans/HTM/stdplns‐met‐new99.htm>.
Camp Dresser and McKee Inc.; Larry Walker Associates. California Stormwater Best Management Practice Handbook for New Development and Redevelopment. California Stormwater Quality Association (CASQA), 2004.
Contra Costa Clean Water Program. Stormwater Quality Requirements for Development Applications. 3rd Edition. Contra Costa, 2006.
County of Los Angeles Public Works. Stormwater Best Management Practice Design and Maintenance Manual. Los Angeles, 2009.
Kim, Hunho, Eric A. Seagren and Allen P. Davis. "Engineered Bioretention for Removal of Nitrate from Stormwater Runoff." Water Environment Research 75.4 (2003): 355‐366.
LA Team Effort. LA Team Effort: FREE Planter Boxes for Businesses. 2 November 2009. May 2010 <http://lateameffort.blogspot.com/2009/11/free‐planter‐boxes‐for‐businesses‐est.html>.
Montgomery County Maryland Department of Permitting Services Water Resources Section.
Biofiltration (BF). Montgomery County, 2005.
Program, Ventura Countywide Stormwater Quality Management. Technical Guidance Manual for Stormwater Quality Control Measures. Ventura, 2002.
United States Environmental Protection Agency. Storm Water Technology Fact Sheet Bioretention. Washington D.C, 1999.
Urban Drainage and Flood Control District. Urban Storm Drainage Criteria Manual Volume 3 ‐ Best Management Practices. Vol. 3. Denver, 2008. 3 vols.
Urbonas, Ben R. Stormwater Sand Filter Sizing and Design: A Unit Operations Approach. Denver:
Urban Drainage and Flood Control District, 2002.
Riverside County - Low Impact Development BMP Design Handbook rev. 9/2011
APPENDIX B – UNDERDRAINS
Where underdrains are specified, the following information provides guidance for underdrain requirements.
Underdrain Material Types
Underdrain pipe shall be 6-inch diameter ABS pipe or PVC pipe. ABS pipe shall meet the requirements of ASTM Designation D-2751, SDR 23.5, and PVC pipe shall meet the requirements of ASTM Designation D-2665. Perforations shall be as described in ASTM Designation C-700. It should be noted that placing the pipe such that the perforations are oriented upward may help to maximize infiltration in unlined BMP’s with underdrains. If the BMP is constructed with an impermeable liner, the perforations should be angled downward to maximize the volume of water that will be drained from the BMP.
Underdrain Connections
Pipe joints and storm drain structure connections must be adequately sealed to avoid piping conditions (water seeping through pipe or structure joints). Pipe sections shall be coupled using suitable connection rings and flanges. Field connections to storm drain structures and pipes shall be sealed with polymer grout material that is capable of adhering to surfaces. Underdrain pipe shall be capped (at structure) until completion of site construction. Underdrains connected directly to a storm drainage structure shall be non-perforated for an appropriate distance from the structure interface to avoid possible piping problems.
Underdrain Slope
Underdrains must "daylight" or connect to an existing drainage system to achieve positive flow.
All underdrains must be placed with a minimum slope of 0.5% (s = 0.005 ft/ft).
Underdrains Layout and Spacing
Typically, there are two main layouts for underdrains. One is a non-perforated central collector pipe with perforated lateral feeder pipes, the other is simply a series of longitudinal perforated pipes. Both layouts connect to a non-perforated outlet pipe before “daylighting" or connecting to an existing drainage system. The minimum spacing is shown below.
BMP Type Underdrains
Center to Center Spacing
Sand Filter Basin 20’
Extended Detention Basins (Bottom stage 500 sq ft. or greater) 20’ Extended Detention Basins (Bottom stage < 500 sq ft.) 10’ Bioretention Facility 5’
Riverside County - Low Impact Development BMP Design Handbook rev. 9/2011
Underdrain Gravel
Gravel bed materials should be used to protect an underdrain pipe and to reduce clogging potential. Placement of gravel over the underdrain must be done with care. Avoid dropping the gravel from excessive heights from a backhoe or front-end loader bucket. Spill directly over underdrain and spread manually.
Recommended construction specifications for gravel used to protect underdrains are as follows:
• AASHTO #57 stone preferred
• Geotextile fabrics should be avoided because tearing and/or plugging can dramatically affect performance. If the designer is concerned about the engineered soil media migrating into the underdrain, a 3-inch thick layer of "pea gravel" may be added to create a “choker” course.
Maintenance
Access for cleaning underdrains is required for each system. Clean-outs, with diameters equal to the underdrain, should extend 6 inches above the media and have a lockable screw cap for easy access. Cleanouts should be located for every 50 feet of lateral, at the collector drain line connection, and at any bends.
Underdrain Orifice Plate
When designing a BMP to meet Hydraulic Conditions of Concern (HCOC) criteria in addition to water quality criteria, it is sometimes necessary to install an orifice plate near the downstream end of the underdrain system. The orifice plate restricts the opening of the underdrain to mitigate flows to a specific lower flow threshold. Proper maintenance access should be provided to the orifice plate location to facilitate maintenance activities, specifically the removal of accumulated sediment and debris upstream of the orifice plate.
to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 1
6.45 0.80
Impervious surfaces
1.00 0.89
0.712
16,670
DMA Type C
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 1
6.45 Impervious Soils
1.00 0.89
5.74 DMA Type C
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 1a
0.67 0.80
Landscaping
0.15 0.14
0.112
272
DMA Type B
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 1a
0.67 Landscaping
0.15 0.14
0.014
DMA Type B
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 2
4.42 0.80
Impervious Surfaces
1.00 0.89
0.712
11,424
DMA Type D
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 1a
04.42 Impervious Surfaces
1.00 0.89
0.59 DMA Type D
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 3
2.51 0.80
Impervious Surfaces
1.00 0.89
0.712
6,487
DMA Type C
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 3
2.51 Impervious Surfaces
1.00 0.89
2.23 DMA Type C
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 3a
0.94 0.80
Landscaping
0.15 0.14
0.112
382
DMA Type B
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 3a
0.94 Landscaping
0.15 0.14
0.020
DMA Type B
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 4
9.98 0.80
Impervious Surfaces
1.00 0.89
0.712
25,794
DMA Type D
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 4
9.98 Impervious Surfaces
1.00 0.89
8.88 DMA Type D
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 5
10.41 0.80
Impervious Surfaces
1.00 0.89
0.712
26,905
DMA Type C
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 5
10.41 Impervious Surfaces
1.00 0.89
9.26 DMA Type C
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 5a
1.44 0.80
Landscaping
0.15 0.14
0.112
585
DMA Type B
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 3a
1.44 Landscaping
0.15 0.14
0.30 DMA Type B
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets to access the worksheets for the Santa Margarita Watershed If your project is not located in the Santa Margarita Watershed, Do not use these worksheets! Instead visit
www.rcflood.org/npdes/developers.aspx
To access worksheets applicable to your watershed
Use the tabs across the bottom
Santa Margarita Watershed
VBMP and QBMP worksheets
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Margarita Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
Date
Enter the Area Tributary to this Feature AT = acres
Site Location Township
Range
Section
D85 =
If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
Vu =
VBMP (ft3)= VBMP = ft3
Drainage Area Number/Name
Calculated Cells
Company Name
Santa Margarita Watershed
BMP Design Volume, VBMP (Rev. 03-2012) Legend: Required Entries Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Determine Design Storage Volume, VBMP
(in*ac)/ac
Designed by County/City Case No
Company Project Number/Name
Notes:
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook) Calculate the design storage volume of the BMP, VBMP.
12 (in/ft)
Calculate VU, the 85% Unit Storage Volume VU= D85 x C
VU (in-ac/ac) x AT (ac) x 43,560 (ft2/ac)
Enter the 85th Percentile, 24-hour Rainfall Depth
Determine the Effective Impervious Fraction
Type of post-development surface cover
(use pull down menu)
Roofs
Effective Impervious Fraction
85th Percentile, 24-hour Rainfall Depth, from the Isohyetal Map in Handbook Appendix E Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 6
2.07 0.80
Impervious Surfaces
1.00 0.89
0.712
5,350
DMA Type D
Date
Enter the Area Tributary to this Feature AT = acres
Effective Impervious Fraction If =
Use the following equation based on the WEF/ASCE Method C = 0.858If
3 - 0.78If
2 + 0.774If + 0.04 C =
QBMP = C x I x AT ft3
/s
Notes:
Calculated Cells
Company Name
BMP Design Flow Rate
Designed by County/City Case No
Calculate the composite Runoff Coefficient, C for the BMP Tributary Area Required Entries
Drainage Area Number/Name
Company Project Number/Name
Legend: Santa Margarita Watershed
BMP Design Flow Rate, QBMP (Rev. 03-2012)
Type of post-development surface cover
(use pull down menu)
Determine the Effective Impervious Fraction
Roofs
QBMP =
Hall & Foreman 2/19/2015
Glenn M. Chung
150015 / CarMax Automotive Dealership
DMA 6
2.07 Impervious Surfaces
1.00 0.89
1.84 DMA Type D
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets Water Quality Management Plan (WQMP)
CarMax Automotive Dealership ‐ Murrieta
‐ 48 ‐
Appendix 7: Hydromodification
Supporting Detail Relating to compliance with the HMP Performance Standards SMRHM
PROJECT REPORT
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 2 General Model Information
Project Name: Conceptual Design_0.5 Infiltration
Site Name: Carmax 6002
Site Address:
City: Murrieta
Report Date: 2/12/2015
Gage: Temecula Valley
Data Start: 1974/10/01
Data End: 2011/09/30
Timestep: 15 Minute
Precip Scale: 1.00
Version: 2015/01/28
POC Thresholds
Low Flow Threshold for POC1: 10 Percent of the 2 Year
High Flow Threshold for POC1: 10 Year
Low Flow Threshold for POC2: 10 Percent of the 2 Year
High Flow Threshold for POC2: 10 Year
Low Flow Threshold for POC3: 10 Percent of the 2 Year
High Flow Threshold for POC3: 10 Year
Low Flow Threshold for POC4: 10 Percent of the 2 Year
High Flow Threshold for POC4: 10 Year
Low Flow Threshold for POC5: 10 Percent of the 2 Year
High Flow Threshold for POC5: 10 Year
Low Flow Threshold for POC6: 10 Percent of the 2 Year
High Flow Threshold for POC6: 10 Year
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 3 Landuse Basin Data
Predeveloped Land Use
DMA A
Bypass: No
GroundWater: No
Pervious Land Use Acres
B,Grass,Stee(10-20%) 7.117
Pervious Total 7.117
Impervious Land Use Acres
Impervious Total 0
Basin Total 7.117
Element Flows To:
Surface Interflow Groundwater
Channel 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 4 DMA B
Bypass: No
GroundWater: No
Pervious Land Use Acres
B,Grass,Stee(10-20%) 4.417
Pervious Total 4.417
Impervious Land Use Acres
Impervious Total 0
Basin Total 4.417
Element Flows To:
Surface Interflow Groundwater
Channel 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 5 DMA C
Bypass: No
GroundWater: No
Pervious Land Use Acres
B,Grass,Stee(10-20%) 3.449
Pervious Total 3.449
Impervious Land Use Acres
Impervious Total 0
Basin Total 3.449
Element Flows To:
Surface Interflow Groundwater
Channel 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 6 DMA D
Bypass: No
GroundWater: No
Pervious Land Use Acres
B,Grass,Stee(10-20%) 9.981
Pervious Total 9.981
Impervious Land Use Acres
Impervious Total 0
Basin Total 9.981
Element Flows To:
Surface Interflow Groundwater
Channel 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 7 DMA E
Bypass: No
GroundWater: No
Pervious Land Use Acres
B,Grass,Stee(10-20%) 11.846
Pervious Total 11.846
Impervious Land Use Acres
Impervious Total 0
Basin Total 11.846
Element Flows To:
Surface Interflow Groundwater
Channel 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 8 DMA F
Bypass: No
GroundWater: No
Pervious Land Use Acres
B,Grass,Stee(10-20%) 2.073
Pervious Total 2.073
Impervious Land Use Acres
Impervious Total 0
Basin Total 2.073
Element Flows To:
Surface Interflow Groundwater
Channel 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 9 Mitigated Land Use
DMA A
Bypass: No
GroundWater: No
Pervious Land Use Acres
A,Urban,Stee(10-20%) 0.873
A,Urban,Flat(0-5%) 0.378
A,Urban,Very S(>20%) 0.673
Pervious Total 1.924
Impervious Land Use Acres
Roof Area 0.311
Sidewalks,Flat(0-5%) 0.142
Parking,Flat(0-5%) 4.739
Impervious Total 5.192
Basin Total 7.116
Element Flows To:
Surface Interflow Groundwater
Infilt Pla Surface 1 Infilt Pla Surface 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 10 DMA B
Bypass: No
GroundWater: No
Pervious Land Use Acres
A,Urban,Stee(10-20%) 0.138
Pervious Total 0.138
Impervious Land Use Acres
Roof Area 0.856
Sidewalks,Flat(0-5%) 0.076
Parking,Flat(0-5%) 3.346
Impervious Total 4.278
Basin Total 4.416
Element Flows To:
Surface Interflow Groundwater
Gravel Trench Bed 1 Gravel Trench Bed 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 11 DMA D
Bypass: No
GroundWater: No
Pervious Land Use Acres
A,Urban,Flat(0-5%) 0.317
A,Urban,Stee(10-20%) 0.372
A,Urban,Very S(>20%) 1.309
Pervious Total 1.998
Impervious Land Use Acres
Roof Area 0.535
Sidewalks,Flat(0-5%) 0.078
Parking,Flat(0-5%) 7.369
Impervious Total 7.982
Basin Total 9.98
Element Flows To:
Surface Interflow Groundwater
Infilt Pla Surface 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 12 DMA E
Bypass: No
GroundWater: No
Pervious Land Use Acres
A,Urban,Flat(0-5%) 0.522
A,Urban,Stee(10-20%) 2.233
Pervious Total 2.755
Impervious Land Use Acres
Roof Area 0.439
Sidewalks,Flat(0-5%) 0.173
Parking,Flat(0-5%) 8.489
Impervious Total 9.101
Basin Total 11.856
Element Flows To:
Surface Interflow Groundwater
Infilt Pla Surface 1 Infilt Pla Surface 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 13 DMA C
Bypass: No
GroundWater: No
Pervious Land Use Acres
A,Urban,Flat(0-5%) 0.273
A,Urban,Stee(10-20%) 0.198
A,Urban,Very S(>20%) 0.947
Pervious Total 1.418
Impervious Land Use Acres
Sidewalks,Flat(0-5%) 0.007
Parking,Flat(0-5%) 2.023
Impervious Total 2.03
Basin Total 3.448
Element Flows To:
Surface Interflow Groundwater
Infilt Pla Surface 1 Infilt Pla Surface 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 14 DMA F
Bypass: No
GroundWater: No
Pervious Land Use Acres
A,Urban,Flat(0-5%) 0.168
Pervious Total 0.168
Impervious Land Use Acres
Roof Area 0.28
Sidewalks,Flat(0-5%) 0.092
Parking,Flat(0-5%) 1.53
Impervious Total 1.902
Basin Total 2.07
Element Flows To:
Surface Interflow Groundwater
Infilt Pla Surface 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 15 Routing Elements
Predeveloped Routing
Channel 1
Bottom Length: 700.00 ft.
Bottom Width: 40.00 ft.
Manning's n: 0.025
Channel bottom slope 1: 0.02 To 1
Channel Left side slope 0: 2 To 1
Channel right side slope 2: 2 To 1
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Element Flows To:
Outlet 1 Outlet 2
Channel Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.642 0.000 0.000 0.000
0.2000 0.655 0.129 23.10 0.000
0.4000 0.668 0.262 73.49 0.000
0.6000 0.681 0.397 144.7 0.000
0.8000 0.694 0.534 234.3 0.000
1.0000 0.707 0.675 340.7 0.000
1.2000 0.720 0.817 462.9 0.000
1.4000 0.732 0.962 600.1 0.000
1.6000 0.745 1.110 751.7 0.000
1.8000 0.758 1.261 917.4 0.000
2.0000 0.771 1.414 1096. 0.000
2.2000 0.784 1.569 1289. 0.000
2.4000 0.797 1.727 1495. 0.000
2.6000 0.810 1.888 1714. 0.000
2.8000 0.822 2.052 1945. 0.000
3.0000 0.835 2.217 2189. 0.000
3.2000 0.848 2.386 2446. 0.000
3.4000 0.861 2.557 2716. 0.000
3.6000 0.874 2.730 2998. 0.000
3.8000 0.887 2.907 3292. 0.000
4.0000 0.900 3.085 3599. 0.000
4.2000 0.913 3.267 3918. 0.000
4.4000 0.925 3.451 4249. 0.000
4.6000 0.938 3.637 4593. 0.000
4.8000 0.951 3.826 4949. 0.000
5.0000 0.964 4.018 5317. 0.000
5.2000 0.977 4.212 5698. 0.000
5.4000 0.990 4.409 6091. 0.000
5.6000 1.003 4.608 6497. 0.000
5.8000 1.015 4.810 6915. 0.000
6.0000 1.028 5.014 7345. 0.000
6.2000 1.041 5.221 7788. 0.000
6.4000 1.054 5.431 8244. 0.000
6.6000 1.067 5.643 8712. 0.000
6.8000 1.080 5.858 9193. 0.000
7.0000 1.093 6.075 9686. 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 16
7.2000 1.106 6.295 10192 0.000
7.4000 1.118 6.518 10711 0.000
7.6000 1.131 6.743 11243 0.000
7.8000 1.144 6.970 11788 0.000
8.0000 1.157 7.201 12346 0.000
8.2000 1.170 7.433 12916 0.000
8.4000 1.183 7.669 13500 0.000
8.6000 1.196 7.907 14097 0.000
8.8000 1.209 8.147 14708 0.000
9.0000 1.221 8.390 15331 0.000
9.2000 1.234 8.636 15968 0.000
9.4000 1.247 8.884 16618 0.000
9.6000 1.260 9.135 17282 0.000
9.8000 1.273 9.389 17959 0.000
10.000 1.286 9.644 18650 0.000
10.200 1.299 9.903 19354 0.000
10.400 1.312 10.16 20072 0.000
10.600 1.325 10.42 20804 0.000
10.800 1.337 10.69 21550 0.000
11.000 1.350 10.96 22310 0.000
11.200 1.363 11.23 23084 0.000
11.400 1.376 11.50 23872 0.000
11.600 1.389 11.78 24674 0.000
11.800 1.402 12.06 25490 0.000
12.000 1.415 12.34 26321 0.000
12.200 1.428 12.63 27166 0.000
12.400 1.440 12.91 28025 0.000
12.600 1.453 13.20 28899 0.000
12.800 1.466 13.49 29788 0.000
13.000 1.479 13.79 30691 0.000
13.200 1.492 14.09 31609 0.000
13.400 1.505 14.39 32541 0.000
13.600 1.518 14.69 33489 0.000
13.800 1.531 14.99 34451 0.000
14.000 1.543 15.30 35429 0.000
14.200 1.556 15.61 36421 0.000
14.400 1.569 15.92 37429 0.000
14.600 1.582 16.24 38452 0.000
14.800 1.595 16.56 39490 0.000
15.000 1.608 16.88 40544 0.000
15.200 1.621 17.20 41613 0.000
15.400 1.634 17.53 42698 0.000
15.600 1.647 17.85 43798 0.000
15.800 1.659 18.18 44914 0.000
16.000 1.672 18.52 46045 0.000
16.200 1.685 18.85 47193 0.000
16.400 1.698 19.19 48356 0.000
16.600 1.711 19.53 49535 0.000
16.800 1.724 19.88 50731 0.000
17.000 1.737 20.22 51942 0.000
17.200 1.750 20.57 53170 0.000
17.400 1.763 20.92 54414 0.000
17.600 1.775 21.28 55674 0.000
17.800 1.788 21.63 56950 0.000
18.000 1.801 21.99 58243 0.000
18.200 1.814 22.35 59553 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 17 Channel 1
Bottom Length: 700.00 ft.
Bottom Width: 40.00 ft.
Manning's n: 0.025
Channel bottom slope 1: 0.02 To 1
Channel Left side slope 0: 2 To 1
Channel right side slope 2: 2 To 1
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Element Flows To:
Outlet 1 Outlet 2
Channel Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.642 0.000 0.000 0.000
0.2000 0.655 0.129 23.10 0.000
0.4000 0.668 0.262 73.49 0.000
0.6000 0.681 0.397 144.7 0.000
0.8000 0.694 0.534 234.3 0.000
1.0000 0.707 0.675 340.7 0.000
1.2000 0.720 0.817 462.9 0.000
1.4000 0.732 0.962 600.1 0.000
1.6000 0.745 1.110 751.7 0.000
1.8000 0.758 1.261 917.4 0.000
2.0000 0.771 1.414 1096. 0.000
2.2000 0.784 1.569 1289. 0.000
2.4000 0.797 1.727 1495. 0.000
2.6000 0.810 1.888 1714. 0.000
2.8000 0.822 2.052 1945. 0.000
3.0000 0.835 2.217 2189. 0.000
3.2000 0.848 2.386 2446. 0.000
3.4000 0.861 2.557 2716. 0.000
3.6000 0.874 2.730 2998. 0.000
3.8000 0.887 2.907 3292. 0.000
4.0000 0.900 3.085 3599. 0.000
4.2000 0.913 3.267 3918. 0.000
4.4000 0.925 3.451 4249. 0.000
4.6000 0.938 3.637 4593. 0.000
4.8000 0.951 3.826 4949. 0.000
5.0000 0.964 4.018 5317. 0.000
5.2000 0.977 4.212 5698. 0.000
5.4000 0.990 4.409 6091. 0.000
5.6000 1.003 4.608 6497. 0.000
5.8000 1.015 4.810 6915. 0.000
6.0000 1.028 5.014 7345. 0.000
6.2000 1.041 5.221 7788. 0.000
6.4000 1.054 5.431 8244. 0.000
6.6000 1.067 5.643 8712. 0.000
6.8000 1.080 5.858 9193. 0.000
7.0000 1.093 6.075 9686. 0.000
7.2000 1.106 6.295 10192 0.000
7.4000 1.118 6.518 10711 0.000
7.6000 1.131 6.743 11243 0.000
7.8000 1.144 6.970 11788 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 18
8.0000 1.157 7.201 12346 0.000
8.2000 1.170 7.433 12916 0.000
8.4000 1.183 7.669 13500 0.000
8.6000 1.196 7.907 14097 0.000
8.8000 1.209 8.147 14708 0.000
9.0000 1.221 8.390 15331 0.000
9.2000 1.234 8.636 15968 0.000
9.4000 1.247 8.884 16618 0.000
9.6000 1.260 9.135 17282 0.000
9.8000 1.273 9.389 17959 0.000
10.000 1.286 9.644 18650 0.000
10.200 1.299 9.903 19354 0.000
10.400 1.312 10.16 20072 0.000
10.600 1.325 10.42 20804 0.000
10.800 1.337 10.69 21550 0.000
11.000 1.350 10.96 22310 0.000
11.200 1.363 11.23 23084 0.000
11.400 1.376 11.50 23872 0.000
11.600 1.389 11.78 24674 0.000
11.800 1.402 12.06 25490 0.000
12.000 1.415 12.34 26321 0.000
12.200 1.428 12.63 27166 0.000
12.400 1.440 12.91 28025 0.000
12.600 1.453 13.20 28899 0.000
12.800 1.466 13.49 29788 0.000
13.000 1.479 13.79 30691 0.000
13.200 1.492 14.09 31609 0.000
13.400 1.505 14.39 32541 0.000
13.600 1.518 14.69 33489 0.000
13.800 1.531 14.99 34451 0.000
14.000 1.543 15.30 35429 0.000
14.200 1.556 15.61 36421 0.000
14.400 1.569 15.92 37429 0.000
14.600 1.582 16.24 38452 0.000
14.800 1.595 16.56 39490 0.000
15.000 1.608 16.88 40544 0.000
15.200 1.621 17.20 41613 0.000
15.400 1.634 17.53 42698 0.000
15.600 1.647 17.85 43798 0.000
15.800 1.659 18.18 44914 0.000
16.000 1.672 18.52 46045 0.000
16.200 1.685 18.85 47193 0.000
16.400 1.698 19.19 48356 0.000
16.600 1.711 19.53 49535 0.000
16.800 1.724 19.88 50731 0.000
17.000 1.737 20.22 51942 0.000
17.200 1.750 20.57 53170 0.000
17.400 1.763 20.92 54414 0.000
17.600 1.775 21.28 55674 0.000
17.800 1.788 21.63 56950 0.000
18.000 1.801 21.99 58243 0.000
18.200 1.814 22.35 59553 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 19 Channel 1
Bottom Length: 700.00 ft.
Bottom Width: 40.00 ft.
Manning's n: 0.025
Channel bottom slope 1: 0.02 To 1
Channel Left side slope 0: 2 To 1
Channel right side slope 2: 2 To 1
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Element Flows To:
Outlet 1 Outlet 2
Channel Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.642 0.000 0.000 0.000
0.2000 0.655 0.129 23.10 0.000
0.4000 0.668 0.262 73.49 0.000
0.6000 0.681 0.397 144.7 0.000
0.8000 0.694 0.534 234.3 0.000
1.0000 0.707 0.675 340.7 0.000
1.2000 0.720 0.817 462.9 0.000
1.4000 0.732 0.962 600.1 0.000
1.6000 0.745 1.110 751.7 0.000
1.8000 0.758 1.261 917.4 0.000
2.0000 0.771 1.414 1096. 0.000
2.2000 0.784 1.569 1289. 0.000
2.4000 0.797 1.727 1495. 0.000
2.6000 0.810 1.888 1714. 0.000
2.8000 0.822 2.052 1945. 0.000
3.0000 0.835 2.217 2189. 0.000
3.2000 0.848 2.386 2446. 0.000
3.4000 0.861 2.557 2716. 0.000
3.6000 0.874 2.730 2998. 0.000
3.8000 0.887 2.907 3292. 0.000
4.0000 0.900 3.085 3599. 0.000
4.2000 0.913 3.267 3918. 0.000
4.4000 0.925 3.451 4249. 0.000
4.6000 0.938 3.637 4593. 0.000
4.8000 0.951 3.826 4949. 0.000
5.0000 0.964 4.018 5317. 0.000
5.2000 0.977 4.212 5698. 0.000
5.4000 0.990 4.409 6091. 0.000
5.6000 1.003 4.608 6497. 0.000
5.8000 1.015 4.810 6915. 0.000
6.0000 1.028 5.014 7345. 0.000
6.2000 1.041 5.221 7788. 0.000
6.4000 1.054 5.431 8244. 0.000
6.6000 1.067 5.643 8712. 0.000
6.8000 1.080 5.858 9193. 0.000
7.0000 1.093 6.075 9686. 0.000
7.2000 1.106 6.295 10192 0.000
7.4000 1.118 6.518 10711 0.000
7.6000 1.131 6.743 11243 0.000
7.8000 1.144 6.970 11788 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 20
8.0000 1.157 7.201 12346 0.000
8.2000 1.170 7.433 12916 0.000
8.4000 1.183 7.669 13500 0.000
8.6000 1.196 7.907 14097 0.000
8.8000 1.209 8.147 14708 0.000
9.0000 1.221 8.390 15331 0.000
9.2000 1.234 8.636 15968 0.000
9.4000 1.247 8.884 16618 0.000
9.6000 1.260 9.135 17282 0.000
9.8000 1.273 9.389 17959 0.000
10.000 1.286 9.644 18650 0.000
10.200 1.299 9.903 19354 0.000
10.400 1.312 10.16 20072 0.000
10.600 1.325 10.42 20804 0.000
10.800 1.337 10.69 21550 0.000
11.000 1.350 10.96 22310 0.000
11.200 1.363 11.23 23084 0.000
11.400 1.376 11.50 23872 0.000
11.600 1.389 11.78 24674 0.000
11.800 1.402 12.06 25490 0.000
12.000 1.415 12.34 26321 0.000
12.200 1.428 12.63 27166 0.000
12.400 1.440 12.91 28025 0.000
12.600 1.453 13.20 28899 0.000
12.800 1.466 13.49 29788 0.000
13.000 1.479 13.79 30691 0.000
13.200 1.492 14.09 31609 0.000
13.400 1.505 14.39 32541 0.000
13.600 1.518 14.69 33489 0.000
13.800 1.531 14.99 34451 0.000
14.000 1.543 15.30 35429 0.000
14.200 1.556 15.61 36421 0.000
14.400 1.569 15.92 37429 0.000
14.600 1.582 16.24 38452 0.000
14.800 1.595 16.56 39490 0.000
15.000 1.608 16.88 40544 0.000
15.200 1.621 17.20 41613 0.000
15.400 1.634 17.53 42698 0.000
15.600 1.647 17.85 43798 0.000
15.800 1.659 18.18 44914 0.000
16.000 1.672 18.52 46045 0.000
16.200 1.685 18.85 47193 0.000
16.400 1.698 19.19 48356 0.000
16.600 1.711 19.53 49535 0.000
16.800 1.724 19.88 50731 0.000
17.000 1.737 20.22 51942 0.000
17.200 1.750 20.57 53170 0.000
17.400 1.763 20.92 54414 0.000
17.600 1.775 21.28 55674 0.000
17.800 1.788 21.63 56950 0.000
18.000 1.801 21.99 58243 0.000
18.200 1.814 22.35 59553 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 21 Channel 1
Bottom Length: 700.00 ft.
Bottom Width: 40.00 ft.
Manning's n: 0.025
Channel bottom slope 1: 0.02 To 1
Channel Left side slope 0: 2 To 1
Channel right side slope 2: 2 To 1
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Element Flows To:
Outlet 1 Outlet 2
Channel Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.642 0.000 0.000 0.000
0.2000 0.655 0.129 23.10 0.000
0.4000 0.668 0.262 73.49 0.000
0.6000 0.681 0.397 144.7 0.000
0.8000 0.694 0.534 234.3 0.000
1.0000 0.707 0.675 340.7 0.000
1.2000 0.720 0.817 462.9 0.000
1.4000 0.732 0.962 600.1 0.000
1.6000 0.745 1.110 751.7 0.000
1.8000 0.758 1.261 917.4 0.000
2.0000 0.771 1.414 1096. 0.000
2.2000 0.784 1.569 1289. 0.000
2.4000 0.797 1.727 1495. 0.000
2.6000 0.810 1.888 1714. 0.000
2.8000 0.822 2.052 1945. 0.000
3.0000 0.835 2.217 2189. 0.000
3.2000 0.848 2.386 2446. 0.000
3.4000 0.861 2.557 2716. 0.000
3.6000 0.874 2.730 2998. 0.000
3.8000 0.887 2.907 3292. 0.000
4.0000 0.900 3.085 3599. 0.000
4.2000 0.913 3.267 3918. 0.000
4.4000 0.925 3.451 4249. 0.000
4.6000 0.938 3.637 4593. 0.000
4.8000 0.951 3.826 4949. 0.000
5.0000 0.964 4.018 5317. 0.000
5.2000 0.977 4.212 5698. 0.000
5.4000 0.990 4.409 6091. 0.000
5.6000 1.003 4.608 6497. 0.000
5.8000 1.015 4.810 6915. 0.000
6.0000 1.028 5.014 7345. 0.000
6.2000 1.041 5.221 7788. 0.000
6.4000 1.054 5.431 8244. 0.000
6.6000 1.067 5.643 8712. 0.000
6.8000 1.080 5.858 9193. 0.000
7.0000 1.093 6.075 9686. 0.000
7.2000 1.106 6.295 10192 0.000
7.4000 1.118 6.518 10711 0.000
7.6000 1.131 6.743 11243 0.000
7.8000 1.144 6.970 11788 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 22
8.0000 1.157 7.201 12346 0.000
8.2000 1.170 7.433 12916 0.000
8.4000 1.183 7.669 13500 0.000
8.6000 1.196 7.907 14097 0.000
8.8000 1.209 8.147 14708 0.000
9.0000 1.221 8.390 15331 0.000
9.2000 1.234 8.636 15968 0.000
9.4000 1.247 8.884 16618 0.000
9.6000 1.260 9.135 17282 0.000
9.8000 1.273 9.389 17959 0.000
10.000 1.286 9.644 18650 0.000
10.200 1.299 9.903 19354 0.000
10.400 1.312 10.16 20072 0.000
10.600 1.325 10.42 20804 0.000
10.800 1.337 10.69 21550 0.000
11.000 1.350 10.96 22310 0.000
11.200 1.363 11.23 23084 0.000
11.400 1.376 11.50 23872 0.000
11.600 1.389 11.78 24674 0.000
11.800 1.402 12.06 25490 0.000
12.000 1.415 12.34 26321 0.000
12.200 1.428 12.63 27166 0.000
12.400 1.440 12.91 28025 0.000
12.600 1.453 13.20 28899 0.000
12.800 1.466 13.49 29788 0.000
13.000 1.479 13.79 30691 0.000
13.200 1.492 14.09 31609 0.000
13.400 1.505 14.39 32541 0.000
13.600 1.518 14.69 33489 0.000
13.800 1.531 14.99 34451 0.000
14.000 1.543 15.30 35429 0.000
14.200 1.556 15.61 36421 0.000
14.400 1.569 15.92 37429 0.000
14.600 1.582 16.24 38452 0.000
14.800 1.595 16.56 39490 0.000
15.000 1.608 16.88 40544 0.000
15.200 1.621 17.20 41613 0.000
15.400 1.634 17.53 42698 0.000
15.600 1.647 17.85 43798 0.000
15.800 1.659 18.18 44914 0.000
16.000 1.672 18.52 46045 0.000
16.200 1.685 18.85 47193 0.000
16.400 1.698 19.19 48356 0.000
16.600 1.711 19.53 49535 0.000
16.800 1.724 19.88 50731 0.000
17.000 1.737 20.22 51942 0.000
17.200 1.750 20.57 53170 0.000
17.400 1.763 20.92 54414 0.000
17.600 1.775 21.28 55674 0.000
17.800 1.788 21.63 56950 0.000
18.000 1.801 21.99 58243 0.000
18.200 1.814 22.35 59553 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 23 Channel 1
Bottom Length: 700.00 ft.
Bottom Width: 40.00 ft.
Manning's n: 0.025
Channel bottom slope 1: 0.02 To 1
Channel Left side slope 0: 2 To 1
Channel right side slope 2: 2 To 1
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Element Flows To:
Outlet 1 Outlet 2
Channel Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.642 0.000 0.000 0.000
0.2000 0.655 0.129 23.10 0.000
0.4000 0.668 0.262 73.49 0.000
0.6000 0.681 0.397 144.7 0.000
0.8000 0.694 0.534 234.3 0.000
1.0000 0.707 0.675 340.7 0.000
1.2000 0.720 0.817 462.9 0.000
1.4000 0.732 0.962 600.1 0.000
1.6000 0.745 1.110 751.7 0.000
1.8000 0.758 1.261 917.4 0.000
2.0000 0.771 1.414 1096. 0.000
2.2000 0.784 1.569 1289. 0.000
2.4000 0.797 1.727 1495. 0.000
2.6000 0.810 1.888 1714. 0.000
2.8000 0.822 2.052 1945. 0.000
3.0000 0.835 2.217 2189. 0.000
3.2000 0.848 2.386 2446. 0.000
3.4000 0.861 2.557 2716. 0.000
3.6000 0.874 2.730 2998. 0.000
3.8000 0.887 2.907 3292. 0.000
4.0000 0.900 3.085 3599. 0.000
4.2000 0.913 3.267 3918. 0.000
4.4000 0.925 3.451 4249. 0.000
4.6000 0.938 3.637 4593. 0.000
4.8000 0.951 3.826 4949. 0.000
5.0000 0.964 4.018 5317. 0.000
5.2000 0.977 4.212 5698. 0.000
5.4000 0.990 4.409 6091. 0.000
5.6000 1.003 4.608 6497. 0.000
5.8000 1.015 4.810 6915. 0.000
6.0000 1.028 5.014 7345. 0.000
6.2000 1.041 5.221 7788. 0.000
6.4000 1.054 5.431 8244. 0.000
6.6000 1.067 5.643 8712. 0.000
6.8000 1.080 5.858 9193. 0.000
7.0000 1.093 6.075 9686. 0.000
7.2000 1.106 6.295 10192 0.000
7.4000 1.118 6.518 10711 0.000
7.6000 1.131 6.743 11243 0.000
7.8000 1.144 6.970 11788 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 24
8.0000 1.157 7.201 12346 0.000
8.2000 1.170 7.433 12916 0.000
8.4000 1.183 7.669 13500 0.000
8.6000 1.196 7.907 14097 0.000
8.8000 1.209 8.147 14708 0.000
9.0000 1.221 8.390 15331 0.000
9.2000 1.234 8.636 15968 0.000
9.4000 1.247 8.884 16618 0.000
9.6000 1.260 9.135 17282 0.000
9.8000 1.273 9.389 17959 0.000
10.000 1.286 9.644 18650 0.000
10.200 1.299 9.903 19354 0.000
10.400 1.312 10.16 20072 0.000
10.600 1.325 10.42 20804 0.000
10.800 1.337 10.69 21550 0.000
11.000 1.350 10.96 22310 0.000
11.200 1.363 11.23 23084 0.000
11.400 1.376 11.50 23872 0.000
11.600 1.389 11.78 24674 0.000
11.800 1.402 12.06 25490 0.000
12.000 1.415 12.34 26321 0.000
12.200 1.428 12.63 27166 0.000
12.400 1.440 12.91 28025 0.000
12.600 1.453 13.20 28899 0.000
12.800 1.466 13.49 29788 0.000
13.000 1.479 13.79 30691 0.000
13.200 1.492 14.09 31609 0.000
13.400 1.505 14.39 32541 0.000
13.600 1.518 14.69 33489 0.000
13.800 1.531 14.99 34451 0.000
14.000 1.543 15.30 35429 0.000
14.200 1.556 15.61 36421 0.000
14.400 1.569 15.92 37429 0.000
14.600 1.582 16.24 38452 0.000
14.800 1.595 16.56 39490 0.000
15.000 1.608 16.88 40544 0.000
15.200 1.621 17.20 41613 0.000
15.400 1.634 17.53 42698 0.000
15.600 1.647 17.85 43798 0.000
15.800 1.659 18.18 44914 0.000
16.000 1.672 18.52 46045 0.000
16.200 1.685 18.85 47193 0.000
16.400 1.698 19.19 48356 0.000
16.600 1.711 19.53 49535 0.000
16.800 1.724 19.88 50731 0.000
17.000 1.737 20.22 51942 0.000
17.200 1.750 20.57 53170 0.000
17.400 1.763 20.92 54414 0.000
17.600 1.775 21.28 55674 0.000
17.800 1.788 21.63 56950 0.000
18.000 1.801 21.99 58243 0.000
18.200 1.814 22.35 59553 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 25 Channel 1
Bottom Length: 700.00 ft.
Bottom Width: 40.00 ft.
Manning's n: 0.025
Channel bottom slope 1: 0.02 To 1
Channel Left side slope 0: 2 To 1
Channel right side slope 2: 2 To 1
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Element Flows To:
Outlet 1 Outlet 2
Channel Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.642 0.000 0.000 0.000
0.2000 0.655 0.129 23.10 0.000
0.4000 0.668 0.262 73.49 0.000
0.6000 0.681 0.397 144.7 0.000
0.8000 0.694 0.534 234.3 0.000
1.0000 0.707 0.675 340.7 0.000
1.2000 0.720 0.817 462.9 0.000
1.4000 0.732 0.962 600.1 0.000
1.6000 0.745 1.110 751.7 0.000
1.8000 0.758 1.261 917.4 0.000
2.0000 0.771 1.414 1096. 0.000
2.2000 0.784 1.569 1289. 0.000
2.4000 0.797 1.727 1495. 0.000
2.6000 0.810 1.888 1714. 0.000
2.8000 0.822 2.052 1945. 0.000
3.0000 0.835 2.217 2189. 0.000
3.2000 0.848 2.386 2446. 0.000
3.4000 0.861 2.557 2716. 0.000
3.6000 0.874 2.730 2998. 0.000
3.8000 0.887 2.907 3292. 0.000
4.0000 0.900 3.085 3599. 0.000
4.2000 0.913 3.267 3918. 0.000
4.4000 0.925 3.451 4249. 0.000
4.6000 0.938 3.637 4593. 0.000
4.8000 0.951 3.826 4949. 0.000
5.0000 0.964 4.018 5317. 0.000
5.2000 0.977 4.212 5698. 0.000
5.4000 0.990 4.409 6091. 0.000
5.6000 1.003 4.608 6497. 0.000
5.8000 1.015 4.810 6915. 0.000
6.0000 1.028 5.014 7345. 0.000
6.2000 1.041 5.221 7788. 0.000
6.4000 1.054 5.431 8244. 0.000
6.6000 1.067 5.643 8712. 0.000
6.8000 1.080 5.858 9193. 0.000
7.0000 1.093 6.075 9686. 0.000
7.2000 1.106 6.295 10192 0.000
7.4000 1.118 6.518 10711 0.000
7.6000 1.131 6.743 11243 0.000
7.8000 1.144 6.970 11788 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 26
8.0000 1.157 7.201 12346 0.000
8.2000 1.170 7.433 12916 0.000
8.4000 1.183 7.669 13500 0.000
8.6000 1.196 7.907 14097 0.000
8.8000 1.209 8.147 14708 0.000
9.0000 1.221 8.390 15331 0.000
9.2000 1.234 8.636 15968 0.000
9.4000 1.247 8.884 16618 0.000
9.6000 1.260 9.135 17282 0.000
9.8000 1.273 9.389 17959 0.000
10.000 1.286 9.644 18650 0.000
10.200 1.299 9.903 19354 0.000
10.400 1.312 10.16 20072 0.000
10.600 1.325 10.42 20804 0.000
10.800 1.337 10.69 21550 0.000
11.000 1.350 10.96 22310 0.000
11.200 1.363 11.23 23084 0.000
11.400 1.376 11.50 23872 0.000
11.600 1.389 11.78 24674 0.000
11.800 1.402 12.06 25490 0.000
12.000 1.415 12.34 26321 0.000
12.200 1.428 12.63 27166 0.000
12.400 1.440 12.91 28025 0.000
12.600 1.453 13.20 28899 0.000
12.800 1.466 13.49 29788 0.000
13.000 1.479 13.79 30691 0.000
13.200 1.492 14.09 31609 0.000
13.400 1.505 14.39 32541 0.000
13.600 1.518 14.69 33489 0.000
13.800 1.531 14.99 34451 0.000
14.000 1.543 15.30 35429 0.000
14.200 1.556 15.61 36421 0.000
14.400 1.569 15.92 37429 0.000
14.600 1.582 16.24 38452 0.000
14.800 1.595 16.56 39490 0.000
15.000 1.608 16.88 40544 0.000
15.200 1.621 17.20 41613 0.000
15.400 1.634 17.53 42698 0.000
15.600 1.647 17.85 43798 0.000
15.800 1.659 18.18 44914 0.000
16.000 1.672 18.52 46045 0.000
16.200 1.685 18.85 47193 0.000
16.400 1.698 19.19 48356 0.000
16.600 1.711 19.53 49535 0.000
16.800 1.724 19.88 50731 0.000
17.000 1.737 20.22 51942 0.000
17.200 1.750 20.57 53170 0.000
17.400 1.763 20.92 54414 0.000
17.600 1.775 21.28 55674 0.000
17.800 1.788 21.63 56950 0.000
18.000 1.801 21.99 58243 0.000
18.200 1.814 22.35 59553 0.000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 27 Mitigated Routing
Infilt Planter 1
Bottom Length: 166.00 ft.
Bottom Width: 103.00 ft.
Material thickness of first layer: 1
Material type for first layer: Sand
Material thickness of second layer: 4
Material type for second layer: GRAVEL
Material thickness of third layer: 0
Material type for third layer: GRAVEL
Infiltration On
Infiltration rate: 0
Infiltration safety factor: 1
Total Volume Infiltrated (ac-ft): 0
Total Volume Through Riser (ac-ft): 271.658
Total Volume Through Facility (ac-ft): 271.658
Percent Infiltrated: 0
Total Precip Applied to Facility: 17.774
Total Evap From Facility: 16.209
Underdrain used
Underdrain Diameter (ft): 0.5
Orifice Diameter (in): 0.67
Offset (in): 0
Flow Through Underdrain (ac-ft): 168.188
Total Outflow (ac-ft): 271.658
Percent Through Underdrain: 61.91
Discharge Structure
Riser Height: 2.5 ft.
Riser Diameter: 8 in.
Element Flows To:
Outlet 1 Outlet 2
In Ground Infilt Planter Box Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.3925 0.0000 0.0000 0.0000
0.1154 0.3925 0.0453 0.0000 0.0000
0.2308 0.3925 0.0906 0.0000 0.0000
0.3462 0.3925 0.1359 0.0000 0.0000
0.4615 0.3925 0.1812 0.0000 0.0000
0.5769 0.3925 0.2265 0.0000 0.0000
0.6923 0.3925 0.2717 0.0000 0.0000
0.8077 0.3925 0.3170 0.0000 0.0000
0.9231 0.3925 0.3623 0.0000 0.0000
1.0385 0.3925 0.4076 0.0000 0.0000
1.1538 0.3925 0.4529 0.0000 0.0000
1.2692 0.3925 0.4982 0.0000 0.0000
1.3846 0.3925 0.5435 0.0000 0.0000
1.5000 0.3925 0.5888 0.0000 0.0000
1.6154 0.3925 0.6341 0.0000 0.0000
1.7308 0.3925 0.6794 0.0000 0.0000
1.8462 0.3925 0.7246 0.0000 0.0000
1.9615 0.3925 0.7699 0.0000 0.0000
2.0769 0.3925 0.8152 0.0000 0.0000
2.1923 0.3925 0.8605 0.0000 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 28
2.3077 0.3925 0.9058 0.0000 0.0000
2.4231 0.3925 0.9511 0.0000 0.0000
2.5385 0.3925 0.9964 0.0000 0.0000
2.6538 0.3925 1.0417 0.0000 0.0000
2.7692 0.3925 1.0870 0.0000 0.0000
2.8846 0.3925 1.1323 0.0000 0.0000
3.0000 0.3925 1.1775 0.0000 0.0000
3.1154 0.3925 1.2228 0.0000 0.0000
3.2308 0.3925 1.2681 0.0000 0.0000
3.3462 0.3925 1.3134 0.0000 0.0000
3.4615 0.3925 1.3587 0.0000 0.0000
3.5769 0.3925 1.4040 0.0000 0.0000
3.6923 0.3925 1.4493 0.0000 0.0000
3.8077 0.3925 1.4946 0.0000 0.0000
3.9231 0.3925 1.5399 0.0000 0.0000
4.0385 0.3925 1.5852 0.0000 0.0000
4.1538 0.3925 1.6305 0.0000 0.0000
4.2692 0.3925 1.6757 0.0000 0.0000
4.3846 0.3925 1.7210 0.0000 0.0000
4.5000 0.3925 1.7663 0.0000 0.0000
4.6154 0.3925 1.8116 0.0000 0.0000
4.7308 0.3925 1.8569 0.0000 0.0000
4.8462 0.3925 1.9022 0.0000 0.0000
4.9615 0.3925 1.9475 0.0000 0.0000
In Ground Infilt Planter Box Hydraulic Table
Stage(ft)Area(ac)Volume(ac-ft)Discharge(cfs)To Amended(cfs)Infilt(cfs)
4.9615 0.3925 1.9475 0.0000 0.0232 0.0000
5.0769 0.3925 1.9928 0.0000 0.0232 0.0000
5.1923 0.3925 2.0381 0.0028 0.0232 0.0000
5.3077 0.3925 2.0834 0.0040 0.0232 0.0000
5.4231 0.3925 2.1286 0.0049 0.0232 0.0000
5.5385 0.3925 2.1739 0.0057 0.0232 0.0000
5.6538 0.3925 2.2192 0.0064 0.0232 0.0000
5.7692 0.3925 2.2645 0.0070 0.0232 0.0000
5.8846 0.3925 2.3098 0.0075 0.0232 0.0000
6.0000 0.3925 2.3551 0.0081 0.0232 0.0000
6.1154 0.3925 2.4004 0.0086 0.0232 0.0000
6.2308 0.3925 2.4457 0.0090 0.0232 0.0000
6.3462 0.3925 2.4910 0.0095 0.0232 0.0000
6.4615 0.3925 2.5363 0.0099 0.0232 0.0000
6.5769 0.3925 2.5815 0.0103 0.0232 0.0000
6.6923 0.3925 2.6268 0.0107 0.0232 0.0000
6.8077 0.3925 2.6721 0.0110 0.0232 0.0000
6.9231 0.3925 2.7174 0.0116 0.0232 0.0000
7.0385 0.3925 2.7627 0.0123 0.0232 0.0000
7.1538 0.3925 2.8080 0.0129 0.0232 0.0000
7.2692 0.3925 2.8533 0.0135 0.0232 0.0000
7.3846 0.3925 2.8986 0.0141 0.0232 0.0000
7.5000 0.3925 2.9439 0.0147 0.0232 0.0000
7.6154 0.3925 2.9892 0.0152 0.0232 0.0000
7.7308 0.3925 3.0345 0.0157 0.0232 0.0000
7.8462 0.3925 3.0797 0.0163 0.0232 0.0000
7.9615 0.3925 3.1250 0.0167 0.0232 0.0000
8.0769 0.3925 3.1703 0.0172 0.0232 0.0000
8.1923 0.3925 3.2156 0.0177 0.0232 0.0000
8.3077 0.3925 3.2609 0.0181 0.0232 0.0000
8.4231 0.3925 3.3062 0.0186 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 29
8.5385 0.3925 3.3515 0.0190 0.0232 0.0000
8.6538 0.3925 3.3968 0.0194 0.0232 0.0000
8.7692 0.3925 3.4421 0.0198 0.0232 0.0000
8.8846 0.3925 3.4874 0.0202 0.0232 0.0000
9.0000 0.3925 3.5326 0.0206 0.0232 0.0000
9.1154 0.3925 3.5779 0.0210 0.0232 0.0000
9.2308 0.3925 3.6232 0.0214 0.0232 0.0000
9.3462 0.3925 3.6685 0.0218 0.0232 0.0000
9.4615 0.3925 3.7138 0.0221 0.0232 0.0000
9.5769 0.3925 3.7591 0.0225 0.0232 0.0000
9.6923 0.3925 3.8044 0.0229 0.0232 0.0000
9.8077 0.3925 3.8497 0.0232 0.0232 0.0000
9.9231 0.3925 3.8950 0.0236 0.0232 0.0000
10.038 0.3925 3.9403 26.858 0.0232 0.0000
10.154 0.3925 3.9855 28.682 0.0232 0.0000
10.269 0.3925 4.0308 30.546 0.0232 0.0000
10.385 0.3925 4.0761 32.448 0.0232 0.0000
10.500 0.3925 4.1214 34.388 0.0232 0.0000
10.615 0.3925 4.1667 36.365 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 30 Infilt Pla Surface 1
Element Flows To:
Outlet 1 Outlet 2
Infilt Planter 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 31 Infilt Planter 1
Bottom Length: 668.00 ft.
Bottom Width: 30.00 ft.
Material thickness of first layer: 1
Material type for first layer: Sand
Material thickness of second layer: 4
Material type for second layer: GRAVEL
Material thickness of third layer: 0
Material type for third layer: GRAVEL
Infiltration On
Infiltration rate: 0
Infiltration safety factor: 1
Total Volume Infiltrated (ac-ft): 0
Total Volume Through Riser (ac-ft): 383.397
Total Volume Through Facility (ac-ft): 383.397
Percent Infiltrated: 0
Total Precip Applied to Facility: 20.622
Total Evap From Facility: 17.527
Underdrain used
Underdrain Diameter (ft): 0.5
Orifice Diameter (in): 0.67
Offset (in): 0
Flow Through Underdrain (ac-ft): 141.161
Total Outflow (ac-ft): 383.397
Percent Through Underdrain: 36.82
Discharge Structure
Riser Height: 1 ft.
Riser Diameter: 8 in.
Element Flows To:
Outlet 1 Outlet 2
In Ground Infilt Planter Box Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.4601 0.0000 0.0000 0.0000
0.0824 0.4601 0.0379 0.0000 0.0000
0.1648 0.4601 0.0758 0.0000 0.0000
0.2473 0.4601 0.1137 0.0000 0.0000
0.3297 0.4601 0.1517 0.0000 0.0000
0.4121 0.4601 0.1896 0.0000 0.0000
0.4945 0.4601 0.2275 0.0000 0.0000
0.5769 0.4601 0.2654 0.0000 0.0000
0.6593 0.4601 0.3033 0.0000 0.0000
0.7418 0.4601 0.3412 0.0000 0.0000
0.8242 0.4601 0.3792 0.0000 0.0000
0.9066 0.4601 0.4171 0.0000 0.0000
0.9890 0.4601 0.4550 0.0000 0.0000
1.0714 0.4601 0.4929 0.0000 0.0000
1.1538 0.4601 0.5308 0.0000 0.0000
1.2363 0.4601 0.5687 0.0000 0.0000
1.3187 0.4601 0.6067 0.0000 0.0000
1.4011 0.4601 0.6446 0.0000 0.0000
1.4835 0.4601 0.6825 0.0000 0.0000
1.5659 0.4601 0.7204 0.0000 0.0000
1.6484 0.4601 0.7583 0.0000 0.0000
1.7308 0.4601 0.7962 0.0000 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 32
1.8132 0.4601 0.8342 0.0000 0.0000
1.8956 0.4601 0.8721 0.0000 0.0000
1.9780 0.4601 0.9100 0.0000 0.0000
2.0604 0.4601 0.9479 0.0000 0.0000
2.1429 0.4601 0.9858 0.0000 0.0000
2.2253 0.4601 1.0237 0.0000 0.0000
2.3077 0.4601 1.0617 0.0000 0.0000
2.3901 0.4601 1.0996 0.0000 0.0000
2.4725 0.4601 1.1375 0.0000 0.0000
2.5549 0.4601 1.1754 0.0000 0.0000
2.6374 0.4601 1.2133 0.0000 0.0000
2.7198 0.4601 1.2512 0.0000 0.0000
2.8022 0.4601 1.2892 0.0000 0.0000
2.8846 0.4601 1.3271 0.0000 0.0000
2.9670 0.4601 1.3650 0.0000 0.0000
3.0495 0.4601 1.4029 0.0000 0.0000
3.1319 0.4601 1.4408 0.0000 0.0000
3.2143 0.4601 1.4787 0.0000 0.0000
3.2967 0.4601 1.5167 0.0000 0.0000
3.3791 0.4601 1.5546 0.0000 0.0000
3.4615 0.4601 1.5925 0.0000 0.0000
3.5440 0.4601 1.6304 0.0000 0.0000
3.6264 0.4601 1.6683 0.0000 0.0000
3.7088 0.4601 1.7062 0.0000 0.0000
3.7912 0.4601 1.7442 0.0000 0.0000
3.8736 0.4601 1.7821 0.0000 0.0000
3.9560 0.4601 1.8200 0.0000 0.0000
4.0385 0.4601 1.8579 0.0000 0.0000
4.1209 0.4601 1.8958 0.0000 0.0000
4.2033 0.4601 1.9337 0.0000 0.0000
4.2857 0.4601 1.9717 0.0000 0.0000
4.3681 0.4601 2.0096 0.0000 0.0000
4.4505 0.4601 2.0475 0.0000 0.0000
4.5330 0.4601 2.0854 0.0000 0.0000
4.6154 0.4601 2.1233 0.0000 0.0000
4.6978 0.4601 2.1612 0.0000 0.0000
4.7802 0.4601 2.1992 0.0000 0.0000
4.8626 0.4601 2.2371 0.0000 0.0000
4.9451 0.4601 2.2750 0.0000 0.0000
In Ground Infilt Planter Box Hydraulic Table
Stage(ft)Area(ac)Volume(ac-ft)Discharge(cfs)To Amended(cfs)Infilt(cfs)
4.9451 0.4601 2.2750 0.0000 0.0232 0.0000
5.0275 0.4601 2.3129 0.0000 0.0232 0.0000
5.1099 0.4601 2.3508 0.0016 0.0232 0.0000
5.1923 0.4601 2.3887 0.0030 0.0232 0.0000
5.2747 0.4601 2.4267 0.0038 0.0232 0.0000
5.3571 0.4601 2.4646 0.0046 0.0232 0.0000
5.4396 0.4601 2.5025 0.0052 0.0232 0.0000
5.5220 0.4601 2.5404 0.0057 0.0232 0.0000
5.6044 0.4601 2.5783 0.0062 0.0232 0.0000
5.6868 0.4601 2.6162 0.0066 0.0232 0.0000
5.7692 0.4601 2.6542 0.0071 0.0232 0.0000
5.8516 0.4601 2.6921 0.0075 0.0232 0.0000
5.9341 0.4601 2.7300 0.0078 0.0232 0.0000
6.0165 0.4601 2.7679 0.0082 0.0232 0.0000
6.0989 0.4601 2.8058 0.0086 0.0232 0.0000
6.1813 0.4601 2.8437 0.0089 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 33
6.2637 0.4601 2.8817 0.0092 0.0232 0.0000
6.3462 0.4601 2.9196 0.0095 0.0232 0.0000
6.4286 0.4601 2.9575 0.0098 0.0232 0.0000
6.5110 0.4601 2.9954 0.0101 0.0232 0.0000
6.5934 0.4601 3.0333 0.0104 0.0232 0.0000
6.6758 0.4601 3.0712 0.0107 0.0232 0.0000
6.7582 0.4601 3.1092 0.0109 0.0232 0.0000
6.8407 0.4601 3.1471 0.0112 0.0232 0.0000
6.9231 0.4601 3.1850 0.0116 0.0232 0.0000
7.0055 0.4601 3.2229 0.0121 0.0232 0.0000
7.0879 0.4601 3.2608 0.0126 0.0232 0.0000
7.1703 0.4601 3.2987 0.0130 0.0232 0.0000
7.2527 0.4601 3.3367 0.0135 0.0232 0.0000
7.3352 0.4601 3.3746 0.0139 0.0232 0.0000
7.4176 0.4601 3.4125 0.0143 0.0232 0.0000
7.5000 0.4601 3.4504 0.0147 0.0232 0.0000
7.5824 0.4601 3.4883 0.0151 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 34 Infilt Pla Surface 1
Element Flows To:
Outlet 1 Outlet 2
Infilt Planter 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 35 Infilt Planter 1
Bottom Length: 250.00 ft.
Bottom Width: 60.00 ft.
Material thickness of first layer: 1
Material type for first layer: Sand
Material thickness of second layer: 4
Material type for second layer: GRAVEL
Material thickness of third layer: 0
Material type for third layer: GRAVEL
Infiltration On
Infiltration rate: 0
Infiltration safety factor: 1
Total Volume Infiltrated (ac-ft): 0
Total Volume Through Riser (ac-ft): 446.771
Total Volume Through Facility (ac-ft): 446.771
Percent Infiltrated: 0
Total Precip Applied to Facility: 15.349
Total Evap From Facility: 13.048
Underdrain used
Underdrain Diameter (ft): 0.5
Orifice Diameter (in): 0.67
Offset (in): 0
Flow Through Underdrain (ac-ft): 131.57
Total Outflow (ac-ft): 446.771
Percent Through Underdrain: 29.45
Discharge Structure
Riser Height: 1 ft.
Riser Diameter: 8 in.
Element Flows To:
Outlet 1 Outlet 2
In Ground Infilt Planter Box Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.3444 0.0000 0.0000 0.0000
0.0824 0.3444 0.0284 0.0000 0.0000
0.1648 0.3444 0.0568 0.0000 0.0000
0.2473 0.3444 0.0851 0.0000 0.0000
0.3297 0.3444 0.1135 0.0000 0.0000
0.4121 0.3444 0.1419 0.0000 0.0000
0.4945 0.3444 0.1703 0.0000 0.0000
0.5769 0.3444 0.1987 0.0000 0.0000
0.6593 0.3444 0.2270 0.0000 0.0000
0.7418 0.3444 0.2554 0.0000 0.0000
0.8242 0.3444 0.2838 0.0000 0.0000
0.9066 0.3444 0.3122 0.0000 0.0000
0.9890 0.3444 0.3406 0.0000 0.0000
1.0714 0.3444 0.3689 0.0000 0.0000
1.1538 0.3444 0.3973 0.0000 0.0000
1.2363 0.3444 0.4257 0.0000 0.0000
1.3187 0.3444 0.4541 0.0000 0.0000
1.4011 0.3444 0.4825 0.0000 0.0000
1.4835 0.3444 0.5109 0.0000 0.0000
1.5659 0.3444 0.5392 0.0000 0.0000
1.6484 0.3444 0.5676 0.0000 0.0000
1.7308 0.3444 0.5960 0.0000 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 36
1.8132 0.3444 0.6244 0.0000 0.0000
1.8956 0.3444 0.6528 0.0000 0.0000
1.9780 0.3444 0.6811 0.0000 0.0000
2.0604 0.3444 0.7095 0.0000 0.0000
2.1429 0.3444 0.7379 0.0000 0.0000
2.2253 0.3444 0.7663 0.0000 0.0000
2.3077 0.3444 0.7947 0.0000 0.0000
2.3901 0.3444 0.8230 0.0000 0.0000
2.4725 0.3444 0.8514 0.0000 0.0000
2.5549 0.3444 0.8798 0.0000 0.0000
2.6374 0.3444 0.9082 0.0000 0.0000
2.7198 0.3444 0.9366 0.0000 0.0000
2.8022 0.3444 0.9649 0.0000 0.0000
2.8846 0.3444 0.9933 0.0000 0.0000
2.9670 0.3444 1.0217 0.0000 0.0000
3.0495 0.3444 1.0501 0.0000 0.0000
3.1319 0.3444 1.0785 0.0000 0.0000
3.2143 0.3444 1.1068 0.0000 0.0000
3.2967 0.3444 1.1352 0.0000 0.0000
3.3791 0.3444 1.1636 0.0000 0.0000
3.4615 0.3444 1.1920 0.0000 0.0000
3.5440 0.3444 1.2204 0.0000 0.0000
3.6264 0.3444 1.2488 0.0000 0.0000
3.7088 0.3444 1.2771 0.0000 0.0000
3.7912 0.3444 1.3055 0.0000 0.0000
3.8736 0.3444 1.3339 0.0000 0.0000
3.9560 0.3444 1.3623 0.0000 0.0000
4.0385 0.3444 1.3907 0.0000 0.0000
4.1209 0.3444 1.4190 0.0000 0.0000
4.2033 0.3444 1.4474 0.0000 0.0000
4.2857 0.3444 1.4758 0.0000 0.0000
4.3681 0.3444 1.5042 0.0000 0.0000
4.4505 0.3444 1.5326 0.0000 0.0000
4.5330 0.3444 1.5609 0.0000 0.0000
4.6154 0.3444 1.5893 0.0000 0.0000
4.6978 0.3444 1.6177 0.0000 0.0000
4.7802 0.3444 1.6461 0.0000 0.0000
4.8626 0.3444 1.6745 0.0000 0.0000
4.9451 0.3444 1.7028 0.0000 0.0000
In Ground Infilt Planter Box Hydraulic Table
Stage(ft)Area(ac)Volume(ac-ft)Discharge(cfs)To Amended(cfs)Infilt(cfs)
4.9451 0.3444 1.7028 0.0000 0.0232 0.0000
5.0275 0.3444 1.7312 0.0000 0.0232 0.0000
5.1099 0.3444 1.7596 0.0016 0.0232 0.0000
5.1923 0.3444 1.7880 0.0030 0.0232 0.0000
5.2747 0.3444 1.8164 0.0038 0.0232 0.0000
5.3571 0.3444 1.8447 0.0046 0.0232 0.0000
5.4396 0.3444 1.8731 0.0052 0.0232 0.0000
5.5220 0.3444 1.9015 0.0057 0.0232 0.0000
5.6044 0.3444 1.9299 0.0062 0.0232 0.0000
5.6868 0.3444 1.9583 0.0066 0.0232 0.0000
5.7692 0.3444 1.9866 0.0071 0.0232 0.0000
5.8516 0.3444 2.0150 0.0075 0.0232 0.0000
5.9341 0.3444 2.0434 0.0078 0.0232 0.0000
6.0165 0.3444 2.0718 0.0082 0.0232 0.0000
6.0989 0.3444 2.1002 0.0086 0.0232 0.0000
6.1813 0.3444 2.1286 0.0089 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 37
6.2637 0.3444 2.1569 0.0092 0.0232 0.0000
6.3462 0.3444 2.1853 0.0095 0.0232 0.0000
6.4286 0.3444 2.2137 0.0098 0.0232 0.0000
6.5110 0.3444 2.2421 0.0101 0.0232 0.0000
6.5934 0.3444 2.2705 0.0104 0.0232 0.0000
6.6758 0.3444 2.2988 0.0107 0.0232 0.0000
6.7582 0.3444 2.3272 0.0109 0.0232 0.0000
6.8407 0.3444 2.3556 0.0112 0.0232 0.0000
6.9231 0.3444 2.3840 0.0116 0.0232 0.0000
7.0055 0.3444 2.4124 0.0121 0.0232 0.0000
7.0879 0.3444 2.4407 0.0126 0.0232 0.0000
7.1703 0.3444 2.4691 0.0130 0.0232 0.0000
7.2527 0.3444 2.4975 0.0135 0.0232 0.0000
7.3352 0.3444 2.5259 0.0139 0.0232 0.0000
7.4176 0.3444 2.5543 0.0143 0.0232 0.0000
7.5000 0.3444 2.5826 0.0147 0.0232 0.0000
7.5824 0.3444 2.6110 0.0151 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 38 Infilt Pla Surface 1
Element Flows To:
Outlet 1 Outlet 2
Infilt Planter 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 39 Infilt Planter 1
Bottom Length: 600.00 ft.
Bottom Width: 30.00 ft.
Material thickness of first layer: 1
Material type for first layer: Sand
Material thickness of second layer: 4
Material type for second layer: GRAVEL
Material thickness of third layer: 0
Material type for third layer: GRAVEL
Infiltration On
Infiltration rate: 0
Infiltration safety factor: 1
Total Volume Infiltrated (ac-ft): 0
Total Volume Through Riser (ac-ft): 135.308
Total Volume Through Facility (ac-ft): 135.308
Percent Infiltrated: 0
Total Precip Applied to Facility: 18.043
Total Evap From Facility: 12.844
Underdrain used
Underdrain Diameter (ft): 0.5
Orifice Diameter (in): 0.67
Offset (in): 0
Flow Through Underdrain (ac-ft): 106.105
Total Outflow (ac-ft): 135.308
Percent Through Underdrain: 78.42
Discharge Structure
Riser Height: 1.5 ft.
Riser Diameter: 8 in.
Element Flows To:
Outlet 1 Outlet 2
In Ground Infilt Planter Box Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.4132 0.0000 0.0000 0.0000
0.0934 0.4132 0.0386 0.0000 0.0000
0.1868 0.4132 0.0772 0.0000 0.0000
0.2802 0.4132 0.1158 0.0000 0.0000
0.3736 0.4132 0.1544 0.0000 0.0000
0.4670 0.4132 0.1930 0.0000 0.0000
0.5604 0.4132 0.2316 0.0000 0.0000
0.6538 0.4132 0.2702 0.0000 0.0000
0.7473 0.4132 0.3088 0.0000 0.0000
0.8407 0.4132 0.3474 0.0000 0.0000
0.9341 0.4132 0.3860 0.0000 0.0000
1.0275 0.4132 0.4246 0.0000 0.0000
1.1209 0.4132 0.4632 0.0000 0.0000
1.2143 0.4132 0.5018 0.0000 0.0000
1.3077 0.4132 0.5404 0.0000 0.0000
1.4011 0.4132 0.5790 0.0000 0.0000
1.4945 0.4132 0.6176 0.0000 0.0000
1.5879 0.4132 0.6562 0.0000 0.0000
1.6813 0.4132 0.6948 0.0000 0.0000
1.7747 0.4132 0.7334 0.0000 0.0000
1.8681 0.4132 0.7720 0.0000 0.0000
1.9615 0.4132 0.8106 0.0000 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 40
2.0549 0.4132 0.8492 0.0000 0.0000
2.1484 0.4132 0.8877 0.0000 0.0000
2.2418 0.4132 0.9263 0.0000 0.0000
2.3352 0.4132 0.9649 0.0000 0.0000
2.4286 0.4132 1.0035 0.0000 0.0000
2.5220 0.4132 1.0421 0.0000 0.0000
2.6154 0.4132 1.0807 0.0000 0.0000
2.7088 0.4132 1.1193 0.0000 0.0000
2.8022 0.4132 1.1579 0.0000 0.0000
2.8956 0.4132 1.1965 0.0000 0.0000
2.9890 0.4132 1.2351 0.0000 0.0000
3.0824 0.4132 1.2737 0.0000 0.0000
3.1758 0.4132 1.3123 0.0000 0.0000
3.2692 0.4132 1.3509 0.0000 0.0000
3.3626 0.4132 1.3895 0.0000 0.0000
3.4560 0.4132 1.4281 0.0000 0.0000
3.5495 0.4132 1.4667 0.0000 0.0000
3.6429 0.4132 1.5053 0.0000 0.0000
3.7363 0.4132 1.5439 0.0000 0.0000
3.8297 0.4132 1.5825 0.0000 0.0000
3.9231 0.4132 1.6211 0.0000 0.0000
4.0165 0.4132 1.6597 0.0000 0.0000
4.1099 0.4132 1.6983 0.0000 0.0000
4.2033 0.4132 1.7369 0.0000 0.0000
4.2967 0.4132 1.7755 0.0000 0.0000
4.3901 0.4132 1.8141 0.0000 0.0000
4.4835 0.4132 1.8527 0.0000 0.0000
4.5769 0.4132 1.8913 0.0000 0.0000
4.6703 0.4132 1.9299 0.0000 0.0000
4.7637 0.4132 1.9685 0.0000 0.0000
4.8571 0.4132 2.0071 0.0000 0.0000
4.9505 0.4132 2.0457 0.0000 0.0000
In Ground Infilt Planter Box Hydraulic Table
Stage(ft)Area(ac)Volume(ac-ft)Discharge(cfs)To Amended(cfs)Infilt(cfs)
4.9505 0.4132 2.0457 0.0000 0.0232 0.0000
5.0440 0.4132 2.0843 0.0000 0.0232 0.0000
5.1374 0.4132 2.1229 0.0021 0.0232 0.0000
5.2308 0.4132 2.1615 0.0034 0.0232 0.0000
5.3242 0.4132 2.2001 0.0042 0.0232 0.0000
5.4176 0.4132 2.2387 0.0050 0.0232 0.0000
5.5110 0.4132 2.2773 0.0056 0.0232 0.0000
5.6044 0.4132 2.3159 0.0062 0.0232 0.0000
5.6978 0.4132 2.3545 0.0067 0.0232 0.0000
5.7912 0.4132 2.3931 0.0072 0.0232 0.0000
5.8846 0.4132 2.4317 0.0076 0.0232 0.0000
5.9780 0.4132 2.4703 0.0080 0.0232 0.0000
6.0714 0.4132 2.5089 0.0084 0.0232 0.0000
6.1648 0.4132 2.5475 0.0088 0.0232 0.0000
6.2582 0.4132 2.5861 0.0092 0.0232 0.0000
6.3516 0.4132 2.6246 0.0095 0.0232 0.0000
6.4451 0.4132 2.6632 0.0099 0.0232 0.0000
6.5385 0.4132 2.7018 0.0102 0.0232 0.0000
6.6319 0.4132 2.7404 0.0105 0.0232 0.0000
6.7253 0.4132 2.7790 0.0108 0.0232 0.0000
6.8187 0.4132 2.8176 0.0111 0.0232 0.0000
6.9121 0.4132 2.8562 0.0116 0.0232 0.0000
7.0055 0.4132 2.8948 0.0121 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 41
7.0989 0.4132 2.9334 0.0126 0.0232 0.0000
7.1923 0.4132 2.9720 0.0131 0.0232 0.0000
7.2857 0.4132 3.0106 0.0136 0.0232 0.0000
7.3791 0.4132 3.0492 0.0141 0.0232 0.0000
7.4725 0.4132 3.0878 0.0146 0.0232 0.0000
7.5659 0.4132 3.1264 0.0150 0.0232 0.0000
7.6593 0.4132 3.1650 0.0154 0.0232 0.0000
7.7527 0.4132 3.2036 0.0158 0.0232 0.0000
7.8462 0.4132 3.2422 0.0163 0.0232 0.0000
7.9396 0.4132 3.2808 0.0166 0.0232 0.0000
8.0330 0.4132 3.3194 0.0170 0.0232 0.0000
8.1264 0.4132 3.3580 0.0174 0.0232 0.0000
8.2198 0.4132 3.3966 0.0178 0.0232 0.0000
8.3132 0.4132 3.4352 0.0181 0.0232 0.0000
8.4066 0.4132 3.4738 0.0185 0.0232 0.0000
8.5000 0.4132 3.5124 0.0189 0.0232 0.0000
8.5934 0.4132 3.5510 0.0192 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 42 Infilt Pla Surface 1
Element Flows To:
Outlet 1 Outlet 2
Infilt Planter 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 43 Infilt Planter 1
Bottom Length: 700.00 ft.
Bottom Width: 10.00 ft.
Material thickness of first layer: 1
Material type for first layer: Sand
Material thickness of second layer: 4
Material type for second layer: GRAVEL
Material thickness of third layer: 0
Material type for third layer: GRAVEL
Infiltration On
Infiltration rate: 0
Infiltration safety factor: 1
Total Volume Infiltrated (ac-ft): 0
Total Volume Through Riser (ac-ft): 91.493
Total Volume Through Facility (ac-ft): 91.493
Percent Infiltrated: 0
Total Precip Applied to Facility: 6.845
Total Evap From Facility: 3.545
Underdrain used
Underdrain Diameter (ft): 0.5
Orifice Diameter (in): 0.67
Offset (in): 0
Flow Through Underdrain (ac-ft): 59.226
Total Outflow (ac-ft): 91.493
Percent Through Underdrain: 64.73
Discharge Structure
Riser Height: 1 ft.
Riser Diameter: 8 in.
Element Flows To:
Outlet 1 Outlet 2
In Ground Infilt Planter Box Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.1607 0.0000 0.0000 0.0000
0.0824 0.1607 0.0132 0.0000 0.0000
0.1648 0.1607 0.0265 0.0000 0.0000
0.2473 0.1607 0.0397 0.0000 0.0000
0.3297 0.1607 0.0530 0.0000 0.0000
0.4121 0.1607 0.0662 0.0000 0.0000
0.4945 0.1607 0.0795 0.0000 0.0000
0.5769 0.1607 0.0927 0.0000 0.0000
0.6593 0.1607 0.1060 0.0000 0.0000
0.7418 0.1607 0.1192 0.0000 0.0000
0.8242 0.1607 0.1324 0.0000 0.0000
0.9066 0.1607 0.1457 0.0000 0.0000
0.9890 0.1607 0.1589 0.0000 0.0000
1.0714 0.1607 0.1722 0.0000 0.0000
1.1538 0.1607 0.1854 0.0000 0.0000
1.2363 0.1607 0.1987 0.0000 0.0000
1.3187 0.1607 0.2119 0.0000 0.0000
1.4011 0.1607 0.2252 0.0000 0.0000
1.4835 0.1607 0.2384 0.0000 0.0000
1.5659 0.1607 0.2516 0.0000 0.0000
1.6484 0.1607 0.2649 0.0000 0.0000
1.7308 0.1607 0.2781 0.0000 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:02 PM Page 44
1.8132 0.1607 0.2914 0.0000 0.0000
1.8956 0.1607 0.3046 0.0000 0.0000
1.9780 0.1607 0.3179 0.0000 0.0000
2.0604 0.1607 0.3311 0.0000 0.0000
2.1429 0.1607 0.3444 0.0000 0.0000
2.2253 0.1607 0.3576 0.0000 0.0000
2.3077 0.1607 0.3708 0.0000 0.0000
2.3901 0.1607 0.3841 0.0000 0.0000
2.4725 0.1607 0.3973 0.0000 0.0000
2.5549 0.1607 0.4106 0.0000 0.0000
2.6374 0.1607 0.4238 0.0000 0.0000
2.7198 0.1607 0.4371 0.0000 0.0000
2.8022 0.1607 0.4503 0.0000 0.0000
2.8846 0.1607 0.4636 0.0000 0.0000
2.9670 0.1607 0.4768 0.0000 0.0000
3.0495 0.1607 0.4900 0.0000 0.0000
3.1319 0.1607 0.5033 0.0000 0.0000
3.2143 0.1607 0.5165 0.0000 0.0000
3.2967 0.1607 0.5298 0.0000 0.0000
3.3791 0.1607 0.5430 0.0000 0.0000
3.4615 0.1607 0.5563 0.0000 0.0000
3.5440 0.1607 0.5695 0.0000 0.0000
3.6264 0.1607 0.5828 0.0000 0.0000
3.7088 0.1607 0.5960 0.0000 0.0000
3.7912 0.1607 0.6092 0.0000 0.0000
3.8736 0.1607 0.6225 0.0000 0.0000
3.9560 0.1607 0.6357 0.0000 0.0000
4.0385 0.1607 0.6490 0.0000 0.0000
4.1209 0.1607 0.6622 0.0000 0.0000
4.2033 0.1607 0.6755 0.0000 0.0000
4.2857 0.1607 0.6887 0.0000 0.0000
4.3681 0.1607 0.7019 0.0000 0.0000
4.4505 0.1607 0.7152 0.0000 0.0000
4.5330 0.1607 0.7284 0.0000 0.0000
4.6154 0.1607 0.7417 0.0000 0.0000
4.6978 0.1607 0.7549 0.0000 0.0000
4.7802 0.1607 0.7682 0.0000 0.0000
4.8626 0.1607 0.7814 0.0000 0.0000
4.9451 0.1607 0.7947 0.0000 0.0000
In Ground Infilt Planter Box Hydraulic Table
Stage(ft)Area(ac)Volume(ac-ft)Discharge(cfs)To Amended(cfs)Infilt(cfs)
4.9451 0.1607 0.7947 0.0000 0.0232 0.0000
5.0275 0.1607 0.8079 0.0000 0.0232 0.0000
5.1099 0.1607 0.8211 0.0016 0.0232 0.0000
5.1923 0.1607 0.8344 0.0030 0.0232 0.0000
5.2747 0.1607 0.8476 0.0038 0.0232 0.0000
5.3571 0.1607 0.8609 0.0046 0.0232 0.0000
5.4396 0.1607 0.8741 0.0052 0.0232 0.0000
5.5220 0.1607 0.8874 0.0057 0.0232 0.0000
5.6044 0.1607 0.9006 0.0062 0.0232 0.0000
5.6868 0.1607 0.9139 0.0066 0.0232 0.0000
5.7692 0.1607 0.9271 0.0071 0.0232 0.0000
5.8516 0.1607 0.9403 0.0075 0.0232 0.0000
5.9341 0.1607 0.9536 0.0078 0.0232 0.0000
6.0165 0.1607 0.9668 0.0082 0.0232 0.0000
6.0989 0.1607 0.9801 0.0086 0.0232 0.0000
6.1813 0.1607 0.9933 0.0089 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:03 PM Page 45
6.2637 0.1607 1.0066 0.0092 0.0232 0.0000
6.3462 0.1607 1.0198 0.0095 0.0232 0.0000
6.4286 0.1607 1.0331 0.0098 0.0232 0.0000
6.5110 0.1607 1.0463 0.0101 0.0232 0.0000
6.5934 0.1607 1.0595 0.0104 0.0232 0.0000
6.6758 0.1607 1.0728 0.0107 0.0232 0.0000
6.7582 0.1607 1.0860 0.0109 0.0232 0.0000
6.8407 0.1607 1.0993 0.0112 0.0232 0.0000
6.9231 0.1607 1.1125 0.0116 0.0232 0.0000
7.0055 0.1607 1.1258 0.0121 0.0232 0.0000
7.0879 0.1607 1.1390 0.0126 0.0232 0.0000
7.1703 0.1607 1.1523 0.0130 0.0232 0.0000
7.2527 0.1607 1.1655 0.0135 0.0232 0.0000
7.3352 0.1607 1.1787 0.0139 0.0232 0.0000
7.4176 0.1607 1.1920 0.0143 0.0232 0.0000
7.5000 0.1607 1.2052 0.0147 0.0232 0.0000
7.5824 0.1607 1.2185 0.0151 0.0232 0.0000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:03 PM Page 46 Infilt Pla Surface 1
Element Flows To:
Outlet 1 Outlet 2
Infilt Planter 1
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:03 PM Page 47 Gravel Trench Bed 1
Bottom Length: 255.00 ft.
Bottom Width: 50.00 ft.
Trench bottom slope 1: 0.01 To 1
Trench Left side slope 0: 3 To 1
Trench right side slope 2: 3 To 1
Material thickness of first layer: 1
Pour Space of material for first layer: 0.15
Material thickness of second layer: 4
Pour Space of material for second layer: 0.4
Material thickness of third layer: 0
Pour Space of material for third layer: 0
Infiltration On
Infiltration rate: 5
Infiltration safety factor: 1
Wetted surface area On
Total Volume Infiltrated (ac-ft): 183.167
Total Volume Through Riser (ac-ft): 0
Total Volume Through Facility (ac-ft): 183.167
Percent Infiltrated: 100
Total Precip Applied to Facility: 0
Total Evap From Facility: 0
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Orifice 1 Diameter: 24 in. Elevation:8 ft.
Element Flows To:
Outlet 1 Outlet 2
Gravel Trench Bed Hydraulic Table
Stage(ft) Area(ac) Volume(ac-ft) Discharge(cfs) Infilt(cfs)
0.0000 0.292 0.000 0.000 0.000
0.0889 0.295 0.003 0.000 1.491
0.1778 0.298 0.007 0.000 1.507
0.2667 0.302 0.011 0.000 1.522
0.3556 0.305 0.015 0.000 1.538
0.4444 0.308 0.020 0.000 1.554
0.5333 0.311 0.024 0.000 1.570
0.6222 0.314 0.028 0.000 1.586
0.7111 0.317 0.032 0.000 1.601
0.8000 0.320 0.036 0.000 1.617
0.8889 0.323 0.041 0.000 1.633
0.9778 0.327 0.045 0.000 1.649
1.0667 0.330 0.057 0.000 1.664
1.1556 0.333 0.068 0.000 1.680
1.2444 0.336 0.080 0.000 1.696
1.3333 0.339 0.092 0.000 1.712
1.4222 0.342 0.105 0.000 1.727
1.5111 0.345 0.117 0.000 1.743
1.6000 0.348 0.129 0.000 1.759
1.6889 0.352 0.142 0.000 1.775
1.7778 0.355 0.154 0.000 1.790
1.8667 0.358 0.167 0.000 1.806
1.9556 0.361 0.180 0.000 1.822
2.0444 0.364 0.193 0.000 1.838
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:03 PM Page 48
2.1333 0.367 0.206 0.000 1.853
2.2222 0.370 0.219 0.000 1.869
2.3111 0.373 0.232 0.000 1.885
2.4000 0.377 0.245 0.000 1.901
2.4889 0.380 0.259 0.000 1.916
2.5778 0.383 0.272 0.000 1.932
2.6667 0.386 0.286 0.000 1.948
2.7556 0.389 0.300 0.000 1.964
2.8444 0.392 0.314 0.000 1.979
2.9333 0.395 0.328 0.000 1.995
3.0222 0.398 0.342 0.000 2.011
3.1111 0.402 0.356 0.000 2.027
3.2000 0.405 0.370 0.000 2.042
3.2889 0.408 0.385 0.000 2.058
3.3778 0.411 0.399 0.000 2.074
3.4667 0.414 0.414 0.000 2.090
3.5556 0.417 0.429 0.000 2.105
3.6444 0.420 0.444 0.000 2.121
3.7333 0.424 0.459 0.000 2.137
3.8222 0.427 0.474 0.000 2.153
3.9111 0.430 0.489 0.000 2.169
4.0000 0.433 0.505 0.000 2.184
4.0889 0.436 0.520 0.000 2.200
4.1778 0.439 0.536 0.000 2.216
4.2667 0.442 0.551 0.000 2.232
4.3556 0.445 0.567 0.000 2.247
4.4444 0.449 0.583 0.000 2.263
4.5333 0.452 0.599 0.000 2.279
4.6222 0.455 0.615 0.000 2.295
4.7111 0.458 0.631 0.000 2.310
4.8000 0.461 0.648 0.000 2.326
4.8889 0.464 0.664 0.000 2.342
4.9778 0.467 0.681 0.000 2.358
5.0667 0.470 0.723 0.000 2.373
5.1556 0.474 0.765 0.000 2.389
5.2444 0.477 0.807 0.000 2.405
5.3333 0.480 0.849 0.000 2.421
5.4222 0.483 0.892 0.000 2.436
5.5111 0.486 0.935 0.000 2.452
5.6000 0.489 0.979 0.000 2.468
5.6889 0.492 1.022 0.000 2.484
5.7778 0.495 1.066 0.000 2.500
5.8667 0.499 1.110 0.000 2.515
5.9556 0.502 1.155 0.000 2.531
6.0444 0.505 1.200 0.000 2.547
6.1333 0.508 1.245 0.000 2.563
6.2222 0.511 1.290 0.000 2.578
6.3111 0.514 1.336 0.000 2.594
6.4000 0.517 1.382 0.000 2.610
6.4889 0.520 1.428 0.000 2.626
6.5778 0.524 1.474 0.000 2.641
6.6667 0.527 1.521 0.000 2.657
6.7556 0.530 1.568 0.000 2.673
6.8444 0.533 1.615 0.000 2.689
6.9333 0.536 1.663 0.000 2.704
7.0222 0.539 1.711 0.000 2.720
7.1111 0.542 1.759 0.000 2.736
7.2000 0.545 1.807 0.000 2.752
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:03 PM Page 49
7.2889 0.549 1.856 0.000 2.768
7.3778 0.552 1.905 0.000 2.783
7.4667 0.555 1.954 0.000 2.799
7.5556 0.558 2.003 0.000 2.815
7.6444 0.561 2.053 0.000 2.831
7.7333 0.564 2.103 0.000 2.846
7.8222 0.567 2.154 0.000 2.862
7.9111 0.570 2.204 0.000 2.878
8.0000 0.574 2.255 0.000 2.894
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:03 PM Page 50 Analysis Results
POC 1
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #1
Total Pervious Area: 7.117
Total Impervious Area: 0
Mitigated Landuse Totals for POC #1
Total Pervious Area: 1.924
Total Impervious Area: 5.192
Flow Frequency Method: Cunnane
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 2.852206
5 year 4.566032
10 year 5.82026
25 year 7.617141
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 1.795191
5 year 3.429398
10 year 4.910243
25 year 6.439638
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:40 PM Page 51 Duration Flows
Flow(cfs) Predev Mit Percentage Pass/Fail
0.2852 1265 4748 375 Fail
0.3411 1158 4102 354 Fail
0.3970 1057 3608 341 Fail
0.4529 961 3252 338 Fail
0.5089 877 2970 338 Fail
0.5648 803 2641 328 Fail
0.6207 747 2372 317 Fail
0.6766 703 2117 301 Fail
0.7325 654 1924 294 Fail
0.7884 621 1748 281 Fail
0.8443 574 1593 277 Fail
0.9002 534 1434 268 Fail
0.9561 502 1310 260 Fail
1.0120 465 1215 261 Fail
1.0680 437 1147 262 Fail
1.1239 411 1066 259 Fail
1.1798 380 1000 263 Fail
1.2357 355 939 264 Fail
1.2916 333 868 260 Fail
1.3475 313 807 257 Fail
1.4034 292 755 258 Fail
1.4593 275 704 256 Fail
1.5152 258 659 255 Fail
1.5711 246 621 252 Fail
1.6270 230 572 248 Fail
1.6830 220 524 238 Fail
1.7389 204 492 241 Fail
1.7948 188 447 237 Fail
1.8507 178 422 237 Fail
1.9066 170 396 232 Fail
1.9625 163 366 224 Fail
2.0184 154 332 215 Fail
2.0743 146 313 214 Fail
2.1302 132 291 220 Fail
2.1861 127 271 213 Fail
2.2421 123 249 202 Fail
2.2980 116 233 200 Fail
2.3539 114 208 182 Fail
2.4098 107 200 186 Fail
2.4657 102 185 181 Fail
2.5216 99 171 172 Fail
2.5775 96 166 172 Fail
2.6334 91 155 170 Fail
2.6893 85 143 168 Fail
2.7452 79 135 170 Fail
2.8011 72 124 172 Fail
2.8571 63 116 184 Fail
2.9130 61 110 180 Fail
2.9689 55 102 185 Fail
3.0248 52 95 182 Fail
3.0807 51 91 178 Fail
3.1366 48 87 181 Fail
3.1925 45 80 177 Fail
3.2484 43 78 181 Fail
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:41 PM Page 52
3.3043 41 77 187 Fail
3.3602 39 70 179 Fail
3.4162 38 68 178 Fail
3.4721 36 65 180 Fail
3.5280 36 62 172 Fail
3.5839 35 60 171 Fail
3.6398 32 56 175 Fail
3.6957 31 54 174 Fail
3.7516 29 52 179 Fail
3.8075 29 49 168 Fail
3.8634 28 46 164 Fail
3.9193 28 43 153 Fail
3.9752 25 42 168 Fail
4.0312 23 40 173 Fail
4.0871 23 38 165 Fail
4.1430 23 34 147 Fail
4.1989 22 31 140 Fail
4.2548 21 29 138 Fail
4.3107 21 27 128 Fail
4.3666 21 24 114 Fail
4.4225 21 23 109 Pass
4.4784 20 23 115 Fail
4.5343 20 21 104 Pass
4.5903 19 17 89 Pass
4.6462 15 16 106 Pass
4.7021 14 14 100 Pass
4.7580 13 14 107 Pass
4.8139 12 13 108 Pass
4.8698 12 13 108 Pass
4.9257 12 13 108 Pass
4.9816 11 12 109 Pass
5.0375 10 12 120 Fail
5.0934 10 12 120 Fail
5.1493 10 11 110 Pass
5.2053 10 11 110 Pass
5.2612 109 90 Pass
5.3171 108 80 Pass
5.373098 88 Pass
5.428998 88 Pass
5.484888 100 Pass
5.540788 100 Pass
5.596688 100 Pass
5.652587 87 Pass
5.708477 100 Pass
5.764477 100 Pass
5.820357 140 Fail
The development has an increase in flow durations
for more than a 20% increase from the 5 year to the 10
year flow.
The development has an increase in flow durations for
more than 20% of the flows for the range of the
duration analysis.
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:41 PM Page 53 Water Quality
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:26:41 PM Page 54 POC 2
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #2
Total Pervious Area: 4.417
Total Impervious Area: 0
Mitigated Landuse Totals for POC #2
Total Pervious Area: 0.138
Total Impervious Area: 4.278
Flow Frequency Method: Cunnane
Flow Frequency Return Periods for Predeveloped. POC #2
Return Period Flow(cfs)
2 year 1.770155
5 year 2.833801
10 year 3.612208
25 year 4.7274
Flow Frequency Return Periods for Mitigated. POC #2
Return Period Flow(cfs)
2 year 1.684472
5 year 1.798048
10 year 1.945907
25 year 2.016105
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:27:54 PM Page 55 Duration Flows
Flow(cfs) Predev Mit Percentage Pass/Fail
0.1770 1263 12828 1015 Fail
0.2117 1160 11179 963 Fail
0.2464 1060 10195 961 Fail
0.2811 960 9607 1000 Fail
0.3158 879 8752 995 Fail
0.3505 803 7953 990 Fail
0.3852 747 7545 1010 Fail
0.4199 704 6943 986 Fail
0.4546 654 6087 930 Fail
0.4893 621 5672 913 Fail
0.5240 574 5423 944 Fail
0.5587 536 5029 938 Fail
0.5934 502 4429 882 Fail
0.6281 465 4175 897 Fail
0.6628 437 3953 904 Fail
0.6975 411 3770 917 Fail
0.7322 380 3569 939 Fail
0.7669 355 3385 953 Fail
0.8016 333 3155 947 Fail
0.8363 313 2866 915 Fail
0.8710 292 2427 831 Fail
0.9057 276 2253 816 Fail
0.9404 258 2148 832 Fail
0.9751 246 2049 832 Fail
1.0098 231 1971 853 Fail
1.0445 220 1858 844 Fail
1.0792 204 1794 879 Fail
1.1139 188 1745 928 Fail
1.1486 178 1674 940 Fail
1.1833 170 1539 905 Fail
1.2180 163 1474 904 Fail
1.2527 154 1431 929 Fail
1.2874 146 1366 935 Fail
1.3221 132 1292 978 Fail
1.3568 127 1265 996 Fail
1.3915 124 1241 1000 Fail
1.4262 116 1207 1040 Fail
1.4609 114 1184 1038 Fail
1.4956 107 1151 1075 Fail
1.5303 102 926 907 Fail
1.5650 99 741 748 Fail
1.5997 96 595 619 Fail
1.6344 91 456 501 Fail
1.6691 85 309 363 Fail
1.7038 80 206 257 Fail
1.7385 72 146 202 Fail
1.7732 63 115 182 Fail
1.8079 61 87 142 Fail
1.8426 55 59 107 Pass
1.8773 52 44 84 Pass
1.9120 51 36 70 Pass
1.9467 48 24 50 Pass
1.9814 458 17 Pass
2.0161 4336 Pass
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:27:54 PM Page 56
2.0508 4124 Pass
2.0855 3900 Pass
2.1202 3800 Pass
2.1549 3600 Pass
2.1896 3600 Pass
2.2243 3500 Pass
2.2590 3200 Pass
2.2936 3100 Pass
2.3283 2900 Pass
2.3630 2900 Pass
2.3977 2800 Pass
2.4324 2800 Pass
2.4671 2500 Pass
2.5018 2300 Pass
2.5365 2300 Pass
2.5712 2300 Pass
2.6059 2200 Pass
2.6406 2100 Pass
2.6753 2100 Pass
2.7100 2100 Pass
2.7447 2100 Pass
2.7794 2000 Pass
2.8141 2000 Pass
2.8488 1900 Pass
2.8835 1500 Pass
2.9182 1400 Pass
2.9529 1300 Pass
2.9876 1200 Pass
3.0223 1200 Pass
3.0570 1200 Pass
3.0917 1100 Pass
3.1264 1000 Pass
3.1611 1000 Pass
3.1958 1000 Pass
3.2305 1000 Pass
3.2652 1000 Pass
3.2999 1000 Pass
3.3346900 Pass
3.3693900 Pass
3.4040800 Pass
3.4387800 Pass
3.4734800 Pass
3.5081800 Pass
3.5428700 Pass
3.5775700 Pass
3.6122500 Pass
The development has an increase in flow durations
for more than a 20% increase from the 5 year to the 10
year flow.
The development has an increase in flow durations for
more than 20% of the flows for the range of the
duration analysis.
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:27:54 PM Page 57 Water Quality
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:27:54 PM Page 58 POC 3
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #3
Total Pervious Area: 9.981
Total Impervious Area: 0
Mitigated Landuse Totals for POC #3
Total Pervious Area: 1.998
Total Impervious Area: 7.982
Flow Frequency Method: Cunnane
Flow Frequency Return Periods for Predeveloped. POC #3
Return Period Flow(cfs)
2 year 3.999981
5 year 6.403479
10 year 8.16243
25 year 10.682406
Flow Frequency Return Periods for Mitigated. POC #3
Return Period Flow(cfs)
2 year 3.784059
5 year 5.2474
10 year 7.824492
25 year 9.611713
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:28:56 PM Page 59 Duration Flows
Flow(cfs) Predev Mit Percentage Pass/Fail
0.4000 1267 8236 650 Fail
0.4784 1158 7247 625 Fail
0.5568 1059 6432 607 Fail
0.6352 960 5749 598 Fail
0.7136 877 5058 576 Fail
0.7920 803 4581 570 Fail
0.8704 747 4113 550 Fail
0.9489 703 3695 525 Fail
1.0273 654 3358 513 Fail
1.1057 621 3071 494 Fail
1.1841 574 2737 476 Fail
1.2625 534 2444 457 Fail
1.3409 502 2224 443 Fail
1.4193 465 2021 434 Fail
1.4977 437 1834 419 Fail
1.5761 411 1644 400 Fail
1.6545 380 1520 400 Fail
1.7329 355 1405 395 Fail
1.8113 333 1269 381 Fail
1.8898 313 1170 373 Fail
1.9682 292 1091 373 Fail
2.0466 275 1015 369 Fail
2.1250 258 937 363 Fail
2.2034 246 873 354 Fail
2.2818 231 813 351 Fail
2.3602 220 755 343 Fail
2.4386 204 705 345 Fail
2.5170 188 645 343 Fail
2.5954 178 595 334 Fail
2.6738 170 553 325 Fail
2.7523 163 511 313 Fail
2.8307 154 481 312 Fail
2.9091 146 440 301 Fail
2.9875 132 409 309 Fail
3.0659 127 377 296 Fail
3.1443 123 352 286 Fail
3.2227 116 322 277 Fail
3.3011 114 295 258 Fail
3.3795 107 271 253 Fail
3.4579 102 254 249 Fail
3.5363 99 237 239 Fail
3.6147 96 221 230 Fail
3.6932 90 210 233 Fail
3.7716 85 196 230 Fail
3.8500 80 178 222 Fail
3.9284 72 169 234 Fail
4.0068 63 155 246 Fail
4.0852 61 147 240 Fail
4.1636 55 137 249 Fail
4.2420 52 129 248 Fail
4.3204 51 119 233 Fail
4.3988 48 114 237 Fail
4.4772 45 107 237 Fail
4.5556 43 105 244 Fail
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:28:56 PM Page 60
4.6341 41 100 243 Fail
4.7125 39 93 238 Fail
4.7909 38 91 239 Fail
4.8693 36 86 238 Fail
4.9477 36 81 225 Fail
5.0261 35 78 222 Fail
5.1045 32 75 234 Fail
5.1829 31 70 225 Fail
5.2613 29 65 224 Fail
5.3397 29 63 217 Fail
5.4181 28 60 214 Fail
5.4965 28 59 210 Fail
5.5750 25 53 211 Fail
5.6534 23 51 221 Fail
5.7318 23 48 208 Fail
5.8102 23 45 195 Fail
5.8886 22 40 181 Fail
5.9670 21 37 176 Fail
6.0454 21 35 166 Fail
6.1238 21 34 161 Fail
6.2022 21 31 147 Fail
6.2806 20 30 150 Fail
6.3590 20 26 130 Fail
6.4374 19 26 136 Fail
6.5159 15 26 173 Fail
6.5943 14 25 178 Fail
6.6727 13 24 184 Fail
6.7511 12 23 191 Fail
6.8295 12 23 191 Fail
6.9079 12 22 183 Fail
6.9863 11 22 200 Fail
7.0647 10 22 220 Fail
7.1431 10 20 200 Fail
7.2215 10 20 200 Fail
7.2999 10 19 190 Fail
7.3783 10 18 180 Fail
7.4568 10 16 160 Fail
7.53529 15 166 Fail
7.61369 14 155 Fail
7.69208 14 175 Fail
7.77048 14 175 Fail
7.84888 14 175 Fail
7.92728 13 162 Fail
8.00567 11 157 Fail
8.08407 11 157 Fail
8.16245 11 220 Fail
The development has an increase in flow durations
for more than a 20% increase from the 5 year to the 10
year flow.
The development has an increase in flow durations for
more than 20% of the flows for the range of the
duration analysis.
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:28:56 PM Page 61 Water Quality
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:28:56 PM Page 62 POC 4
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #4
Total Pervious Area: 11.846
Total Impervious Area: 0
Mitigated Landuse Totals for POC #4
Total Pervious Area: 2.755
Total Impervious Area: 9.101
Flow Frequency Method: Cunnane
Flow Frequency Return Periods for Predeveloped. POC #4
Return Period Flow(cfs)
2 year 4.747397
5 year 7.600001
10 year 9.68762
25 year 12.678468
Flow Frequency Return Periods for Mitigated. POC #4
Return Period Flow(cfs)
2 year 4.615271
5 year 6.886257
10 year 9.993596
25 year 13.893853
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:29:52 PM Page 63 Duration Flows
Flow(cfs) Predev Mit Percentage Pass/Fail
0.4747 1266 9036 713 Fail
0.5678 1158 7925 684 Fail
0.6609 1059 6985 659 Fail
0.7539 961 6184 643 Fail
0.8470 877 5518 629 Fail
0.9400 803 4936 614 Fail
1.0331 747 4394 588 Fail
1.1262 703 3932 559 Fail
1.2192 654 3583 547 Fail
1.3123 621 3149 507 Fail
1.4053 574 2858 497 Fail
1.4984 534 2567 480 Fail
1.5915 502 2311 460 Fail
1.6845 465 2117 455 Fail
1.7776 437 1908 436 Fail
1.8706 411 1736 422 Fail
1.9637 380 1581 416 Fail
2.0567 355 1448 407 Fail
2.1498 333 1334 400 Fail
2.2429 313 1221 390 Fail
2.3359 292 1117 382 Fail
2.4290 276 1032 373 Fail
2.5220 258 964 373 Fail
2.6151 246 891 362 Fail
2.7082 230 835 363 Fail
2.8012 220 769 349 Fail
2.8943 204 709 347 Fail
2.9873 188 662 352 Fail
3.0804 178 612 343 Fail
3.1735 170 575 338 Fail
3.2665 163 540 331 Fail
3.3596 154 507 329 Fail
3.4526 146 468 320 Fail
3.5457 132 437 331 Fail
3.6388 127 398 313 Fail
3.7318 124 368 296 Fail
3.8249 116 349 300 Fail
3.9179 114 326 285 Fail
4.0110 107 306 285 Fail
4.1041 102 287 281 Fail
4.1971 99 269 271 Fail
4.2902 96 247 257 Fail
4.3832 91 234 257 Fail
4.4763 85 220 258 Fail
4.5694 79 201 254 Fail
4.6624 72 192 266 Fail
4.7555 63 177 280 Fail
4.8485 61 164 268 Fail
4.9416 55 154 280 Fail
5.0347 52 144 276 Fail
5.1277 51 135 264 Fail
5.2208 48 128 266 Fail
5.3138 45 121 268 Fail
5.4069 43 113 262 Fail
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:29:52 PM Page 64
5.4999 41 108 263 Fail
5.5930 39 101 258 Fail
5.6861 38 93 244 Fail
5.7791 36 88 244 Fail
5.8722 36 86 238 Fail
5.9652 35 83 237 Fail
6.0583 32 78 243 Fail
6.1514 31 75 241 Fail
6.2444 29 71 244 Fail
6.3375 29 67 231 Fail
6.4305 28 64 228 Fail
6.5236 28 61 217 Fail
6.6167 25 56 224 Fail
6.7097 23 52 226 Fail
6.8028 23 52 226 Fail
6.8958 23 49 213 Fail
6.9889 22 48 218 Fail
7.0820 21 46 219 Fail
7.1750 21 41 195 Fail
7.2681 21 35 166 Fail
7.3611 21 32 152 Fail
7.4542 20 32 160 Fail
7.5473 20 31 155 Fail
7.6403 19 28 147 Fail
7.7334 15 27 180 Fail
7.8264 14 27 192 Fail
7.9195 13 25 192 Fail
8.0126 12 25 208 Fail
8.1056 12 24 200 Fail
8.1987 12 21 175 Fail
8.2917 11 20 181 Fail
8.3848 10 19 190 Fail
8.4778 10 19 190 Fail
8.5709 10 19 190 Fail
8.6640 10 19 190 Fail
8.7570 10 18 180 Fail
8.8501 10 17 170 Fail
8.94319 16 177 Fail
9.03629 16 177 Fail
9.12938 15 187 Fail
9.22238 14 175 Fail
9.31548 14 175 Fail
9.40848 13 162 Fail
9.50157 13 185 Fail
9.59467 13 185 Fail
9.68765 12 240 Fail
The development has an increase in flow durations
for more than a 20% increase from the 5 year to the 10
year flow.
The development has an increase in flow durations for
more than 20% of the flows for the range of the
duration analysis.
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:29:52 PM Page 65 Water Quality
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:29:52 PM Page 66 POC 5
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #5
Total Pervious Area: 3.449
Total Impervious Area: 0
Mitigated Landuse Totals for POC #5
Total Pervious Area: 1.418
Total Impervious Area: 2.03
Flow Frequency Method: Cunnane
Flow Frequency Return Periods for Predeveloped. POC #5
Return Period Flow(cfs)
2 year 1.38222
5 year 2.212764
10 year 2.820581
25 year 3.691375
Flow Frequency Return Periods for Mitigated. POC #5
Return Period Flow(cfs)
2 year 0.020455
5 year 0.022479
10 year 0.023527
25 year 0.023569
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:30:48 PM Page 67 Duration Flows
The Facility PASSED
Flow(cfs) Predev Mit Percentage Pass/Fail
0.1382 126600 Pass
0.1653 115800 Pass
0.1924 106100 Pass
0.2195 96100 Pass
0.2466 87900 Pass
0.2737 80500 Pass
0.3008 74800 Pass
0.3279 70400 Pass
0.3550 65500 Pass
0.3821 62100 Pass
0.4092 57400 Pass
0.4363 53400 Pass
0.4634 50200 Pass
0.4905 46600 Pass
0.5175 43700 Pass
0.5446 41100 Pass
0.5717 38100 Pass
0.5988 35500 Pass
0.6259 33300 Pass
0.6530 31300 Pass
0.6801 29200 Pass
0.7072 27500 Pass
0.7343 25800 Pass
0.7614 24600 Pass
0.7885 23100 Pass
0.8156 22000 Pass
0.8427 20400 Pass
0.8698 18800 Pass
0.8969 17800 Pass
0.9240 17000 Pass
0.9511 16300 Pass
0.9782 15400 Pass
1.0052 14600 Pass
1.0323 13200 Pass
1.0594 12700 Pass
1.0865 12400 Pass
1.1136 11600 Pass
1.1407 11400 Pass
1.1678 10700 Pass
1.1949 10200 Pass
1.2220 9900 Pass
1.2491 9600 Pass
1.2762 9100 Pass
1.3033 8500 Pass
1.3304 8000 Pass
1.3575 7200 Pass
1.3846 6300 Pass
1.4117 6100 Pass
1.4388 5500 Pass
1.4659 5200 Pass
1.4929 5100 Pass
1.5200 4800 Pass
1.5471 4500 Pass
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:30:48 PM Page 68
1.5742 43 0 0 Pass
1.6013 41 0 0 Pass
1.6284 39 0 0 Pass
1.6555 38 0 0 Pass
1.6826 36 0 0 Pass
1.7097 36 0 0 Pass
1.7368 35 0 0 Pass
1.7639 32 0 0 Pass
1.7910 31 0 0 Pass
1.8181 29 0 0 Pass
1.8452 29 0 0 Pass
1.8723 28 0 0 Pass
1.8994 28 0 0 Pass
1.9265 25 0 0 Pass
1.9536 23 0 0 Pass
1.9807 23 0 0 Pass
2.0077 23 0 0 Pass
2.0348 22 0 0 Pass
2.0619 21 0 0 Pass
2.0890 21 0 0 Pass
2.1161 21 0 0 Pass
2.1432 21 0 0 Pass
2.1703 20 0 0 Pass
2.1974 20 0 0 Pass
2.2245 19 0 0 Pass
2.2516 15 0 0 Pass
2.2787 14 0 0 Pass
2.3058 13 0 0 Pass
2.3329 12 0 0 Pass
2.3600 12 0 0 Pass
2.3871 12 0 0 Pass
2.4142 11 0 0 Pass
2.4413 10 0 0 Pass
2.4684 10 0 0 Pass
2.4954 10 0 0 Pass
2.5225 10 0 0 Pass
2.5496 10 0 0 Pass
2.5767 10 0 0 Pass
2.6038 9 0 0 Pass
2.6309 9 0 0 Pass
2.6580 8 0 0 Pass
2.6851 8 0 0 Pass
2.7122 8 0 0 Pass
2.7393 8 0 0 Pass
2.7664 7 0 0 Pass
2.7935 7 0 0 Pass
2.8206 5 0 0 Pass
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:30:48 PM Page 69 Water Quality
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:30:48 PM Page 70 POC 6
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #6
Total Pervious Area: 2.073
Total Impervious Area: 0
Mitigated Landuse Totals for POC #6
Total Pervious Area: 0.168
Total Impervious Area: 1.902
Flow Frequency Method: Cunnane
Flow Frequency Return Periods for Predeveloped. POC #6
Return Period Flow(cfs)
2 year 0.830775
5 year 1.329968
10 year 1.695293
25 year 2.218678
Flow Frequency Return Periods for Mitigated. POC #6
Return Period Flow(cfs)
2 year 0.018808
5 year 0.021405
10 year 0.022974
25 year 0.023493
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:43 PM Page 71 Duration Flows
The Facility PASSED
Flow(cfs) Predev Mit Percentage Pass/Fail
0.0831 126500 Pass
0.0994 116000 Pass
0.1156 106400 Pass
0.1319 96300 Pass
0.1482 87700 Pass
0.1645 80500 Pass
0.1808 75000 Pass
0.1971 70300 Pass
0.2134 65500 Pass
0.2296 62100 Pass
0.2459 57400 Pass
0.2622 53500 Pass
0.2785 50300 Pass
0.2948 46800 Pass
0.3111 43700 Pass
0.3274 41100 Pass
0.3436 38200 Pass
0.3599 35500 Pass
0.3762 33300 Pass
0.3925 31400 Pass
0.4088 29300 Pass
0.4251 27500 Pass
0.4413 25800 Pass
0.4576 24700 Pass
0.4739 23100 Pass
0.4902 22000 Pass
0.5065 20400 Pass
0.5228 18800 Pass
0.5391 17800 Pass
0.5553 17000 Pass
0.5716 16300 Pass
0.5879 15400 Pass
0.6042 14600 Pass
0.6205 13200 Pass
0.6368 12900 Pass
0.6531 12300 Pass
0.6693 11600 Pass
0.6856 11400 Pass
0.7019 10700 Pass
0.7182 10200 Pass
0.7345 9900 Pass
0.7508 9600 Pass
0.7670 9100 Pass
0.7833 8500 Pass
0.7996 8000 Pass
0.8159 7200 Pass
0.8322 6300 Pass
0.8485 6100 Pass
0.8648 5500 Pass
0.8810 5200 Pass
0.8973 5100 Pass
0.9136 4900 Pass
0.9299 4500 Pass
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:43 PM Page 72
0.9462 43 0 0 Pass
0.9625 41 0 0 Pass
0.9788 39 0 0 Pass
0.9950 38 0 0 Pass
1.0113 36 0 0 Pass
1.0276 36 0 0 Pass
1.0439 36 0 0 Pass
1.0602 32 0 0 Pass
1.0765 31 0 0 Pass
1.0927 29 0 0 Pass
1.1090 29 0 0 Pass
1.1253 28 0 0 Pass
1.1416 28 0 0 Pass
1.1579 25 0 0 Pass
1.1742 23 0 0 Pass
1.1905 23 0 0 Pass
1.2067 23 0 0 Pass
1.2230 22 0 0 Pass
1.2393 21 0 0 Pass
1.2556 21 0 0 Pass
1.2719 21 0 0 Pass
1.2882 21 0 0 Pass
1.3045 20 0 0 Pass
1.3207 20 0 0 Pass
1.3370 19 0 0 Pass
1.3533 15 0 0 Pass
1.3696 14 0 0 Pass
1.3859 13 0 0 Pass
1.4022 12 0 0 Pass
1.4184 12 0 0 Pass
1.4347 12 0 0 Pass
1.4510 11 0 0 Pass
1.4673 10 0 0 Pass
1.4836 10 0 0 Pass
1.4999 10 0 0 Pass
1.5162 10 0 0 Pass
1.5324 10 0 0 Pass
1.5487 10 0 0 Pass
1.5650 9 0 0 Pass
1.5813 9 0 0 Pass
1.5976 8 0 0 Pass
1.6139 8 0 0 Pass
1.6302 8 0 0 Pass
1.6464 8 0 0 Pass
1.6627 7 0 0 Pass
1.6790 7 0 0 Pass
1.6953 5 0 0 Pass
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:43 PM Page 73 Water Quality
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:43 PM Page 74 Rational Method
Company Name
Designed by
Company Project Number/Name CarMax Murrieta
Drainage Area Number/Name DMA A
Date
County/City Case No.
Township
Range
Section
0.80 85th Percentile
Acres Cover Type
.311 Roofs
4.739 Concrete or Asphalt
Grouted or Gapless Paving Blocks
Compacted Soil (e.g. unpaved parking)
Decomposed Granite
Permeable Paving Blocks w/ Sand Filled Gap
Class 2 Base
Gravel or Class 2 Permeable Base
.142 Pervious Concrete / Porous Asphalt
Open and Porous Pavers
Turf block
1.924 Ornamental Landscaping
Natural (A Soil)
Natural (B Soil)
Natural (C Soil)
Natural (D Soil)
Mixed Surface Types Fraction = 0.00
Calculated Values
C = 0.66
Vu = 0.53 (in * ac)/ac
Vbmp = 13,691 ft3
Qbmp = 0.9 ft3/s
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:43 PM Page 75 Model Default Modifications
Total of 0 changes have been made.
PERLND Changes
No PERLND changes have been made.
IMPLND Changes
No IMPLND changes have been made.
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:43 PM Page 76 Appendix
Predeveloped Schematic
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:43 PM Page 77 Mitigated Schematic
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 78 Predeveloped UCI File
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 79 Mitigated UCI File
RUN
GLOBAL
WWHM4 model simulation
START 1974 10 01 END 2011 09 30
RUN INTERP OUTPUT LEVEL 3 0
RESUME 0 RUN 1 UNIT SYSTEM 1
END GLOBAL
FILES
<File> <Un#> <-----------File Name------------------------------>*** <-ID-> ***
WDM 26 Conceptual Design_0.5 Infiltration.wdm
MESSU 25 MitConceptual Design_0.5 Infiltration.MES
27 MitConceptual Design_0.5 Infiltration.L61
28 MitConceptual Design_0.5 Infiltration.L62
30 POCConceptual Design_0.5 Infiltration1.dat
31 POCConceptual Design_0.5 Infiltration2.dat
32 POCConceptual Design_0.5 Infiltration3.dat
33 POCConceptual Design_0.5 Infiltration4.dat
34 POCConceptual Design_0.5 Infiltration5.dat
35 POCConceptual Design_0.5 Infiltration6.dat
END FILES
OPN SEQUENCE
INGRP INDELT 00:15
PERLND 15
PERLND 13
PERLND 16
IMPLND 5
IMPLND 10
IMPLND 14
RCHRES 1
RCHRES 2
RCHRES 3
RCHRES 4
RCHRES 5
RCHRES 6
RCHRES 7
RCHRES 8
RCHRES 9
RCHRES 10
RCHRES 11
COPY 1
COPY 501
COPY 3
COPY 503
COPY 4
COPY 504
COPY 5
COPY 505
COPY 6
COPY 506
COPY 2
COPY 502
DISPLY 1
DISPLY 3
DISPLY 4
DISPLY 5
DISPLY 6
DISPLY 2
END INGRP
END OPN SEQUENCE
DISPLY
DISPLY-INFO1
# - #<----------Title----------->***TRAN PIVL DIG1 FIL1 PYR DIG2 FIL2 YRND 1 Infilt Pla Surface 1 MAX 1 2 30 9
3 Infilt Pla Surface 1 MAX 1 2 32 9
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 80 4 Infilt Pla Surface 1 MAX 1 2 33 9
5 Infilt Pla Surface 1 MAX 1 2 34 9
6 Infilt Pla Surface 1 MAX 1 2 35 9
2 Gravel Trench Bed 1 MAX 1 2 31 9
END DISPLY-INFO1
END DISPLY
COPY
TIMESERIES
# - # NPT NMN ***
1 1 1
501 1 1
3 1 1
503 1 1
4 1 1
504 1 1
5 1 1
505 1 1
6 1 1
506 1 1
2 1 1
502 1 1
END TIMESERIES
END COPY
GENER
OPCODE
# # OPCD ***
END OPCODE
PARM
# # K ***
END PARM
END GENER
PERLND
GEN-INFO
<PLS ><-------Name------->NBLKS Unit-systems Printer *** # - # User t-series Engl Metr ***
in out ***
15 A,Urban,Stee(10-20%) 1 1 1 1 27 0
13 A,Urban,Flat(0-5%) 1 1 1 1 27 0
16 A,Urban,Very S(>20%) 1 1 1 1 27 0
END GEN-INFO
*** Section PWATER***
ACTIVITY
<PLS > ************* Active Sections ***************************** # - # ATMP SNOW PWAT SED PST PWG PQAL MSTL PEST NITR PHOS TRAC *** 15 0 0 1 0 0 0 0 0 0 0 0 0
13 0 0 1 0 0 0 0 0 0 0 0 0
16 0 0 1 0 0 0 0 0 0 0 0 0
END ACTIVITY
PRINT-INFO
<PLS > ***************** Print-flags ***************************** PIVL PYR # - # ATMP SNOW PWAT SED PST PWG PQAL MSTL PEST NITR PHOS TRAC ********* 15 0 0 4 0 0 0 0 0 0 0 0 0 1 9
13 0 0 4 0 0 0 0 0 0 0 0 0 1 9
16 0 0 4 0 0 0 0 0 0 0 0 0 1 9
END PRINT-INFO
PWAT-PARM1
<PLS > PWATER variable monthly parameter value flags *** # - # CSNO RTOP UZFG VCS VUZ VNN VIFW VIRC VLE INFC HWT *** 15 0 0 0 1 0 0 0 0 1 0 0
13 0 0 0 1 0 0 0 0 1 0 0
16 0 0 0 1 0 0 0 0 1 0 0
END PWAT-PARM1
PWAT-PARM2
<PLS > PWATER input info: Part 2 ***
# - # ***FOREST LZSN INFILT LSUR SLSUR KVARY AGWRC
15 0 4.2 0.04 300 0.15 1.2 0.997
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 81 13 0 5 0.06 400 0.05 1.2 0.997
16 0 3.8 0.03 200 0.25 1.2 0.997
END PWAT-PARM2
PWAT-PARM3
<PLS > PWATER input info: Part 3 ***
# - # ***PETMAX PETMIN INFEXP INFILD DEEPFR BASETP AGWETP 15 40 35 2 2 0.06 0.03 0
13 40 35 2 2 0.06 0.03 0
16 40 35 2 2 0.06 0.03 0
END PWAT-PARM3
PWAT-PARM4
<PLS > PWATER input info: Part 4 ***
# - # CEPSC UZSN NSUR INTFW IRC LZETP ***
15 0 0.35 0.25 1.6 0.3 0
13 0 0.7 0.25 3 0.4 0
16 0 0.3 0.25 1 0.3 0
END PWAT-PARM4
MON-LZETPARM
<PLS > PWATER input info: Part 3 ***
# - # JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC *** 15 0.5 0.5 0.5 0.6 0.65 0.65 0.65 0.65 0.65 0.65 0.55 0.5 13 0.5 0.5 0.5 0.6 0.65 0.65 0.65 0.65 0.65 0.65 0.55 0.5 16 0.5 0.5 0.5 0.6 0.65 0.65 0.65 0.65 0.65 0.65 0.55 0.5
END MON-LZETPARM
MON-INTERCEP
<PLS > PWATER input info: Part 3 ***
# - # JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC *** 15 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 13 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 16 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11 0.11
END MON-INTERCEP
PWAT-STATE1
<PLS > *** Initial conditions at start of simulation
ran from 1990 to end of 1992 (pat 1-11-95) RUN 21 ***
# - # *** CEPS SURS UZS IFWS LZS AGWS GWVS
15 0 0 0.01 0 3.5 1.5 0.1
13 0 0 0.01 0 3.5 1.5 0.1
16 0 0 0.01 0 3.5 1.5 0.1
END PWAT-STATE1
END PERLND
IMPLND
GEN-INFO
<PLS ><-------Name-------> Unit-systems Printer ***
# - # User t-series Engl Metr ***
in out ***
5 Roof Area 1 1 1 27 0
10 Sidewalks,Flat(0-5%) 1 1 1 27 0
14 Parking,Flat(0-5%) 1 1 1 27 0
END GEN-INFO
*** Section IWATER***
ACTIVITY
<PLS > ************* Active Sections ***************************** # - # ATMP SNOW IWAT SLD IWG IQAL ***
5 0 0 1 0 0 0
10 0 0 1 0 0 0
14 0 0 1 0 0 0
END ACTIVITY
PRINT-INFO
<ILS > ******** Print-flags ******** PIVL PYR
# - # ATMP SNOW IWAT SLD IWG IQAL *********
5 0 0 4 0 0 0 1 9
10 0 0 4 0 0 0 1 9
14 0 0 4 0 0 0 1 9
END PRINT-INFO
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 82 IWAT-PARM1
<PLS > IWATER variable monthly parameter value flags *** # - # CSNO RTOP VRS VNN RTLI ***
5 0 0 0 0 0
10 0 0 0 0 0
14 0 0 0 0 0
END IWAT-PARM1
IWAT-PARM2
<PLS > IWATER input info: Part 2 ***
# - # *** LSUR SLSUR NSUR RETSC
5 100 0.05 0.1 0.1
10 100 0.05 0.1 0.1
14 100 0.05 0.1 0.1
END IWAT-PARM2
IWAT-PARM3
<PLS > IWATER input info: Part 3 ***
# - # ***PETMAX PETMIN
5 0 0
10 0 0
14 0 0
END IWAT-PARM3
IWAT-STATE1
<PLS > *** Initial conditions at start of simulation
# - # *** RETS SURS
5 0 0
10 0 0
14 0 0
END IWAT-STATE1
END IMPLND
SCHEMATIC
<-Source-> <--Area--> <-Target-> MBLK ***
<Name> # <-factor-> <Name> # Tbl# ***
DMA A***
PERLND 15 0.873 RCHRES 1 2
PERLND 15 0.873 RCHRES 1 3
PERLND 13 0.378 RCHRES 1 2
PERLND 13 0.378 RCHRES 1 3
PERLND 16 0.673 RCHRES 1 2
PERLND 16 0.673 RCHRES 1 3
IMPLND 5 0.311 RCHRES 1 5
IMPLND 10 0.142 RCHRES 1 5
IMPLND 14 4.739 RCHRES 1 5
DMA B***
PERLND 15 0.138 RCHRES 11 2
PERLND 15 0.138 RCHRES 11 3
IMPLND 5 0.856 RCHRES 11 5
IMPLND 10 0.076 RCHRES 11 5
IMPLND 14 3.346 RCHRES 11 5
DMA D***
PERLND 13 0.317 RCHRES 3 2
PERLND 15 0.372 RCHRES 3 2
PERLND 16 1.309 RCHRES 3 2
IMPLND 5 0.535 RCHRES 3 5
IMPLND 10 0.078 RCHRES 3 5
IMPLND 14 7.369 RCHRES 3 5
DMA E***
PERLND 13 0.522 RCHRES 5 2
PERLND 13 0.522 RCHRES 5 3
PERLND 15 2.233 RCHRES 5 2
PERLND 15 2.233 RCHRES 5 3
IMPLND 5 0.439 RCHRES 5 5
IMPLND 10 0.173 RCHRES 5 5
IMPLND 14 8.489 RCHRES 5 5
DMA C***
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 83 PERLND 13 0.273 RCHRES 7 2
PERLND 13 0.273 RCHRES 7 3
PERLND 15 0.198 RCHRES 7 2
PERLND 15 0.198 RCHRES 7 3
PERLND 16 0.947 RCHRES 7 2
PERLND 16 0.947 RCHRES 7 3
IMPLND 10 0.007 RCHRES 7 5
IMPLND 14 2.023 RCHRES 7 5
DMA F***
PERLND 13 0.168 RCHRES 9 2
IMPLND 5 0.28 RCHRES 9 5
IMPLND 10 0.092 RCHRES 9 5
IMPLND 14 1.53 RCHRES 9 5
******Routing******
PERLND 15 0.873 COPY 1 12
PERLND 13 0.378 COPY 1 12
PERLND 16 0.673 COPY 1 12
IMPLND 5 0.311 COPY 1 15
IMPLND 10 0.142 COPY 1 15
IMPLND 14 4.739 COPY 1 15
PERLND 15 0.873 COPY 1 13
PERLND 13 0.378 COPY 1 13
PERLND 16 0.673 COPY 1 13
RCHRES 1 1 COPY 1 18
RCHRES 1 RCHRES 2 8
PERLND 15 0.138 COPY 2 12
IMPLND 5 0.856 COPY 2 15
IMPLND 10 0.076 COPY 2 15
IMPLND 14 3.346 COPY 2 15
PERLND 15 0.138 COPY 2 13
PERLND 13 0.317 COPY 3 12
PERLND 15 0.372 COPY 3 12
PERLND 16 1.309 COPY 3 12
IMPLND 5 0.535 COPY 3 15
IMPLND 10 0.078 COPY 3 15
IMPLND 14 7.369 COPY 3 15
RCHRES 3 1 COPY 3 18
RCHRES 3 RCHRES 4 8
PERLND 13 0.522 COPY 4 12
PERLND 15 2.233 COPY 4 12
IMPLND 5 0.439 COPY 4 15
IMPLND 10 0.173 COPY 4 15
IMPLND 14 8.489 COPY 4 15
PERLND 13 0.522 COPY 4 13
PERLND 15 2.233 COPY 4 13
RCHRES 5 1 COPY 4 18
RCHRES 5 RCHRES 6 8
PERLND 13 0.273 COPY 5 12
PERLND 15 0.198 COPY 5 12
PERLND 16 0.947 COPY 5 12
IMPLND 10 0.007 COPY 5 15
IMPLND 14 2.023 COPY 5 15
PERLND 13 0.273 COPY 5 13
PERLND 15 0.198 COPY 5 13
PERLND 16 0.947 COPY 5 13
RCHRES 7 1 COPY 5 18
RCHRES 7 RCHRES 8 8
PERLND 13 0.168 COPY 6 12
IMPLND 5 0.28 COPY 6 15
IMPLND 10 0.092 COPY 6 15
IMPLND 14 1.53 COPY 6 15
RCHRES 9 1 COPY 6 18
RCHRES 9 RCHRES 10 8
RCHRES 2 1 COPY 501 17
RCHRES 1 1 COPY 501 17
RCHRES 4 1 COPY 503 17
RCHRES 3 1 COPY 503 17
RCHRES 6 1 COPY 504 16
RCHRES 5 1 COPY 504 17
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 84 RCHRES 8 1 COPY 505 17
RCHRES 10 1 COPY 506 17
RCHRES 11 1 COPY 502 16
END SCHEMATIC
NETWORK
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Target vols> <-Grp> <-Member-> *** <Name> # <Name> # #<-factor->strg <Name> # # <Name> # # *** COPY 501 OUTPUT MEAN 1 1 48.4 DISPLY 1 INPUT TIMSER 1
COPY 503 OUTPUT MEAN 1 1 48.4 DISPLY 3 INPUT TIMSER 1
COPY 504 OUTPUT MEAN 1 1 48.4 DISPLY 4 INPUT TIMSER 1
COPY 505 OUTPUT MEAN 1 1 48.4 DISPLY 5 INPUT TIMSER 1
COPY 506 OUTPUT MEAN 1 1 48.4 DISPLY 6 INPUT TIMSER 1
COPY 502 OUTPUT MEAN 1 1 48.4 DISPLY 2 INPUT TIMSER 1
GENER 2 OUTPUT TIMSER .0011111 RCHRES 1 EXTNL OUTDGT 1
GENER 4 OUTPUT TIMSER .0011111 RCHRES 3 EXTNL OUTDGT 1
GENER 6 OUTPUT TIMSER .0011111 RCHRES 5 EXTNL OUTDGT 1
GENER 8 OUTPUT TIMSER .0011111 RCHRES 7 EXTNL OUTDGT 1
GENER 10 OUTPUT TIMSER .0011111 RCHRES 9 EXTNL OUTDGT 1 <-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Target vols> <-Grp> <-Member-> *** <Name> # <Name> # #<-factor->strg <Name> # # <Name> # # ***
END NETWORK
RCHRES
GEN-INFO
RCHRES Name Nexits Unit Systems Printer ***
# - #<------------------><---> User T-series Engl Metr LKFG *** in out ***
1 Infilt Pla Surfa-008 3 1 1 1 28 0 1
2 Infilt Planter -007 2 1 1 1 28 0 1
3 Infilt Pla Surfa-013 3 1 1 1 28 0 1
4 Infilt Planter -012 2 1 1 1 28 0 1
5 Infilt Pla Surfa-019 3 1 1 1 28 0 1
6 Infilt Planter -018 2 1 1 1 28 0 1
7 Infilt Pla Surfa-022 3 1 1 1 28 0 1
8 Infilt Planter -021 2 1 1 1 28 0 1
9 Infilt Pla Surfa-025 3 1 1 1 28 0 1
10 Infilt Planter -024 2 1 1 1 28 0 1
11 Gravel Trench Be-056 2 1 1 1 28 0 1
END GEN-INFO
*** Section RCHRES***
ACTIVITY
<PLS > ************* Active Sections ***************************** # - # HYFG ADFG CNFG HTFG SDFG GQFG OXFG NUFG PKFG PHFG *** 1 1 0 0 0 0 0 0 0 0 0
2 1 0 0 0 0 0 0 0 0 0
3 1 0 0 0 0 0 0 0 0 0
4 1 0 0 0 0 0 0 0 0 0
5 1 0 0 0 0 0 0 0 0 0
6 1 0 0 0 0 0 0 0 0 0
7 1 0 0 0 0 0 0 0 0 0
8 1 0 0 0 0 0 0 0 0 0
9 1 0 0 0 0 0 0 0 0 0
10 1 0 0 0 0 0 0 0 0 0
11 1 0 0 0 0 0 0 0 0 0
END ACTIVITY
PRINT-INFO
<PLS > ***************** Print-flags ******************* PIVL PYR # - # HYDR ADCA CONS HEAT SED GQL OXRX NUTR PLNK PHCB PIVL PYR ********* 1 4 0 0 0 0 0 0 0 0 0 1 9
2 4 0 0 0 0 0 0 0 0 0 1 9
3 4 0 0 0 0 0 0 0 0 0 1 9
4 4 0 0 0 0 0 0 0 0 0 1 9
5 4 0 0 0 0 0 0 0 0 0 1 9
6 4 0 0 0 0 0 0 0 0 0 1 9
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 85 7 4 0 0 0 0 0 0 0 0 0 1 9
8 4 0 0 0 0 0 0 0 0 0 1 9
9 4 0 0 0 0 0 0 0 0 0 1 9
10 4 0 0 0 0 0 0 0 0 0 1 9
11 4 0 0 0 0 0 0 0 0 0 1 9
END PRINT-INFO
HYDR-PARM1
RCHRES Flags for each HYDR Section ***
# - # VC A1 A2 A3 ODFVFG for each *** ODGTFG for each FUNCT for each FG FG FG FG possible exit *** possible exit possible exit * * * * * * * * * * * * * * ***
1 0 1 0 0 4 5 6 0 0 0 0 0 0 0 2 2 2 2 2
2 0 1 0 0 4 5 0 0 0 0 0 0 0 0 2 2 2 2 2
3 0 1 0 0 4 5 6 0 0 0 0 0 0 0 2 2 2 2 2
4 0 1 0 0 4 5 0 0 0 0 0 0 0 0 2 2 2 2 2
5 0 1 0 0 4 5 6 0 0 0 0 0 0 0 2 2 2 2 2
6 0 1 0 0 4 5 0 0 0 0 0 0 0 0 2 2 2 2 2
7 0 1 0 0 4 5 6 0 0 0 0 0 0 0 2 2 2 2 2
8 0 1 0 0 4 5 0 0 0 0 0 0 0 0 2 2 2 2 2
9 0 1 0 0 4 5 6 0 0 0 0 0 0 0 2 2 2 2 2
10 0 1 0 0 4 5 0 0 0 0 0 0 0 0 2 2 2 2 2
11 0 1 0 0 4 5 0 0 0 0 0 0 0 0 2 2 2 2 2
END HYDR-PARM1
HYDR-PARM2
# - # FTABNO LEN DELTH STCOR KS DB50 ***
<------><--------><--------><--------><--------><--------><--------> *** 1 1 0.01 0.0 0.0 0.5 0.0
2 2 0.03 0.0 0.0 0.5 0.0
3 3 0.01 0.0 0.0 0.5 0.0
4 4 0.13 0.0 0.0 0.5 0.0
5 5 0.01 0.0 0.0 0.5 0.0
6 6 0.05 0.0 0.0 0.5 0.0
7 7 0.01 0.0 0.0 0.5 0.0
8 8 0.11 0.0 0.0 0.5 0.0
9 9 0.01 0.0 0.0 0.5 0.0
10 10 0.13 0.0 0.0 0.5 0.0
11 11 0.05 0.0 0.0 0.5 0.0
END HYDR-PARM2
HYDR-INIT
RCHRES Initial conditions for each HYDR section ***
# - # *** VOL Initial value of COLIND Initial value of OUTDGT *** ac-ft for each possible exit for each possible exit <------><--------> <---><---><---><---><---> *** <---><---><---><---><---> 1 0 4.0 5.0 6.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
2 0 4.0 5.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
3 0 4.0 5.0 6.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
4 0 4.0 5.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
5 0 4.0 5.0 6.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
6 0 4.0 5.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
7 0 4.0 5.0 6.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
8 0 4.0 5.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
9 0 4.0 5.0 6.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
10 0 4.0 5.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
11 0 4.0 5.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
END HYDR-INIT
END RCHRES
SPEC-ACTIONS
END SPEC-ACTIONS
FTABLES
FTABLE 2
45 5
Depth Area Volume Outflow1 Outflow2 Velocity Travel Time*** (ft) (acres) (acre-ft) (cfs) (cfs) (ft/sec) (Minutes)***
0.000000 0.392516 0.000000 0.000000 0.000000
0.115385 0.392516 0.018116 0.000000 0.000000
0.230769 0.392516 0.036232 0.002757 0.000000
0.346154 0.392516 0.054348 0.004000 0.000000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 86
0.461538 0.392516 0.072465 0.004928 0.000000
0.576923 0.392516 0.090581 0.005701 0.000000
0.692308 0.392516 0.108697 0.006378 0.000000
0.807692 0.392516 0.126813 0.006989 0.000000
0.923077 0.392516 0.144929 0.007548 0.000000
1.038462 0.392516 0.163724 0.008068 0.000000
1.153846 0.392516 0.182520 0.008556 0.000000
1.269231 0.392516 0.201315 0.009017 0.000000
1.384615 0.392516 0.220111 0.009456 0.000000
1.500000 0.392516 0.238906 0.009874 0.000000
1.615385 0.392516 0.257702 0.010275 0.000000
1.730769 0.392516 0.276497 0.010661 0.000000
1.846154 0.392516 0.295293 0.011034 0.000000
1.961538 0.392516 0.314088 0.011628 0.000000
2.076923 0.392516 0.332884 0.012302 0.000000
2.192308 0.392516 0.351679 0.012941 0.000000
2.307692 0.392516 0.370475 0.013550 0.000000
2.423077 0.392516 0.389270 0.014132 0.000000
2.538462 0.392516 0.408066 0.014691 0.000000
2.653846 0.392516 0.426861 0.015230 0.000000
2.769231 0.392516 0.445657 0.015750 0.000000
2.884615 0.392516 0.464452 0.016253 0.000000
3.000000 0.392516 0.483248 0.016741 0.000000
3.115385 0.392516 0.502043 0.017216 0.000000
3.230769 0.392516 0.520839 0.017677 0.000000
3.346154 0.392516 0.539634 0.018127 0.000000
3.461538 0.392516 0.558430 0.018566 0.000000
3.576923 0.392516 0.577225 0.018995 0.000000
3.692308 0.392516 0.596021 0.019414 0.000000
3.807692 0.392516 0.614816 0.019825 0.000000
3.923077 0.392516 0.633612 0.020227 0.000000
4.038462 0.392516 0.652407 0.020622 0.000000
4.153846 0.392516 0.671202 0.021009 0.000000
4.269231 0.392516 0.689998 0.021390 0.000000
4.384615 0.392516 0.708793 0.021764 0.000000
4.500000 0.392516 0.727589 0.022132 0.000000
4.615385 0.392516 0.746384 0.022495 0.000000
4.730769 0.392516 0.765180 0.022853 0.000000
4.846154 0.392516 0.783975 0.023209 0.000000
4.961538 0.392516 0.802771 0.023636 0.000000
5.000000 0.392516 1.618072 0.023693 0.000000
END FTABLE 2
FTABLE 1
49 6
Depth Area Volume Outflow1 Outflow2 outflow 3 Velocity Travel Time***
(ft) (acres) (acre-ft) (cfs) (cfs) (cfs) (ft/sec)
(Minutes)***
0.000000 0.392516 0.000000 0.000000 0.023693 0.000000
0.115385 0.392516 0.045290 0.000000 0.023636 0.000000
0.230769 0.392516 0.090581 0.000000 0.023636 0.000000
0.346154 0.392516 0.135871 0.000000 0.023636 0.000000
0.461538 0.392516 0.181161 0.000000 0.023636 0.000000
0.576923 0.392516 0.226452 0.000000 0.023636 0.000000
0.692308 0.392516 0.271742 0.000000 0.023636 0.000000
0.807692 0.392516 0.317032 0.000000 0.023636 0.000000
0.923077 0.392516 0.362323 0.000000 0.023636 0.000000
1.038462 0.392516 0.407613 0.000000 0.023636 0.000000
1.153846 0.392516 0.452903 0.000000 0.023636 0.000000
1.269231 0.392516 0.498193 0.000000 0.023636 0.000000
1.384615 0.392516 0.543484 0.000000 0.023636 0.000000
1.500000 0.392516 0.588774 0.000000 0.023636 0.000000
1.615385 0.392516 0.634064 0.000000 0.023636 0.000000
1.730769 0.392516 0.679355 0.000000 0.023636 0.000000
1.846154 0.392516 0.724645 0.000000 0.023636 0.000000
1.961538 0.392516 0.769935 0.000000 0.023636 0.000000
2.076923 0.392516 0.815226 0.000000 0.023636 0.000000
2.192308 0.392516 0.860516 0.000000 0.023636 0.000000
2.307692 0.392516 0.905806 0.000000 0.023636 0.000000
2.423077 0.392516 0.951097 0.000000 0.023636 0.000000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 87
2.538462 0.392516 0.996387 0.048974 0.023636 0.000000
2.653846 0.392516 1.041677 0.391790 0.023636 0.000000
2.769231 0.392516 1.086968 0.907006 0.023636 0.000000
2.884615 0.392516 1.132258 1.548685 0.023636 0.000000
3.000000 0.392516 1.177548 2.295504 0.023636 0.000000
3.115385 0.392516 1.222839 3.134318 0.023636 0.000000
3.230769 0.392516 1.268129 4.055958 0.023636 0.000000
3.346154 0.392516 1.313419 5.053556 0.023636 0.000000
3.461538 0.392516 1.358709 6.121715 0.023636 0.000000
3.576923 0.392516 1.404000 7.256048 0.023636 0.000000
3.692308 0.392516 1.449290 8.452898 0.023636 0.000000
3.807692 0.392516 1.494580 9.709156 0.023636 0.000000
3.923077 0.392516 1.539871 11.02213 0.023636 0.000000
4.038462 0.392516 1.585161 12.38948 0.023636 0.000000
4.153846 0.392516 1.630451 13.80911 0.023636 0.000000
4.269231 0.392516 1.675742 15.27917 0.023636 0.000000
4.384615 0.392516 1.721032 16.79799 0.023636 0.000000
4.500000 0.392516 1.766322 18.36403 0.023636 0.000000
4.615385 0.392516 1.811613 19.97594 0.023636 0.000000
4.730769 0.392516 1.856903 21.63242 0.023636 0.000000
4.846154 0.392516 1.902193 23.33232 0.023636 0.000000
4.961538 0.392516 1.947484 25.07454 0.023636 0.000000
5.076923 0.392516 1.992774 26.85810 0.023636 0.000000
5.192308 0.392516 2.038064 28.68205 0.023636 0.000000
5.307692 0.392516 2.083355 30.54551 0.023636 0.000000
5.423077 0.392516 2.128645 32.44767 0.023636 0.000000
5.500000 0.392516 2.158838 34.38775 0.023636 0.000000
END FTABLE 1
FTABLE 4
62 5
Depth Area Volume Outflow1 Outflow2 Velocity Travel Time*** (ft) (acres) (acre-ft) (cfs) (cfs) (ft/sec) (Minutes)***
0.000000 0.460055 0.000000 0.000000 0.000000
0.082418 0.460055 0.015167 0.000000 0.000000
0.164835 0.460055 0.030333 0.001641 0.000000
0.247253 0.460055 0.045500 0.002969 0.000000
0.329670 0.460055 0.060667 0.003849 0.000000
0.412088 0.460055 0.075833 0.004555 0.000000
0.494505 0.460055 0.091000 0.005161 0.000000
0.576923 0.460055 0.106167 0.005701 0.000000
0.659341 0.460055 0.121333 0.006193 0.000000
0.741758 0.460055 0.136500 0.006647 0.000000
0.824176 0.460055 0.151667 0.007071 0.000000
0.906593 0.460055 0.166833 0.007471 0.000000
0.989011 0.460055 0.182000 0.007850 0.000000
1.071429 0.460055 0.197735 0.008211 0.000000
1.153846 0.460055 0.213471 0.008556 0.000000
1.236264 0.460055 0.229206 0.008888 0.000000
1.318681 0.460055 0.244941 0.009208 0.000000
1.401099 0.460055 0.260677 0.009517 0.000000
1.483516 0.460055 0.276412 0.009816 0.000000
1.565934 0.460055 0.292148 0.010105 0.000000
1.648352 0.460055 0.307883 0.010387 0.000000
1.730769 0.460055 0.323618 0.010661 0.000000
1.813187 0.460055 0.339354 0.010929 0.000000
1.895604 0.460055 0.355089 0.011190 0.000000
1.978022 0.460055 0.370825 0.011628 0.000000
2.060440 0.460055 0.386560 0.012113 0.000000
2.142857 0.460055 0.402295 0.012580 0.000000
2.225275 0.460055 0.418031 0.013030 0.000000
2.307692 0.460055 0.433766 0.013464 0.000000
2.390110 0.460055 0.449502 0.013885 0.000000
2.472527 0.460055 0.465237 0.014294 0.000000
2.554945 0.460055 0.480972 0.014691 0.000000
2.637363 0.460055 0.496708 0.015078 0.000000
2.719780 0.460055 0.512443 0.015455 0.000000
2.802198 0.460055 0.528179 0.015823 0.000000
2.884615 0.460055 0.543914 0.016182 0.000000
2.967033 0.460055 0.559649 0.016534 0.000000
3.049451 0.460055 0.575385 0.016878 0.000000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 88
3.131868 0.460055 0.591120 0.017216 0.000000
3.214286 0.460055 0.606856 0.017547 0.000000
3.296703 0.460055 0.622591 0.017871 0.000000
3.379121 0.460055 0.638326 0.018190 0.000000
3.461538 0.460055 0.654062 0.018504 0.000000
3.543956 0.460055 0.669797 0.018812 0.000000
3.626374 0.460055 0.685533 0.019116 0.000000
3.708791 0.460055 0.701268 0.019414 0.000000
3.791209 0.460055 0.717003 0.019709 0.000000
3.873626 0.460055 0.732739 0.019998 0.000000
3.956044 0.460055 0.748474 0.020284 0.000000
4.038462 0.460055 0.764210 0.020566 0.000000
4.120879 0.460055 0.779945 0.020844 0.000000
4.203297 0.460055 0.795680 0.021119 0.000000
4.285714 0.460055 0.811416 0.021390 0.000000
4.368132 0.460055 0.827151 0.021658 0.000000
4.450549 0.460055 0.842887 0.021923 0.000000
4.532967 0.460055 0.858622 0.022185 0.000000
4.615385 0.460055 0.874357 0.022444 0.000000
4.697802 0.460055 0.890093 0.022700 0.000000
4.780220 0.460055 0.905828 0.022955 0.000000
4.862637 0.460055 0.921564 0.023209 0.000000
4.945055 0.460055 0.937299 0.023470 0.000000
5.000000 0.460055 1.895579 0.023661 0.000000
END FTABLE 4
FTABLE 3
32 6
Depth Area Volume Outflow1 Outflow2 outflow 3 Velocity Travel Time***
(ft) (acres) (acre-ft) (cfs) (cfs) (cfs) (ft/sec)
(Minutes)***
0.000000 0.460055 0.000000 0.000000 0.023661 0.000000
0.082418 0.460055 0.037917 0.000000 0.023470 0.000000
0.164835 0.460055 0.075833 0.000000 0.023470 0.000000
0.247253 0.460055 0.113750 0.000000 0.023470 0.000000
0.329670 0.460055 0.151667 0.000000 0.023470 0.000000
0.412088 0.460055 0.189583 0.000000 0.023470 0.000000
0.494505 0.460055 0.227500 0.000000 0.023470 0.000000
0.576923 0.460055 0.265416 0.000000 0.023470 0.000000
0.659341 0.460055 0.303333 0.000000 0.023470 0.000000
0.741758 0.460055 0.341250 0.000000 0.023470 0.000000
0.824176 0.460055 0.379166 0.000000 0.023470 0.000000
0.906593 0.460055 0.417083 0.000000 0.023470 0.000000
0.989011 0.460055 0.455000 0.000000 0.023470 0.000000
1.071429 0.460055 0.492916 0.123946 0.023470 0.000000
1.153846 0.460055 0.530833 0.391790 0.023470 0.000000
1.236264 0.460055 0.568749 0.745622 0.023470 0.000000
1.318681 0.460055 0.606666 1.168041 0.023470 0.000000
1.401099 0.460055 0.644583 1.649302 0.023470 0.000000
1.483516 0.460055 0.682499 2.182931 0.023470 0.000000
1.565934 0.460055 0.720416 2.764215 0.023470 0.000000
1.648352 0.460055 0.758333 3.389527 0.023470 0.000000
1.730769 0.460055 0.796249 4.055958 0.023470 0.000000
1.813187 0.460055 0.834166 4.761114 0.023470 0.000000
1.895604 0.460055 0.872082 5.502974 0.023470 0.000000
1.978022 0.460055 0.909999 6.279803 0.023470 0.000000
2.060440 0.460055 0.947916 7.090094 0.023470 0.000000
2.142857 0.460055 0.985832 7.932517 0.023470 0.000000
2.225275 0.460055 1.023749 8.805891 0.023470 0.000000
2.307692 0.460055 1.061666 9.709156 0.023470 0.000000
2.390110 0.460055 1.099582 10.64135 0.023470 0.000000
2.472527 0.460055 1.137499 11.60161 0.023470 0.000000
2.500000 0.460055 1.150138 12.58913 0.023470 0.000000
END FTABLE 3
FTABLE 6
62 5
Depth Area Volume Outflow1 Outflow2 Velocity Travel Time*** (ft) (acres) (acre-ft) (cfs) (cfs) (ft/sec) (Minutes)***
0.000000 0.344353 0.000000 0.000000 0.000000
0.082418 0.344353 0.011352 0.000000 0.000000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 89
0.164835 0.344353 0.022705 0.001641 0.000000
0.247253 0.344353 0.034057 0.002969 0.000000
0.329670 0.344353 0.045409 0.003849 0.000000
0.412088 0.344353 0.056761 0.004555 0.000000
0.494505 0.344353 0.068114 0.005161 0.000000
0.576923 0.344353 0.079466 0.005701 0.000000
0.659341 0.344353 0.090818 0.006193 0.000000
0.741758 0.344353 0.102171 0.006647 0.000000
0.824176 0.344353 0.113523 0.007071 0.000000
0.906593 0.344353 0.124875 0.007471 0.000000
0.989011 0.344353 0.136227 0.007850 0.000000
1.071429 0.344353 0.148005 0.008211 0.000000
1.153846 0.344353 0.159783 0.008556 0.000000
1.236264 0.344353 0.171561 0.008888 0.000000
1.318681 0.344353 0.183339 0.009208 0.000000
1.401099 0.344353 0.195117 0.009517 0.000000
1.483516 0.344353 0.206895 0.009816 0.000000
1.565934 0.344353 0.218673 0.010105 0.000000
1.648352 0.344353 0.230451 0.010387 0.000000
1.730769 0.344353 0.242229 0.010661 0.000000
1.813187 0.344353 0.254007 0.010929 0.000000
1.895604 0.344353 0.265785 0.011190 0.000000
1.978022 0.344353 0.277563 0.011628 0.000000
2.060440 0.344353 0.289341 0.012113 0.000000
2.142857 0.344353 0.301119 0.012580 0.000000
2.225275 0.344353 0.312897 0.013030 0.000000
2.307692 0.344353 0.324675 0.013464 0.000000
2.390110 0.344353 0.336453 0.013885 0.000000
2.472527 0.344353 0.348231 0.014294 0.000000
2.554945 0.344353 0.360009 0.014691 0.000000
2.637363 0.344353 0.371787 0.015078 0.000000
2.719780 0.344353 0.383565 0.015455 0.000000
2.802198 0.344353 0.395343 0.015823 0.000000
2.884615 0.344353 0.407121 0.016182 0.000000
2.967033 0.344353 0.418899 0.016534 0.000000
3.049451 0.344353 0.430677 0.016878 0.000000
3.131868 0.344353 0.442455 0.017216 0.000000
3.214286 0.344353 0.454233 0.017547 0.000000
3.296703 0.344353 0.466011 0.017871 0.000000
3.379121 0.344353 0.477789 0.018190 0.000000
3.461538 0.344353 0.489567 0.018504 0.000000
3.543956 0.344353 0.501345 0.018812 0.000000
3.626374 0.344353 0.513123 0.019116 0.000000
3.708791 0.344353 0.524901 0.019414 0.000000
3.791209 0.344353 0.536679 0.019709 0.000000
3.873626 0.344353 0.548457 0.019998 0.000000
3.956044 0.344353 0.560235 0.020284 0.000000
4.038462 0.344353 0.572013 0.020566 0.000000
4.120879 0.344353 0.583791 0.020844 0.000000
4.203297 0.344353 0.595569 0.021119 0.000000
4.285714 0.344353 0.607347 0.021390 0.000000
4.368132 0.344353 0.619125 0.021658 0.000000
4.450549 0.344353 0.630903 0.021923 0.000000
4.532967 0.344353 0.642681 0.022185 0.000000
4.615385 0.344353 0.654459 0.022444 0.000000
4.697802 0.344353 0.666237 0.022700 0.000000
4.780220 0.344353 0.678015 0.022955 0.000000
4.862637 0.344353 0.689793 0.023209 0.000000
4.945055 0.344353 0.701571 0.023470 0.000000
5.000000 0.344353 1.418846 0.023661 0.000000
END FTABLE 6
FTABLE 5
32 6
Depth Area Volume Outflow1 Outflow2 outflow 3 Velocity Travel Time***
(ft) (acres) (acre-ft) (cfs) (cfs) (cfs) (ft/sec)
(Minutes)***
0.000000 0.344353 0.000000 0.000000 0.023661 0.000000
0.082418 0.344353 0.028381 0.000000 0.023470 0.000000
0.164835 0.344353 0.056761 0.000000 0.023470 0.000000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 90
0.247253 0.344353 0.085142 0.000000 0.023470 0.000000
0.329670 0.344353 0.113523 0.000000 0.023470 0.000000
0.412088 0.344353 0.141904 0.000000 0.023470 0.000000
0.494505 0.344353 0.170284 0.000000 0.023470 0.000000
0.576923 0.344353 0.198665 0.000000 0.023470 0.000000
0.659341 0.344353 0.227046 0.000000 0.023470 0.000000
0.741758 0.344353 0.255426 0.000000 0.023470 0.000000
0.824176 0.344353 0.283807 0.000000 0.023470 0.000000
0.906593 0.344353 0.312188 0.000000 0.023470 0.000000
0.989011 0.344353 0.340569 0.000000 0.023470 0.000000
1.071429 0.344353 0.368949 0.123946 0.023470 0.000000
1.153846 0.344353 0.397330 0.391790 0.023470 0.000000
1.236264 0.344353 0.425711 0.745622 0.023470 0.000000
1.318681 0.344353 0.454091 1.168041 0.023470 0.000000
1.401099 0.344353 0.482472 1.649302 0.023470 0.000000
1.483516 0.344353 0.510853 2.182931 0.023470 0.000000
1.565934 0.344353 0.539233 2.764215 0.023470 0.000000
1.648352 0.344353 0.567614 3.389527 0.023470 0.000000
1.730769 0.344353 0.595995 4.055958 0.023470 0.000000
1.813187 0.344353 0.624376 4.761114 0.023470 0.000000
1.895604 0.344353 0.652756 5.502974 0.023470 0.000000
1.978022 0.344353 0.681137 6.279803 0.023470 0.000000
2.060440 0.344353 0.709518 7.090094 0.023470 0.000000
2.142857 0.344353 0.737898 7.932517 0.023470 0.000000
2.225275 0.344353 0.766279 8.805891 0.023470 0.000000
2.307692 0.344353 0.794660 9.709156 0.023470 0.000000
2.390110 0.344353 0.823041 10.64135 0.023470 0.000000
2.472527 0.344353 0.851421 11.60161 0.023470 0.000000
2.500000 0.344353 0.860882 12.58913 0.023470 0.000000
END FTABLE 5
FTABLE 8
55 5
Depth Area Volume Outflow1 Outflow2 Velocity Travel Time*** (ft) (acres) (acre-ft) (cfs) (cfs) (ft/sec) (Minutes)***
0.000000 0.413223 0.000000 0.000000 0.000000
0.093407 0.413223 0.015439 0.000000 0.000000
0.186813 0.413223 0.030878 0.002084 0.000000
0.280220 0.413223 0.046317 0.003350 0.000000
0.373626 0.413223 0.061756 0.004240 0.000000
0.467033 0.413223 0.077196 0.004968 0.000000
0.560440 0.413223 0.092635 0.005598 0.000000
0.653846 0.413223 0.108074 0.006161 0.000000
0.747253 0.413223 0.123513 0.006676 0.000000
0.840659 0.413223 0.138952 0.007153 0.000000
0.934066 0.413223 0.154391 0.007599 0.000000
1.027473 0.413223 0.170409 0.008020 0.000000
1.120879 0.413223 0.186427 0.008420 0.000000
1.214286 0.413223 0.202445 0.008801 0.000000
1.307692 0.413223 0.218463 0.009166 0.000000
1.401099 0.413223 0.234481 0.009517 0.000000
1.494505 0.413223 0.250500 0.009855 0.000000
1.587912 0.413223 0.266518 0.010181 0.000000
1.681319 0.413223 0.282536 0.010498 0.000000
1.774725 0.413223 0.298554 0.010805 0.000000
1.868132 0.413223 0.314572 0.011103 0.000000
1.961538 0.413223 0.330590 0.011561 0.000000
2.054945 0.413223 0.346608 0.012113 0.000000
2.148352 0.413223 0.362626 0.012641 0.000000
2.241758 0.413223 0.378644 0.013147 0.000000
2.335165 0.413223 0.394662 0.013634 0.000000
2.428571 0.413223 0.410680 0.014105 0.000000
2.521978 0.413223 0.426698 0.014560 0.000000
2.615385 0.413223 0.442716 0.015001 0.000000
2.708791 0.413223 0.458734 0.015430 0.000000
2.802198 0.413223 0.474753 0.015847 0.000000
2.895604 0.413223 0.490771 0.016253 0.000000
2.989011 0.413223 0.506789 0.016649 0.000000
3.082418 0.413223 0.522807 0.017036 0.000000
3.175824 0.413223 0.538825 0.017415 0.000000
3.269231 0.413223 0.554843 0.017785 0.000000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 91
3.362637 0.413223 0.570861 0.018148 0.000000
3.456044 0.413223 0.586879 0.018504 0.000000
3.549451 0.413223 0.602897 0.018853 0.000000
3.642857 0.413223 0.618915 0.019196 0.000000
3.736264 0.413223 0.634933 0.019533 0.000000
3.829670 0.413223 0.650951 0.019864 0.000000
3.923077 0.413223 0.666969 0.020189 0.000000
4.016484 0.413223 0.682987 0.020510 0.000000
4.109890 0.413223 0.699006 0.020826 0.000000
4.203297 0.413223 0.715024 0.021137 0.000000
4.296703 0.413223 0.731042 0.021444 0.000000
4.390110 0.413223 0.747060 0.021746 0.000000
4.483516 0.413223 0.763078 0.022045 0.000000
4.576923 0.413223 0.779096 0.022340 0.000000
4.670330 0.413223 0.795114 0.022632 0.000000
4.763736 0.413223 0.811132 0.022921 0.000000
4.857143 0.413223 0.827150 0.023209 0.000000
4.950549 0.413223 0.843168 0.023513 0.000000
5.000000 0.413223 1.703297 0.023652 0.000000
END FTABLE 8
FTABLE 7
39 6
Depth Area Volume Outflow1 Outflow2 outflow 3 Velocity Travel Time***
(ft) (acres) (acre-ft) (cfs) (cfs) (cfs) (ft/sec)
(Minutes)***
0.000000 0.413223 0.000000 0.000000 0.023652 0.000000
0.093407 0.413223 0.038598 0.000000 0.023513 0.000000
0.186813 0.413223 0.077196 0.000000 0.023513 0.000000
0.280220 0.413223 0.115793 0.000000 0.023513 0.000000
0.373626 0.413223 0.154391 0.000000 0.023513 0.000000
0.467033 0.413223 0.192989 0.000000 0.023513 0.000000
0.560440 0.413223 0.231587 0.000000 0.023513 0.000000
0.653846 0.413223 0.270184 0.000000 0.023513 0.000000
0.747253 0.413223 0.308782 0.000000 0.023513 0.000000
0.840659 0.413223 0.347380 0.000000 0.023513 0.000000
0.934066 0.413223 0.385978 0.000000 0.023513 0.000000
1.027473 0.413223 0.424575 0.000000 0.023513 0.000000
1.120879 0.413223 0.463173 0.000000 0.023513 0.000000
1.214286 0.413223 0.501771 0.000000 0.023513 0.000000
1.307692 0.413223 0.540369 0.000000 0.023513 0.000000
1.401099 0.413223 0.578966 0.000000 0.023513 0.000000
1.494505 0.413223 0.617564 0.000000 0.023513 0.000000
1.587912 0.413223 0.656162 0.169237 0.023513 0.000000
1.681319 0.413223 0.694760 0.501288 0.023513 0.000000
1.774725 0.413223 0.733358 0.934913 0.023513 0.000000
1.868132 0.413223 0.771955 1.450201 0.023513 0.000000
1.961538 0.413223 0.810553 2.035799 0.023513 0.000000
2.054945 0.413223 0.849151 2.684096 0.023513 0.000000
2.148352 0.413223 0.887749 3.389527 0.023513 0.000000
2.241758 0.413223 0.926346 4.147789 0.023513 0.000000
2.335165 0.413223 0.964944 4.955431 0.023513 0.000000
2.428571 0.413223 1.003542 5.809598 0.023513 0.000000
2.521978 0.413223 1.042140 6.707882 0.023513 0.000000
2.615385 0.413223 1.080737 7.648215 0.023513 0.000000
2.708791 0.413223 1.119335 8.628793 0.023513 0.000000
2.802198 0.413223 1.157933 9.648028 0.023513 0.000000
2.895604 0.413223 1.196531 10.70451 0.023513 0.000000
2.989011 0.413223 1.235129 11.79696 0.023513 0.000000
3.082418 0.413223 1.273726 12.92423 0.023513 0.000000
3.175824 0.413223 1.312324 14.08529 0.023513 0.000000
3.269231 0.413223 1.350922 15.27917 0.023513 0.000000
3.362637 0.413223 1.389520 16.50500 0.023513 0.000000
3.456044 0.413223 1.428117 17.76197 0.023513 0.000000
3.500000 0.413223 1.446281 19.04931 0.023513 0.000000
END FTABLE 7
FTABLE 10
62 5
Depth Area Volume Outflow1 Outflow2 Velocity Travel Time*** (ft) (acres) (acre-ft) (cfs) (cfs) (ft/sec) (Minutes)*** DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 92
0.000000 0.160698 0.000000 0.000000 0.000000
0.082418 0.160698 0.005298 0.000000 0.000000
0.164835 0.160698 0.010595 0.001641 0.000000
0.247253 0.160698 0.015893 0.002969 0.000000
0.329670 0.160698 0.021191 0.003849 0.000000
0.412088 0.160698 0.026489 0.004555 0.000000
0.494505 0.160698 0.031786 0.005161 0.000000
0.576923 0.160698 0.037084 0.005701 0.000000
0.659341 0.160698 0.042382 0.006193 0.000000
0.741758 0.160698 0.047680 0.006647 0.000000
0.824176 0.160698 0.052977 0.007071 0.000000
0.906593 0.160698 0.058275 0.007471 0.000000
0.989011 0.160698 0.063573 0.007850 0.000000
1.071429 0.160698 0.069069 0.008211 0.000000
1.153846 0.160698 0.074566 0.008556 0.000000
1.236264 0.160698 0.080062 0.008888 0.000000
1.318681 0.160698 0.085558 0.009208 0.000000
1.401099 0.160698 0.091055 0.009517 0.000000
1.483516 0.160698 0.096551 0.009816 0.000000
1.565934 0.160698 0.102048 0.010105 0.000000
1.648352 0.160698 0.107544 0.010387 0.000000
1.730769 0.160698 0.113040 0.010661 0.000000
1.813187 0.160698 0.118537 0.010929 0.000000
1.895604 0.160698 0.124033 0.011190 0.000000
1.978022 0.160698 0.129530 0.011628 0.000000
2.060440 0.160698 0.135026 0.012113 0.000000
2.142857 0.160698 0.140522 0.012580 0.000000
2.225275 0.160698 0.146019 0.013030 0.000000
2.307692 0.160698 0.151515 0.013464 0.000000
2.390110 0.160698 0.157012 0.013885 0.000000
2.472527 0.160698 0.162508 0.014294 0.000000
2.554945 0.160698 0.168004 0.014691 0.000000
2.637363 0.160698 0.173501 0.015078 0.000000
2.719780 0.160698 0.178997 0.015455 0.000000
2.802198 0.160698 0.184494 0.015823 0.000000
2.884615 0.160698 0.189990 0.016182 0.000000
2.967033 0.160698 0.195486 0.016534 0.000000
3.049451 0.160698 0.200983 0.016878 0.000000
3.131868 0.160698 0.206479 0.017216 0.000000
3.214286 0.160698 0.211976 0.017547 0.000000
3.296703 0.160698 0.217472 0.017871 0.000000
3.379121 0.160698 0.222968 0.018190 0.000000
3.461538 0.160698 0.228465 0.018504 0.000000
3.543956 0.160698 0.233961 0.018812 0.000000
3.626374 0.160698 0.239458 0.019116 0.000000
3.708791 0.160698 0.244954 0.019414 0.000000
3.791209 0.160698 0.250450 0.019709 0.000000
3.873626 0.160698 0.255947 0.019998 0.000000
3.956044 0.160698 0.261443 0.020284 0.000000
4.038462 0.160698 0.266939 0.020566 0.000000
4.120879 0.160698 0.272436 0.020844 0.000000
4.203297 0.160698 0.277932 0.021119 0.000000
4.285714 0.160698 0.283429 0.021390 0.000000
4.368132 0.160698 0.288925 0.021658 0.000000
4.450549 0.160698 0.294421 0.021923 0.000000
4.532967 0.160698 0.299918 0.022185 0.000000
4.615385 0.160698 0.305414 0.022444 0.000000
4.697802 0.160698 0.310911 0.022700 0.000000
4.780220 0.160698 0.316407 0.022955 0.000000
4.862637 0.160698 0.321903 0.023209 0.000000
4.945055 0.160698 0.327400 0.023470 0.000000
5.000000 0.160698 0.662128 0.023661 0.000000
END FTABLE 10
FTABLE 9
32 6
Depth Area Volume Outflow1 Outflow2 outflow 3 Velocity Travel Time***
(ft) (acres) (acre-ft) (cfs) (cfs) (cfs) (ft/sec)
(Minutes)***
0.000000 0.160698 0.000000 0.000000 0.023661 0.000000
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 93
0.082418 0.160698 0.013244 0.000000 0.023470 0.000000
0.164835 0.160698 0.026489 0.000000 0.023470 0.000000
0.247253 0.160698 0.039733 0.000000 0.023470 0.000000
0.329670 0.160698 0.052977 0.000000 0.023470 0.000000
0.412088 0.160698 0.066222 0.000000 0.023470 0.000000
0.494505 0.160698 0.079466 0.000000 0.023470 0.000000
0.576923 0.160698 0.092710 0.000000 0.023470 0.000000
0.659341 0.160698 0.105955 0.000000 0.023470 0.000000
0.741758 0.160698 0.119199 0.000000 0.023470 0.000000
0.824176 0.160698 0.132443 0.000000 0.023470 0.000000
0.906593 0.160698 0.145688 0.000000 0.023470 0.000000
0.989011 0.160698 0.158932 0.000000 0.023470 0.000000
1.071429 0.160698 0.172176 0.123946 0.023470 0.000000
1.153846 0.160698 0.185421 0.391790 0.023470 0.000000
1.236264 0.160698 0.198665 0.745622 0.023470 0.000000
1.318681 0.160698 0.211909 1.168041 0.023470 0.000000
1.401099 0.160698 0.225154 1.649302 0.023470 0.000000
1.483516 0.160698 0.238398 2.182931 0.023470 0.000000
1.565934 0.160698 0.251642 2.764215 0.023470 0.000000
1.648352 0.160698 0.264887 3.389527 0.023470 0.000000
1.730769 0.160698 0.278131 4.055958 0.023470 0.000000
1.813187 0.160698 0.291375 4.761114 0.023470 0.000000
1.895604 0.160698 0.304620 5.502974 0.023470 0.000000
1.978022 0.160698 0.317864 6.279803 0.023470 0.000000
2.060440 0.160698 0.331108 7.090094 0.023470 0.000000
2.142857 0.160698 0.344353 7.932517 0.023470 0.000000
2.225275 0.160698 0.357597 8.805891 0.023470 0.000000
2.307692 0.160698 0.370841 9.709156 0.023470 0.000000
2.390110 0.160698 0.384086 10.64135 0.023470 0.000000
2.472527 0.160698 0.397330 11.60161 0.023470 0.000000
2.500000 0.160698 0.401745 12.58913 0.023470 0.000000
END FTABLE 9
FTABLE 11
92 5
Depth Area Volume Outflow1 Outflow2 Velocity Travel Time*** (ft) (acres) (acre-ft) (cfs) (cfs) (ft/sec) (Minutes)***
0.000000 0.292700 0.000000 0.000000 0.000000
0.088889 0.295824 0.003923 0.000000 1.491446
0.177778 0.298948 0.007889 0.000000 1.507197
0.266667 0.302072 0.011895 0.000000 1.522949
0.355556 0.305197 0.015944 0.000000 1.538700
0.444444 0.308321 0.020034 0.000000 1.554452
0.533333 0.311446 0.024166 0.000000 1.570205
0.622222 0.314570 0.028339 0.000000 1.585957
0.711111 0.317694 0.032554 0.000000 1.601710
0.800000 0.320819 0.036811 0.000000 1.617463
0.888889 0.323944 0.041110 0.000000 1.633216
0.977778 0.327068 0.045450 0.000000 1.648969
1.066667 0.330193 0.057134 0.000000 1.664723
1.155556 0.333318 0.068930 0.000000 1.680476
1.244444 0.336442 0.080837 0.000000 1.696230
1.333333 0.339567 0.092855 0.000000 1.711985
1.422222 0.342692 0.104984 0.000000 1.727739
1.511111 0.345817 0.117224 0.000000 1.743494
1.600000 0.348942 0.129575 0.000000 1.759249
1.688889 0.352067 0.142038 0.000000 1.775004
1.777778 0.355192 0.154611 0.000000 1.790759
1.866667 0.358317 0.167296 0.000000 1.806514
1.955556 0.361442 0.180091 0.000000 1.822270
2.044444 0.364567 0.192998 0.000000 1.838026
2.133333 0.367692 0.206016 0.000000 1.853782
2.222222 0.370818 0.219145 0.000000 1.869539
2.311111 0.373943 0.232385 0.000000 1.885295
2.400000 0.377068 0.245737 0.000000 1.901052
2.488889 0.380194 0.259199 0.000000 1.916809
2.577778 0.383319 0.272773 0.000000 1.932567
2.666667 0.386444 0.286457 0.000000 1.948324
2.755556 0.389570 0.300253 0.000000 1.964082
2.844444 0.392695 0.314160 0.000000 1.979840
2.933333 0.395821 0.328178 0.000000 1.995598
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 94
3.022222 0.398947 0.342307 0.000000 2.011356
3.111111 0.402072 0.356548 0.000000 2.027115
3.200000 0.405198 0.370899 0.000000 2.042874
3.288889 0.408324 0.385362 0.000000 2.058633
3.377778 0.411450 0.399936 0.000000 2.074392
3.466667 0.414576 0.414621 0.000000 2.090151
3.555556 0.417701 0.429417 0.000000 2.105911
3.644444 0.420827 0.444324 0.000000 2.121671
3.733333 0.423953 0.459342 0.000000 2.137431
3.822222 0.427079 0.474472 0.000000 2.153192
3.911111 0.430205 0.489712 0.000000 2.168952
4.000000 0.433331 0.505064 0.000000 2.184713
4.088889 0.436458 0.520527 0.000000 2.200474
4.177778 0.439584 0.536101 0.000000 2.216235
4.266667 0.442710 0.551786 0.000000 2.231997
4.355556 0.445836 0.567583 0.000000 2.247758
4.444444 0.448963 0.583490 0.000000 2.263520
4.533333 0.452089 0.599509 0.000000 2.279282
4.622222 0.455215 0.615639 0.000000 2.295045
4.711111 0.458342 0.631880 0.000000 2.310807
4.800000 0.461468 0.648232 0.000000 2.326570
4.888889 0.464595 0.664695 0.000000 2.342333
4.977778 0.467722 0.681270 0.000000 2.358096
5.066667 0.470848 0.722984 0.000000 2.373860
5.155556 0.473975 0.764976 0.000000 2.389623
5.244444 0.477102 0.807246 0.000000 2.405387
5.333333 0.480228 0.849794 0.000000 2.421151
5.422222 0.483355 0.892620 0.000000 2.436916
5.511111 0.486482 0.935724 0.000000 2.452680
5.600000 0.489609 0.979106 0.000000 2.468445
5.688889 0.492736 1.022765 0.000000 2.484210
5.777778 0.495863 1.066703 0.000000 2.499975
5.866667 0.498990 1.110919 0.000000 2.515740
5.955556 0.502117 1.155412 0.000000 2.531506
6.044444 0.505244 1.200184 0.000000 2.547272
6.133333 0.508371 1.245234 0.000000 2.563038
6.222222 0.511498 1.290561 0.000000 2.578804
6.311111 0.514626 1.336167 0.000000 2.594571
6.400000 0.517753 1.382050 0.000000 2.610337
6.488889 0.520880 1.428212 0.000000 2.626104
6.577778 0.524008 1.474651 0.000000 2.641872
6.666667 0.527135 1.521369 0.000000 2.657639
6.755556 0.530262 1.568364 0.000000 2.673406
6.844444 0.533390 1.615637 0.000000 2.689174
6.933333 0.536517 1.663189 0.000000 2.704942
7.022222 0.539645 1.711018 0.000000 2.720711
7.111111 0.542773 1.759126 0.000000 2.736479
7.200000 0.545900 1.807511 0.000000 2.752248
7.288889 0.549028 1.856175 0.000000 2.768017
7.377778 0.552156 1.905116 0.000000 2.783786
7.466667 0.555284 1.954336 0.000000 2.799555
7.555556 0.558412 2.003833 0.000000 2.815325
7.644444 0.561539 2.053609 0.000000 2.831095
7.733333 0.564667 2.103663 0.000000 2.846865
7.822222 0.567795 2.153994 0.000000 2.862635
7.911111 0.570923 2.204604 0.000000 2.878405
8.000000 0.574051 2.255492 0.000000 2.894176
8.088889 0.577180 2.306658 4.510298 2.909947
END FTABLE 11
END FTABLES
EXT SOURCES
<-Volume-> <Member> SsysSgap<--Mult-->Tran <-Target vols> <-Grp> <-Member-> *** <Name> # <Name> # tem strg<-factor->strg <Name> # # <Name> # # *** WDM 2 PREC ENGL 1 PERLND 1 999 EXTNL PREC
WDM 2 PREC ENGL 1 IMPLND 1 999 EXTNL PREC
WDM 1 EVAP ENGL 1 PERLND 1 999 EXTNL PETINP
WDM 1 EVAP ENGL 1 IMPLND 1 999 EXTNL PETINP
WDM 22 IRRG ENGL 0.7 SAME PERLND 15 EXTNL SURLI
WDM 22 IRRG ENGL 0.7 SAME PERLND 13 EXTNL SURLI
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 95 WDM 22 IRRG ENGL 0.7 SAME PERLND 16 EXTNL SURLI
WDM 2 PREC ENGL 1 RCHRES 1 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 2 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 3 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 4 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 5 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 6 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 7 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 8 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 9 EXTNL PREC
WDM 2 PREC ENGL 1 RCHRES 10 EXTNL PREC
WDM 1 EVAP ENGL 0.5 RCHRES 1 EXTNL POTEV
WDM 1 EVAP ENGL 0.7 RCHRES 2 EXTNL POTEV
WDM 1 EVAP ENGL 0.5 RCHRES 3 EXTNL POTEV
WDM 1 EVAP ENGL 0.7 RCHRES 4 EXTNL POTEV
WDM 1 EVAP ENGL 0.5 RCHRES 5 EXTNL POTEV
WDM 1 EVAP ENGL 0.7 RCHRES 6 EXTNL POTEV
WDM 1 EVAP ENGL 0.5 RCHRES 7 EXTNL POTEV
WDM 1 EVAP ENGL 0.7 RCHRES 8 EXTNL POTEV
WDM 1 EVAP ENGL 0.5 RCHRES 9 EXTNL POTEV
WDM 1 EVAP ENGL 0.7 RCHRES 10 EXTNL POTEV
END EXT SOURCES
EXT TARGETS
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Volume-> <Member> Tsys Tgap Amd *** <Name> # <Name> # #<-factor->strg <Name> # <Name> tem strg strg*** RCHRES 2 HYDR RO 1 1 1 WDM 1002 FLOW ENGL REPL
RCHRES 2 HYDR O 1 1 1 WDM 1003 FLOW ENGL REPL
RCHRES 2 HYDR O 2 1 1 WDM 1004 FLOW ENGL REPL
RCHRES 2 HYDR STAGE 1 1 1 WDM 1005 STAG ENGL REPL
RCHRES 1 HYDR STAGE 1 1 1 WDM 1006 STAG ENGL REPL
RCHRES 1 HYDR O 1 1 1 WDM 1007 FLOW ENGL REPL
COPY 1 OUTPUT MEAN 1 1 48.4 WDM 701 FLOW ENGL REPL
COPY 501 OUTPUT MEAN 1 1 48.4 WDM 801 FLOW ENGL REPL
RCHRES 4 HYDR RO 1 1 1 WDM 1012 FLOW ENGL REPL
RCHRES 4 HYDR O 1 1 1 WDM 1013 FLOW ENGL REPL
RCHRES 4 HYDR O 2 1 1 WDM 1014 FLOW ENGL REPL
RCHRES 4 HYDR STAGE 1 1 1 WDM 1015 STAG ENGL REPL
RCHRES 3 HYDR STAGE 1 1 1 WDM 1016 STAG ENGL REPL
RCHRES 3 HYDR O 1 1 1 WDM 1017 FLOW ENGL REPL
COPY 3 OUTPUT MEAN 1 1 48.4 WDM 703 FLOW ENGL REPL
COPY 503 OUTPUT MEAN 1 1 48.4 WDM 803 FLOW ENGL REPL
RCHRES 6 HYDR RO 1 1 1 WDM 1018 FLOW ENGL REPL
RCHRES 6 HYDR O 1 1 1 WDM 1019 FLOW ENGL REPL
RCHRES 6 HYDR O 2 1 1 WDM 1020 FLOW ENGL REPL
RCHRES 6 HYDR STAGE 1 1 1 WDM 1021 STAG ENGL REPL
RCHRES 5 HYDR STAGE 1 1 1 WDM 1022 STAG ENGL REPL
RCHRES 5 HYDR O 1 1 1 WDM 1023 FLOW ENGL REPL
COPY 4 OUTPUT MEAN 1 1 48.4 WDM 704 FLOW ENGL REPL
COPY 504 OUTPUT MEAN 1 1 48.4 WDM 804 FLOW ENGL REPL
RCHRES 8 HYDR RO 1 1 1 WDM 1024 FLOW ENGL REPL
RCHRES 8 HYDR O 1 1 1 WDM 1025 FLOW ENGL REPL
RCHRES 8 HYDR O 2 1 1 WDM 1026 FLOW ENGL REPL
RCHRES 8 HYDR STAGE 1 1 1 WDM 1027 STAG ENGL REPL
RCHRES 7 HYDR STAGE 1 1 1 WDM 1028 STAG ENGL REPL
RCHRES 7 HYDR O 1 1 1 WDM 1029 FLOW ENGL REPL
COPY 5 OUTPUT MEAN 1 1 48.4 WDM 705 FLOW ENGL REPL
COPY 505 OUTPUT MEAN 1 1 48.4 WDM 805 FLOW ENGL REPL
RCHRES 10 HYDR RO 1 1 1 WDM 1030 FLOW ENGL REPL
RCHRES 10 HYDR O 1 1 1 WDM 1031 FLOW ENGL REPL
RCHRES 10 HYDR O 2 1 1 WDM 1032 FLOW ENGL REPL
RCHRES 10 HYDR STAGE 1 1 1 WDM 1033 STAG ENGL REPL
RCHRES 9 HYDR STAGE 1 1 1 WDM 1034 STAG ENGL REPL
RCHRES 9 HYDR O 1 1 1 WDM 1035 FLOW ENGL REPL
COPY 6 OUTPUT MEAN 1 1 48.4 WDM 706 FLOW ENGL REPL
COPY 506 OUTPUT MEAN 1 1 48.4 WDM 806 FLOW ENGL REPL
RCHRES 11 HYDR RO 1 1 1 WDM 1056 FLOW ENGL REPL
RCHRES 11 HYDR O 1 1 1 WDM 1057 FLOW ENGL REPL
RCHRES 11 HYDR O 2 1 1 WDM 1058 FLOW ENGL REPL
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 96 RCHRES 11 HYDR STAGE 1 1 1 WDM 1059 STAG ENGL REPL
COPY 2 OUTPUT MEAN 1 1 48.4 WDM 702 FLOW ENGL REPL
COPY 502 OUTPUT MEAN 1 1 48.4 WDM 802 FLOW ENGL REPL
END EXT TARGETS
MASS-LINK
<Volume> <-Grp> <-Member-><--Mult--> <Target> <-Grp> <-Member->*** <Name> <Name> # #<-factor-> <Name> <Name> # #***
MASS-LINK 2
PERLND PWATER SURO 0.083333 RCHRES INFLOW IVOL
END MASS-LINK 2
MASS-LINK 3
PERLND PWATER IFWO 0.083333 RCHRES INFLOW IVOL
END MASS-LINK 3
MASS-LINK 5
IMPLND IWATER SURO 0.083333 RCHRES INFLOW IVOL
END MASS-LINK 5
MASS-LINK 8
RCHRES OFLOW OVOL 2 RCHRES INFLOW IVOL
END MASS-LINK 8
MASS-LINK 12
PERLND PWATER SURO 0.083333 COPY INPUT MEAN
END MASS-LINK 12
MASS-LINK 13
PERLND PWATER IFWO 0.083333 COPY INPUT MEAN
END MASS-LINK 13
MASS-LINK 15
IMPLND IWATER SURO 0.083333 COPY INPUT MEAN
END MASS-LINK 15
MASS-LINK 16
RCHRES ROFLOW COPY INPUT MEAN
END MASS-LINK 16
MASS-LINK 17
RCHRES OFLOW OVOL 1 COPY INPUT MEAN
END MASS-LINK 17
MASS-LINK 18
RCHRES OFLOW OVOL 2 COPY INPUT MEAN
END MASS-LINK 18
END MASS-LINK
END RUN
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 97 Predeveloped HSPF Message File
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 98 Mitigated HSPF Message File
ERROR/WARNING ID: 341 6
DATE/TIME: 1978/ 1/ 4 22: 0
RCHRES: 3
The volume of water in this reach/mixed reservoir is greater than the value in the "volume" column of the last row of RCHTAB(). To continue the simulation the table has been extrapolated, based on information contained in the last two rows. This will usually result in some loss of accuracy.
If depth is being calculated it will also cause an error condition.
Relevant data are:
NROWS V1 V2 VOL
32 4.9549E+04 5.0100E+04 5.3099E+04
ERROR/WARNING ID: 341 5
DATE/TIME: 1978/ 1/ 4 22: 0
RCHRES: 3
Calculation of relative depth, using Newton's method of successive approximations, converged to an invalid value (not in range 0.0 to 1.0).
Probably ftable was extrapolated. If extrapolation was small, no problem.
Remedy; extend ftable. Relevant data are:
A B C RDEP1 RDEP2 COUNT
0.0000E+00 4.0080E+04 -2.584E+05 6.4464 6.4464 2
ERROR/WARNING ID: 341 6
DATE/TIME: 1978/ 1/ 4 21:45
RCHRES: 5
The volume of water in this reach/mixed reservoir is greater than the value in the "volume" column of the last row of RCHTAB(). To continue the simulation the table has been extrapolated, based on information contained in the last two rows. This will usually result in some loss of accuracy.
If depth is being calculated it will also cause an error condition.
Relevant data are:
NROWS V1 V2 VOL
32 3.7088E+04 3.7500E+04 3.9590E+04
ERROR/WARNING ID: 341 5
DATE/TIME: 1978/ 1/ 4 21:45
RCHRES: 5
Calculation of relative depth, using Newton's method of successive approximations, converged to an invalid value (not in range 0.0 to 1.0).
Probably ftable was extrapolated. If extrapolation was small, no problem.
Remedy; extend ftable. Relevant data are:
A B C RDEP1 RDEP2 COUNT
0.0000E+00 3.0000E+04 -1.821E+05 6.0706 6.0705E+00 2
ERROR/WARNING ID: 341 6
DATE/TIME: 1978/ 1/ 4 22: 0
RCHRES: 5
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 99 The volume of water in this reach/mixed reservoir is greater than the value in the "volume" column of the last row of RCHTAB(). To continue the simulation the table has been extrapolated, based on information contained in the last two rows. This will usually result in some loss of accuracy.
If depth is being calculated it will also cause an error condition.
Relevant data are:
NROWS V1 V2 VOL
32 3.7088E+04 3.7500E+04 4.2134E+04
ERROR/WARNING ID: 341 5
DATE/TIME: 1978/ 1/ 4 22: 0
RCHRES: 5
Calculation of relative depth, using Newton's method of successive approximations, converged to an invalid value (not in range 0.0 to 1.0).
Probably ftable was extrapolated. If extrapolation was small, no problem.
Remedy; extend ftable. Relevant data are:
A B C RDEP1 RDEP2 COUNT
0.0000E+00 3.0000E+04 -3.674E+05 12.245 1.2245E+01 2
ERROR/WARNING ID: 341 6
DATE/TIME: 1993/ 2/ 8 1:30
RCHRES: 5
The volume of water in this reach/mixed reservoir is greater than the value in the "volume" column of the last row of RCHTAB(). To continue the simulation the table has been extrapolated, based on information contained in the last two rows. This will usually result in some loss of accuracy.
If depth is being calculated it will also cause an error condition.
Relevant data are:
NROWS V1 V2 VOL
32 3.7088E+04 3.7500E+04 3.9240E+04
ERROR/WARNING ID: 341 5
DATE/TIME: 1993/ 2/ 8 1:30
RCHRES: 5
Calculation of relative depth, using Newton's method of successive approximations, converged to an invalid value (not in range 0.0 to 1.0).
Probably ftable was extrapolated. If extrapolation was small, no problem.
Remedy; extend ftable. Relevant data are:
A B C RDEP1 RDEP2 COUNT
0.0000E+00 3.0000E+04 -1.567E+05 5.2232 5.2231E+00 2
DRAFT
Conceptual Design_0.5 Infiltration 2/12/2015 3:31:44 PM Page 100 Disclaimer
Legal Notice
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Water Quality Management Plan (WQMP)
CarMax Automotive Dealership ‐ Murrieta
‐ 49 ‐
Appendix 8: Source Control
Pollutant Sources/Source Control Checklist
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
How to use this worksheet (also see instructions in Section G of the WQMP Template): 1. Review Column 1 and identify which of these potential sources of stormwater pollutants apply to your site. Check each box that applies.
2. Review Column 2 and incorporate all of the corresponding applicable BMPs in your WQMP Exhibit.
3. Review Columns 3 and 4 and incorporate all of the corresponding applicable permanent controls and operational BMPs in your WQMP. Use the format shown in Table G.1on page 23 of this WQMP Template. Describe your specific BMPs in an accompanying narrative, and explain any special conditions or situations that required omitting BMPs or substituting alternative BMPs for those shown here.
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
A. On-site storm drain
inlets
Locations of inlets.
Mark all inlets with the words
“Only Rain Down the Storm Drain” or similar. Catch Basin Markers may be available from the Riverside County Flood Control and Water Conservation District, call 951.955.1200 to verify.
Maintain and periodically repaint or replace inlet markings. Provide stormwater pollution prevention information to new site owners, lessees, or operators. See applicable operational BMPs in Fact Sheet SC-44, “Drainage System Maintenance,” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com Include the following in lease agreements: “Tenant shall not allow anyone to discharge anything to storm drains or to store or deposit materials so as to create a potential discharge to storm drains.” B. Interior floor drains
and elevator shaft sump pumps
State that interior floor drains and
elevator shaft sump pumps will be plumbed to sanitary sewer. Inspect and maintain drains to prevent
blockages and overflow.
C. Interior parking
garages
State that parking garage floor
drains will be plumbed to the sanitary sewer.
Inspect and maintain drains to prevent
blockages and overflow.
X X X
X
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
D1. Need for future
indoor & structural pest control
Note building design features that
discourage entry of pests.
Provide Integrated Pest Management
information to owners, lessees, and operators.
D2. Landscape/
Outdoor Pesticide Use
Show locations of native trees or areas of shrubs and ground cover to be undisturbed and retained. Show self-retaining landscape areas, if any. Show stormwater treatment and hydrograph modification management BMPs. (See instructions in Chapter 3, Step 5 and guidance in Chapter 5.)
State that final landscape plans will accomplish all of the following. Preserve existing native trees, shrubs, and ground cover to the maximum extent possible. Design landscaping to minimize irrigation and runoff, to promote surface infiltration where appropriate, and to minimize the use of fertilizers and pesticides that can contribute to stormwater pollution. Where landscaped areas are used to retain or detain stormwater, specify plants that are tolerant of saturated soil conditions. Consider using pest-resistant plants, especially adjacent to hardscape. To insure successful establishment, select plants appropriate to site soils, slopes, climate, sun, wind, rain, land use, air movement, ecological consistency, and plant interactions.
Maintain landscaping using minimum or no pesticides. See applicable operational BMPs in “What you should know for…..Landscape and Gardening” at http://rcflood.org/stormwater/Error! Hyperlink reference not valid.
Provide IPM information to new owners, lessees and operators.
X X
X
X
X
X
X
X
X
X
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
E. Pools, spas, ponds,
decorative fountains, and other water features.
Show location of water feature and
a sanitary sewer cleanout in an accessible area within 10 feet. (Exception: Public pools must be plumbed according to County Department of Environmental Health Guidelines.) If the Co-Permittee requires pools
to be plumbed to the sanitary sewer, place a note on the plans and state in the narrative that this connection will be made according to local requirements. See applicable operational BMPs in
“Guidelines for Maintaining Your Swimming Pool, Jacuzzi and Garden Fountain” at http://rcflood.org/stormwater/ F. Food service
For restaurants, grocery stores, and other food service operations, show location (indoors or in a covered area outdoors) of a floor sink or other area for cleaning floor mats, containers, and equipment. On the drawing, show a note that this drain will be connected to a grease interceptor before discharging to the sanitary sewer.
Describe the location and features of the designated cleaning area. Describe the items to be cleaned in this facility and how it has been sized to insure that the largest items can be accommodated. See the brochure, “The Food Service
Industry Best Management Practices for: Restaurants, Grocery Stores, Delicatessens and Bakeries” at http://rcflood.org/stormwater/Provide this brochure to new site owners, lessees, and operators. G. Refuse areas
Show where site refuse and recycled materials will be handled and stored for pickup. See local municipal requirements for sizes and other details of refuse areas. If dumpsters or other receptacles are outdoors, show how the designated area will be covered, graded, and paved to prevent runon and show locations of berms to prevent runoff from the area. Any drains from dumpsters, compactors, and tallow bin areas shall be connected to a grease removal device before discharge to sanitary sewer.
State how site refuse will be handled and provide supporting detail to what is shown on plans. State that signs will be posted on or near dumpsters with the words “Do not dump hazardous materials here” or similar. State how the following will be
implemented: Provide adequate number of receptacles. Inspect receptacles regularly; repair or replace leaky receptacles. Keep receptacles covered. Prohibit/prevent dumping of liquid or hazardous wastes. Post “no hazardous materials” signs. Inspect and pick up litter daily and clean up spills immediately. Keep spill control materials available on-site. See Fact Sheet SC-34, “Waste Handling and Disposal” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
H. Industrial processes.
Show process area.
If industrial processes are to be
located on site, state: “All process activities to be performed indoors. No processes to drain to exterior or to storm drain system.” See Fact Sheet SC-10, “NonStormwater Discharges” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com See the brochure “Industrial & Commercial Facilities Best Management Practices for: Industrial, Commercial Facilities” at http://rcflood.org/stormwater/
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
I. Outdoor storage of
equipment or materials. (See rows J and K for source control measures for vehicle cleaning, repair, and maintenance.)
Show any outdoor storage areas, including how materials will be covered. Show how areas will be graded and bermed to prevent runon or run-off from area. Storage of non-hazardous liquids shall be covered by a roof and/or drain to the sanitary sewer system, and be contained by berms, dikes, liners, or vaults. Storage of hazardous materials and wastes must be in compliance with the local hazardous materials ordinance and a Hazardous Materials Management Plan for the site.
Include a detailed description of
materials to be stored, storage areas, and structural features to prevent pollutants from entering storm drains. Where appropriate, reference documentation of compliance with the requirements of Hazardous Materials Programs for:
Hazardous Waste Generation
Hazardous Materials Release
Response and Inventory
California Accidental Release
(CalARP)
Aboveground Storage Tank
Uniform Fire Code Article 80
Section 103(b) & (c) 1991
Underground Storage Tank
www.cchealth.org/groups/hazmat
/
See the Fact Sheets SC-31, “Outdoor
Liquid Container Storage” and SC-33, “Outdoor Storage of Raw Materials ” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
J. Vehicle and
Equipment Cleaning
Show on drawings as appropriate:
(1) Commercial/industrial facilities having vehicle/equipment cleaning needs shall either provide a covered, bermed area for washing activities or discourage vehicle/equipment washing by removing hose bibs and installing signs prohibiting such uses. (2) Multi-dwelling complexes shall have a paved, bermed, and covered car wash area (unless car washing is prohibited on-site and hoses are provided with an automatic shutoff to discourage such use). (3) Washing areas for cars, vehicles, and equipment shall be paved, designed to prevent run-on to or runoff from the area, and plumbed to drain to the sanitary sewer. (4) Commercial car wash facilities shall be designed such that no runoff from the facility is discharged to the storm drain system. Wastewater from the facility shall discharge to the sanitary sewer, or a wastewater reclamation system shall be installed. If a car wash area is not provided,
describe any measures taken to discourage on-site car washing and explain how these will be enforced.
Describe operational measures to implement the following (if applicable): Washwater from vehicle and equipment washing operations shall not be discharged to the storm drain system. Refer to “Outdoor Cleaning Activities and Professional Mobile Service Providers” for many of the Potential Sources of Runoff Pollutants categories below. Brochure can be found at http://rcflood.org/stormwater/Car dealerships and similar may rinse cars with water only.
X X
X
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
K. Vehicle/Equipment
Repair and Maintenance
Accommodate all vehicle equipment repair and maintenance indoors. Or designate an outdoor work area and design the area to prevent run-on and runoff of stormwater. Show secondary containment for exterior work areas where motor oil, brake fluid, gasoline, diesel fuel, radiator fluid, acid-containing batteries or other hazardous materials or hazardous wastes are used or stored. Drains shall not be installed within the secondary containment areas. Add a note on the plans that states either (1) there are no floor drains, or (2) floor drains are connected to wastewater pretreatment systems prior to discharge to the sanitary sewer and an industrial waste discharge permit will be obtained.
State that no vehicle repair or maintenance will be done outdoors, or else describe the required features of the outdoor work area. State that there are no floor drains or if there are floor drains, note the agency from which an industrial waste discharge permit will be obtained and that the design meets that agency’s requirements. State that there are no tanks, containers or sinks to be used for parts cleaning or rinsing or, if there are, note the agency from which an industrial waste discharge permit will be obtained and that the design meets that agency’s requirements.
In the Stormwater Control Plan, note that all of the following restrictions apply to use the site:
No person shall dispose of, nor permit the disposal, directly or indirectly of vehicle fluids, hazardous materials, or rinsewater from parts cleaning into storm drains. No vehicle fluid removal shall be performed outside a building, nor on asphalt or ground surfaces, whether inside or outside a building, except in such a manner as to ensure that any spilled fluid will be in an area of secondary containment. Leaking vehicle fluids shall be contained or drained from the vehicle immediately. No person shall leave unattended drip parts or other open containers containing vehicle fluid, unless such containers are in use or in an area of secondary containment. Refer to “Automotive Maintenance & Car Care Best Management Practices for Auto Body Shops, Auto Repair Shops, Car Dealerships, Gas Stations and Fleet Service Operations”. Brochure can be found at http://rcflood.org/stormwater/Refer to Outdoor Cleaning Activities and Professional Mobile Service Providers for many of the Potential Sources of Runoff Pollutants categories below. Brochure can be found at http://rcflood.org/stormwater/ X
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
L. Fuel Dispensing
Areas
Fueling areas6 shall have
impermeable floors (i.e., portland cement concrete or equivalent smooth impervious surface) that are: a) graded at the minimum slope necessary to prevent ponding; and b) separated from the rest of the site by a grade break that prevents run-on of stormwater to the maximum extent practicable. Fueling areas shall be covered by a canopy that extends a minimum of ten feet in each direction from each pump. [Alternative: The fueling area must be covered and the cover’s minimum dimensions must be equal to or greater than the area within the grade break or fuel dispensing area1.] The canopy [or cover] shall not drain onto the fueling area.
The property owner shall dry sweep the fueling area routinely. See the Fact Sheet SD-30 , “Fueling Areas” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com 6 The fueling area shall be defined as the area extending a minimum of 6.5 feet from the corner of each fuel dispenser or the length at which the hose and nozzle assembly may be operated plus a minimum of one foot, whichever is greater.
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
M. Loading Docks
Show a preliminary design for the loading dock area, including roofing and drainage. Loading docks shall be covered and/or graded to minimize run-on to and runoff from the loading area. Roof downspouts shall be positioned to direct stormwater away from the loading area. Water from loading dock areas shall be drained to the sanitary sewer, or diverted and collected for ultimate discharge to the sanitary sewer. Loading dock areas draining directly to the sanitary sewer shall be equipped with a spill control valve or equivalent device, which shall be kept closed during periods of operation. Provide a roof overhang over the loading area or install door skirts (cowling) at each bay that enclose the end of the trailer.
Move loaded and unloaded items indoors as soon as possible. See Fact Sheet SC-30, “Outdoor Loading and Unloading,” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
N. Fire Sprinkler Test
Water
Provide a means to drain fire
sprinkler test water to the sanitary sewer.
See the note in Fact Sheet SC-41,
“Building and Grounds Maintenance,” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
O. Miscellaneous Drain
or Wash Water or Other Sources Boiler drain lines Condensate drain lines Rooftop equipment Drainage sumps Roofing, gutters, and trim. Other sources
Boiler drain lines shall be directly or indirectly connected to the sanitary sewer system and may not discharge to the storm drain system. Condensate drain lines may discharge to landscaped areas if the flow is small enough that runoff will not occur. Condensate drain lines may not discharge to the storm drain system. Rooftop equipment with potential to produce pollutants shall be roofed and/or have secondary containment. Any drainage sumps on-site shall feature a sediment sump to reduce the quantity of sediment in pumped water. Avoid roofing, gutters, and trim made of copper or other unprotected metals that may leach into runoff. Include controls for other sources as specified by local reviewer.
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
P. Plazas, sidewalks,
and parking lots.
Sweep plazas, sidewalks, and parking
lots regularly to prevent accumulation of litter and debris. Collect debris from pressure washing to prevent entry into the storm drain system. Collect washwater containing any cleaning agent or degreaser and discharge to the sanitary sewer not to a storm drain.
X X
Water Quality Management Plan (WQMP)
CarMax Automotive Dealership ‐ Murrieta
‐ 50 ‐
Appendix 9: O&M
Operation and Maintenance Plan and Documentation of Finance, Maintenance and Recording Mechanisms Water Quality Management Plan (WQMP)
CarMax Automotive Dealership ‐ Murrieta
‐43‐
Appendix 10: Educational Materials
BMP Fact Sheets, Maintenance Guidelines and Other End‐User BMP Information
The primary purpose of storm drains is to carry rain water away from developed areas to prevent flooding. Pollutants discharged to storm drains are transported directly into rivers, lakes and streams. Soaps, degreasers, automotive fluids, litter and a host of materials are washed off buildings, sidewalks, plazas and parking areas. Vehicles and equipment must be properly managed to prevent the pollution of local waterways.
Unintentional spills by mobile service operators
can flow into storm drains and pollute our
waterways. Avoid mishaps. Always have a Spill Response Kit on hand to clean up unintentional spills. Only emergency Mechanical repairs should be done in City streets and use drip pans for spills. Plumbing should be done on private property. Always store chemicals in a leak-proof container and keep covered when not in use. Window/Power Washing waste water shouldn’t be released into the streets, but should be disposed of in a sanitary sewer, landscaped area or in the soil. Soiled Carpet Cleaning wash water should be filtered before being discharged into the sanitary sewer. Dispose of all filter debris properly. Car Washing/Detailing operators should wash cars on private property and use a regulated hose nozzle for water flow control and runoff prevention. Capture and dispose of waste water and chemicals properly. Always prevent runoff water from entering storm drains.
StormWater Pollution
Car Washing / Mobile Detailers
Window and Carpet Cleaners
Power Washers
Waterproofers / Street Sweepers
Equipment cleaners or degreasers and
all mobile service providers
Storm drain pollution prevention
information for:
What you should know for...
WATER AGENCY LIST
in Riverside County
City of Banning (951) 922-3130
City of Beaumont (951) 769-8520
City of Blythe (760) 922-6161
City of Coachella (760) 398-3502
Coachella Valley Water District (760) 398-2651
City of Corona (951) 736-2259
Desert Center, CSA #51 (760) 227-3203
Eastern Municipal Water District (951) 928-3777
Elsinore Valley MWD (951) 674-3146
Farm Mutual Water Company (951) 244-4198
City of Hemet (951) 765-3712
Idyllwild Water District (951) 659-2143
Jurupa Community Services District (951) 360-8795
Lake Hemet MWD (951) 658-3241
Lee Lake Water District (951) 277-1414
March Air Force Base (951) 656-7000
Mission Springs Water District (760) 329-6448
City of Palm Springs (760) 323-8253
Rancho Caballero (951) 780-9272
Rancho California Water District (951) 296-6900
Ripley, CSA #62 (760) 922-4951
City of Riverside (951) 351-6170
Rubidoux Services District (951) 684-7580
Silent Valley Club, Inc (951) 849-4501
Valley Sanitary District (760) 347-2356
Western Municipal Water District (951) 789-5000
Yucaipa Valley Water District (909) 797-5117
REPORT ILLEGAL STORM DRAIN DISPOSAL
or online at
Online resources include:
Riverside County Flood Control and Water
Conservation District
California Storm Water Quality Association
State Water Resources Control Board
Power Washers of North America
1-800-506-2555
www.rcflood.org
•
www.rcflood.org
•
www.casqa.org
•
www.swrcb.ca.gov/
•
www.thepwna.org
Helpful telephone numbers and links: DDoo yyoouu kknnooww wwhheerree ssttrreeeettfflloowwss aaccttuuaallllyy ggoo??
OUTDOOR CLEANING
ACTIVITIES AND
PROFESSIONAL MOBILE
SERVICE PROVIDERS
ONLY RAIN IN THE DRAIN
Storm Drains are NOT connected to sanitary sewer systems and treatment plants!
REPORT ILLEGAL
STORM DRAIN
DISPOSAL
1-800-506-2555
Help Protect Our Waterways!
Use These Guidelines For Outdoor Cleaning Activities and Wash Water Disposal Did you know that disposing of pollutants
into the street, gutter, storm drain or
nearest body of water is PROHIBITED by
law and can bring about stiff penalties.
Waste wash water from Mechanics,
Plumbers, Window/Power Washers, Carpet
Cleaners, Car Washing and Mobile Detailing
activities may contain significant quantities
of motor oil, grease, chemicals, dirt,
detergents, brake pad dust, litter and other
materials.
Best Management Practices, or BMPs as
they are known, are guides to prevent
pollutants from entering the storm drains.
Each of us can do our part to keep storm
water clean by using the suggested BMPs
below:
consider dry cleaning methods first
such as a mop, broom, rag or wire brush.
Always keep a spill response kit on site.
prepare the work area before power
cleaning by using sand bags, rubber mats,
vacuum booms, containment pads or
temporary berms to keep wash water away
from the gutters and storm drains.
use vacuums or other machines to
remove and collect loose debris or litter
before applying water.
Best Management Practices
Simple solutions for both light
and heavy duty jobs:
Do...
Do...
Do...
Do...
Do...
Do...
Do not let...
Report illegal storm drain disposal,
Call Toll Free
1-800-506-2555
obtain the property owner's
permission to dispose small amounts of
power washing waste water to
landscaped, gravel or unpaved surfaces.
check with your local sanitary sewer
agency's policies on wash water disposal
regulations. (See list on reverse side).
be aware that if discharging to
landscape areas, soapy wash water may
damage landscaping. Residual wash water
may remain on paved surfaces to
evaporate. Sweep up solid residuals and
dispose of properly. Vacuum booms are
another option for capturing and collecting
wash water.
wash or waste water from
sidewalk, plaza or building cleaning go into
a street or storm drain.
Using Cleaning Agents
Think Water Conservation
Try using biodegradable/phosphate-free
products. They are easier on the
environment, but don't confuse them for
being toxic free. Soapy water entering the
storm drain system can impact the delicate
aquatic environment.
When cleaning surfaces with a high-pressure
washer or steam cleaner, additional
precautions should be taken to prevent the
discharge of pollutants into the storm drain
system. These two methods of surface
cleaning can loosen additional material that
can contaminate local waterways.
Minimize water use by using high pressure,
low volume nozzles. Be sure to check all
hoses for leaks.
Screening Wash Water
Drain Inlet Protection & Collection
of Wash Water
•
•
•
•
Equipment and Supplies
•
•
•
•
•
A thorough dry cleanup before washing
exterior surfaces, such as buildings and
decks without loose paint, sidewalks, or plaza
areas should be sufficient to protect receiving
waters. Keep debris from entering the storm
drain after cleaning by first passing the wash
water first through a “20 mesh” or finer
screen to catch the solid materials, then
disposing the mesh in a refuse container.
Prior to any washing, block all storm
drains with an impervious barrier such as
sandbags or berms, or seal the storm
drain with plugs or rubber mats.
Create a containment area with berms
and traps or take advantage of a low spot
to keep wash water contained.
Wash vehicles and equipment on grassy
or gravel areas so that the wash water
can seep into the ground.
Pump or vacuum up all wash water in the
contained area.
For special materials, equipment and
supplies:
New Pig — (800) 468-4647
Lab Safety Supply — (800) 356-0783
C&H — (800) 558-90966
W.W. Grainger — (800) 994-9174
Cleaning Equipment Trade Association
— (800) 441-0111
NLY RAIN
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DO
IN
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What is stormwater runoff?
Why is stormwater runoff a problem?
The effects of pollution
Stormwater runoff occurs when precipitation
from rain or snowmelt flows over the ground.
Impervious surfaces like driveways, sidewalks,
and streets prevent stormwater from
naturally soaking into the ground.
Stormwater can pick up debris, chemicals, dirt, and other pollutants and flow into a storm sewer system or directly to a lake, stream, river, wetland, or coastal water. Anything that enters a storm sewer system is discharged untreated into the waterbodies we use for swimming, fishing, and providing drinking water.
Polluted stormwater runoff can have
many adverse effects on plants, fish,
animals, and people.
Sediment can cloud the water
and make it difficult or
impossible for aquatic plants to
grow. Sediment also can
.
destroy aquatic habitats
Excess nutrients can cause
algae blooms. When algae die,
they sink to the bottom and decompose
in a process that removes oxygen from
the water. Fish and other aquatic
organisms can’t exist in water with low
dissolved oxygen levels.
Bacteria and other pathogens can wash
into swimming areas and create health
hazards, often making beach closures
necessary.
Debris—plastic bags, six-pack rings, bottles, and
cigarette butts—washed into waterbodies can choke, suffocate, or disable aquatic life like ducks, fish, turtles, and birds.
Household hazardous wastes like insecticides, pesticides, paint, solvents, used motor oil, and other auto fluids can poison aquatic life.
Land animals and people can become sick or die from eating diseased fish and shellfish or ingesting polluted water.
Polluted stormwater often
affects drinking water
sources. This, in turn, can
affect human health and
increase drinking water
treatment costs.
After the Storm
EPA 833-B-03-002
January 2003
For more information contact:
or visit
www.epa.gov/npdes/stormwater
www.epa.gov/nps
A Citizen’s Guide to
Understanding Stormwater
WHEN IT RAINS
IT DRAINS
WHEN IT RAINS
IT DRAINS Internet Address (URL) HTTP://www.epa.gov
Recycled/Recyclable Printed With Vegetable
Oil Based Inks on 100% Postconsumer,
Process Chlorine Free Recycled Paper
●
●
Auto care
Washing your car and
degreasing auto parts at home
can send detergents and other
contaminants through the
storm sewer system. Dumping
automotive fluids into storm
drains has the same result as
dumping the materials directly
into a waterbody.
Pet waste
Pet waste can be
a major source of
bacteria and
excess nutrients
in local waters.
When walking
your pet,
remember to pick up the
waste and dispose of it
properly. Flushing pet
waste is the best disposal
method. Leaving pet waste
on the ground increases
public health risks by
allowing harmful bacteria
and nutrients to wash into
the storm drain and
eventually into local
waterbodies.
Septic
systems
Leaking and
poorly
maintained
septic
systems release nutrients and
pathogens (bacteria and
viruses) that can be picked up
by stormwater and discharged
into nearby waterbodies.
Pathogens can cause public
health problems and
environmental concerns.
Lawn care
Excess fertilizers
and pesticides
applied to lawns
and gardens wash
off and pollute
streams. In
addition, yard
clippings and
leaves can wash
into storm drains and contribute
nutrients and organic matter to streams.
Education is essential to changing people's behavior.
Signs and markers near storm drains warn residents
that pollutants entering the drains will be carried
untreated into a local waterbody. Recycle or properly dispose of household products that contain chemicals, such as insecticides, pesticides, paint, solvents, and used motor oil and other auto fluids.
Don’t pour them onto the ground or into storm drains.
Use a commercial car wash that treats or
recycles its wastewater, or wash your car on
your yard so the water infiltrates into the
ground.
Repair leaks and dispose of used auto fluids
and batteries at designated drop-off or
recycling locations.
Don’t overwater your lawn. Consider
using a soaker hose instead of a
sprinkler.
Use pesticides and fertilizers
sparingly. When use is necessary, use
these chemicals in the recommended
amounts. Use organic mulch or safer
pest control methods whenever
possible.
Compost or mulch yard waste. Don’t
leave it in the street or sweep it into
storm drains or streams.
Cover piles of dirt or mulch being
used in landscaping projects.
Inspect your system every
3 years and pump your
tank as necessary (every 3
to 5 years).
Don't dispose of
household hazardous
waste in sinks or toilets.
Dirt, oil, and debris that collect in
parking lots and paved areas can be
washed into the storm sewer system
and eventually enter local
waterbodies.
Sweep up litter and debris from
sidewalks, driveways and parking lots,
especially around storm drains.
Cover grease storage and dumpsters
and keep them clean to avoid leaks.
Report any chemical spill to the local
hazardous waste cleanup team.
They’ll know the best way to keep
spills from harming the environment.
Erosion controls that aren’t maintained can cause
excessive amounts of sediment and debris to be
carried into the stormwater system. Construction
vehicles can leak fuel, oil, and other harmful fluids
that can be picked up by stormwater and
deposited into local waterbodies.
Divert stormwater away from disturbed or
exposed areas of the construction site.
Install silt fences, vehicle mud removal areas,
vegetative cover, and other sediment and
erosion controls and properly maintain them,
especially after rainstorms.
Prevent soil erosion by minimizing disturbed
areas during construction projects, and seed
and mulch bare areas as soon as possible.
Uncovered fueling stations allow spills to be
washed into storm drains. Cars waiting to be
repaired can leak fuel, oil, and other harmful
fluids that can be picked up by stormwater.
Clean up spills immediately and properly
dispose of cleanup materials.
Provide cover over fueling stations and
design or retrofit facilities for spill
containment.
Properly maintain fleet vehicles to prevent
oil, gas, and other discharges from being
washed into local waterbodies.
Install and maintain oil/water separators.
Lack of vegetation on streambanks can lead to erosion. Overgrazed pastures can also contribute excessive amounts of sediment to local waterbodies. Excess fertilizers and pesticides can poison aquatic animals and lead to destructive algae blooms. Livestock in streams can contaminate waterways with bacteria, making them unsafe for human contact.
Keep livestock away from streambanks and provide
them a water source away from waterbodies.
Store and apply manure away from waterbodies and in
accordance with a nutrient management plan.
Vegetate riparian areas along waterways.
Rotate animal grazing to prevent soil erosion in fields.
Apply fertilizers and pesticides according to label
instructions to save money and minimize pollution.
Permeable Pavement
Rain Barrels
Rain Gardens and
Grassy Swales
Vegetated Filter Strips
—Traditional concrete and
asphalt don’t allow water to soak into the ground.
Instead these surfaces rely on storm drains to
divert unwanted water. Permeable pavement
systems allow rain and snowmelt to soak through,
decreasing stormwater runoff.
—You can
collect rainwater from
rooftops in mosquitoproof containers. The
water can be used later on
lawn or garden areas.
—Specially
designed areas planted
with native plants can provide natural places for
rainwater to collect
and soak into the
ground. Rain from
rooftop areas or paved
areas can be diverted
into these areas rather
than into storm drains.
—Filter strips are areas of
native grass or plants created along roadways or
streams. They trap the pollutants stormwater
picks up as it flows across driveways and streets.
Residential landscaping
Improperly managed logging operations can result in erosion and sedimentation.
Conduct preharvest planning to prevent erosion and lower costs.
Use logging methods and equipment that minimize soil disturbance.
Plan and design skid trails, yard areas, and truck access roads to minimize stream crossings and avoid disturbing the forest floor.
Construct stream crossings so that they minimize erosion and physical changes to streams.
Expedite revegetation of cleared areas.
Commercial
Stormwater Pollution Solutions
Construction
Agriculture Automotive
Facilities
Forestry
Your community preserves habitat for important native plants and animals. By habitat, we mean homes; food, water, and places with space to live. The habitat is managed as part of a biological conservation easement, a legal agreement that permanently limits its use.
Many conservation easements include a waterway or wetland because plants and animals need clean, fresh water, the most limited resource in our dry Southern California climate. A waterway (also called watercourse, arroyo, wash) conveys a flowing creek, stream, or river, which provides drinking water for local and migrating wildlife.
Not all of our waterways have visible flowing water year-round. Some creeks and streams continue to flow underground, while others flow for a short time after a storm (ephemeral). The small, and often dry washes are important to wildlife because they provide habitat and their periodic flows drain into larger waterways. It's essential that people do not degrade the quality of any water that reaches local waterways.
Water supports an abundance of vegetation and a variety of life, or biodiversity.
Streamside vegetation, along dry or flowing waterways, is referred to as riparian.
Native riparian plants provide native animals with suitable food, shelter, nesting sites and escape-cover from predators.
The purpose of this publication is to
help homeowners become habitatfriendly neighbors for nearby habitat lands. The Resources Directory,
inserted inside this booklet, provides
helpful websites and contact
information for agencies,
organizations, gardens, and native
plant nurseries.
Unfortunately, our modern-day
lifestyles have negative impacts on
the environment around us. Human
activity in, or near waterways can damage the capacity of the habitat to support some kinds of plant and animal life, especially species that do not adapt to urban/suburban conditions. Here are some ways to prevent and reduce negative impacts and help restore habitat to healthy conditions.
Gerald & Buff Crosi, California Academy of Sciences
Help Your Wild Next-Door Neighbors
Living on the Edge
Reduce Impacts on Native Wildlife
Prevent light, noise, and
activity in, and adjacent to
wetlands.
CalTIP,
! If you wish to observe wildlife,
please watch from afar,
especially during the breeding
and nesting season, from
March to September. Most
wild animals are naturally
fearful of human contact.
Human activity near a nest or
den may frighten adult
animals away from young and
jeopardize their survival.
! When visiting natural areas,
disturb as little as possible. Avoid walking or riding in a stream course or on channel banks. Heavy foot traffic, horses, and off-road vehicles may cause channel banks to collapse, accelerating erosion and increasing water-born sediment and turbidity. ! Help control entry into habitat areas. Close unessential roadways to prevent access for illegal dumping, trespass, and off-road vehicle use.
! Leave nothing behind.
! Focus necessary lighting downward and inward toward your home, yard, and buildings. ! To report poaching or polluting call Californians Turn In Poachers and Polluters, a confidential secret witness program. The toll free telephone number operates 24 hours a day, 7 days a week. (See the Resources Directory insert for contact information.) Do not allow pets to roam in habitat land
where they will disturb and hunt native
wildlife. Keep pets on a leash and
droppings out of waterways. Cats and dogs
stress or kill wildlife and prevent natural
ecosystems from supporting their own
predators, such as hawks, coyotes, foxes,
and bobcats. Conversely, domesticated
animals face hazards in wild areas. Pets
may be attacked by predators, such as
coyotes and rattlesnakes, or may contract
disease, fleas, and ticks.
Do not release unwanted animals into
the wild. Abandoned cats, dogs, birds,
reptiles and fish can have significant
impacts on populations of native species,
either through disease, predation or
competition for food and space.
USDA Natural Resources Conservation Service
Diana Ruiz
Respect and protect wild animals by keeping them wild. In some instances, being a good neighbor means protecting your living area by excluding certain kinds of wildlife, mainly mammals. The human habitat includes home sites, buildings, yards, gardens, and regularly used outdoor areas. Install fencing around the human habitat portion of your property and secure enclosures to protect children, pets, and farm animals.
! Do not take small animals, such as tortoises, tadpoles, frogs, snakes, birds, lizards or eggs from the wild. Never attempt to “adopt” or domesticate a wild animal. ! Discourage dangerous predators from penetrating human habitat areas. Install fencing that will exclude predators. Place sensors that trigger sprinklers and lights to deter predators and mammals from entering areas of human activity. ! Prevent mammals from living in and near
your home by closing entries, filling holes,
and removing brush, junk, and woodpiles
near buildings.
! Don’t feed human food to wildlife. Do not
leave pet food outside. Prevent garbage from
becoming a food source for wild mammals by
sealing trash can lids. If you compost, use
closed-containers or turn piles regularly.
Compost plant material only; meat scraps
should not be mixed in a compost pile.
Brown-headed Cowbird
Lee Karney/ U.S. Fish and Wildlife Service
R. H. Barrett/ U. S. Fish and Wildlife Service
The endangered Least Bell’s Vireo is
threatened by the Brown-headed Cowbird.
Mark A. Chappell
! Exotic invaders crowd out native species both on land and in water. Do not place fish, frogs, crayfish, turtles, or aquatic plants into
creeks, streams or
lakes. Some nonnative species are not
only able to survive,
but also reproduce
explosively due to a
lack of natural
predators. For
example, the brown-headed cowbird is overwhelming
riparian habitats. The cowbird lays its eggs in another bird’s nest to the detriment of the host’s young.
! Pets are usually unable to survive in wildlands. They starve to death or are eaten. If you cannot find a
home for a pet, contact animal control, your local
animal shelter, or the Humane Society.
For more information, contact the California Department of Fish and Game. (See the Resources Directory insert for contact information.) Diana Ruiz
Reduce Impacts on Native Plants
Remove invasive, non-native plants from
home landscaping and adjacent habitat lands,
especially those that quickly spread through
waterways, displacing important native species.
DO NOT PLANT
Giant reed
Salt Cedar
Tree of Heaven
Red apple, heartleaf iceplant
Fountain grass (yellow)
Castor bean
Periwinkle
Peruvian (Calif.) pepper tree
Brazilian pepper tree
Mexican fan palm
Sweet fennel
Pampas grass/Jubata grass
Common iceplant
Myoporum species
Arundo donax
Tamarix chinensis
Ailanthus altissima
Aptenia cordifolia
Pennisetum setaceum
Ricinus communis
Vinca major
Schinus molle
Schinus terebinthifolius
Washingtonia robusta
Foeniculum vulgare
Cortaderia jubata/selloana
Mesembryanthemum crystallinum
Contact your local Resource Conservation District for help identifying invasive species and for removal of exotic weeds from waterways. Visit the California Invasive Plant Council web site for suggested plants to replace invasives. (See the Resources Directory insert for contact information.)
Protect Water Quality
Make sure that the water that flows off your
property is clean.
! Prevent trash, debris, and waste of any kind
from washing off homesites and streets into
gutters, storm drains, and dry washes. These
drainage-ways empty into streams that flow
to the Santa Ana River, and ultimately, the
ocean.
! Evaluate the flow of runoff over your property.
Place manure, barnyard bedding, and debris
in areas where water does not pool or flow,
or reuse the waste as fertilizer or mulch.
Check with your local municipality for
ordinances concerning the disposal of
manure and bedding.
! Use care when applying fertilizers, pesticides, and herbicides on your property. Read labels “before you buy and before you apply” for directions, application rates, and disposal. Apply the correct amount at the proper time, for example, not during plant dormancy.
Diana Ruiz
Invasive rrundo donax) is
being removed from Temescal Creek.
Giant Reed (A
Dispose of waste in its proper place.
! Read product labels, and dispose of
household hazardous wastes (oil based
paints, pesticides, antifreeze, motor oil,
batteries, flourescent bulbs, etc.) in
prescribed ways and at designated
disposal sites or community collection
events, not on the ground or in a storm
drain inlet. Whenever possible, reduce
the use of hazardous materials in and
around your home. Call the Only Rain
Down the Storm Drain program for
disposal dates and locations. (See the
Resources Directory insert for contact
numbers.) You can also recycle
automotive fluids, tires, and batteries at
car repair businesses.
! Dispose of trash at sanitary landfills.
! Compost yard and other organic wastes.
Praying mantis Ladybird beetle Lacewing
Better yet:
Reduce,
Reuse,
Recycle.
! Reduce or eliminate the use of pesticides by using “beneficial insects” (ladybugs, praying mantids, lacewings, etc.) If you must use a pesticide, use one with a leasttoxic rating, such as insecticidal soaps, horticultural oils, pyrethrin-based insecticides, and insect growth regulators.
! Control erosion to prevent sediment from entering runoff. ! If you have a septic system, inspect and maintain it. Poorly placed and neglected septic systems contaminate groundwater and streams.
Pollutants that flow from residential and urban areas contaminate surface water and the water that percolates into underground water basins (aquifers). Much of our local water supply is pumped from underground aquifers, so keeping runoff clean is essential.
To report any non-emergency crime, such as dumping, please call your City Police or County Sheriff Departments. To report illegal grading or dumping in waterways, contact your City or County Code Enforcement Department. (See the Resources Directory insert for contact numbers.)
Photos by Greg Balmer
Diana Ruiz
Siting Homes Near Waterways
If you are building next to a waterway, leave a buffer
between the waterway and your human habitat area of
graded pads, structures, and ornamental landscaping.
Wildlife habitat land includes areas beyond buildings,
yards, and defensible space (fire safety zones),
generally to be left undisturbed for wildlife. A buffer between the human habitat and a waterway provides
space for habitat, flood waters, and for wildlife escape during high water.
The buffer or “setback” distance will vary according to site conditions, however a minimum 100-foot setback from the top edge of a waterway, not from the water itself, is recommended. This allows space for creek/stream meander and high water flows. The banks of creeks and streams “meander”, which means they are constantly “wandering” or relocating.
Meander naturally occurs when flows cause erosion of channel banks and deposition of sediment.
As land is converted to urban uses,
the volume of flow in waterways
increases. Impervious surfaces
from streets, roofs, and parking
lots increase the amount of runoff,
erosion and pollutants that
degrade water quality.
Provide Space for Habitat, Fire, and Flood Protection
Many people are not aware of the vulnerability of natural ecosystems, nor are they aware that it is illegal to grade or alter a waterway without an assessment and permits from resource agencies and municipalities. If you propose an activity that will impact a stream, river, or lake, the California Department of Fish and Game (DFG) requires completion of a Streambed Alteration Agreement.
Depending on the activity you are proposing, you may need to obtain a permit, agreement, or other authorization from one or more government agencies. Notify DFG, U.S. Army Corps of Engineers, and the Santa Ana Regional Water Quality Control Board during early planning, prior to beginning a project that will:
use material from a streambed;
divert, obstruct, or change the natural flow or the bed, channel, or bank of any river, stream, or lake; result in the disposal or deposition of debris, waste, or other natural material where it can pass into any river, stream, or lake.
A Streambed Alteration Agreement is also required for streams that flow intermittently, such as dry washes and waterways with subsurface flow.
!
!
!
A house pad fills an important tributary to an waterway.
Robert Caliva
Frank Heyming
When building homes In fire-prone areas, avoid ridge tops and canyons. Set buildings back from the edge of steep slopes. Create a minimum distance of 100-feet of defensible space, a managed area around a home, where the amount of fuel (dead plants, dry leaves, wood) has been reduced. Consult with your local fire department or the California Department of Forestry and Fire Protection for fire safety and weed abatement information. (Please see Resources Directory insert).
Habitat-friendly Yards
Landscape with Locals. Not just any California native
plant is suitable for landscapes near habitat lands. Local native plants are the safest because they have unique
characteristics that have helped them survive in their
specific environments. Gardening with local flora helps maintain the genetic integrity of local plants and
ecosystems. It helps maintain regional variation in
vegetation and wildlife.
Why is regional variation important? If plants from other areas crossbreed with local natives, scientists fear that local populations would lose some of the unique
characteristics that are important for success in this
region. Their genetic material would no longer be unique and regionally identifiable. Plant interbreeding could reduce biological diversity, biodiversity, in the gene pool. There are important interactions between native plants, microorganisms, and the animals that use them, some of which are critical to the reproduction and survival of native plants and animals.
Create habitat in your yard for urban-adapted wildlife. Even if you live in the heart of a city, consider gardening for urban-adapted wildlife by providing a reliable water source and local native plants that provide food, shelter, and nesting sites. Each small patch of yard provides a stepping-stone of habitat from wildlands across the city. A patchwork of habitatyards creates an urban ecosystem that more closely mimics our predevelopment, native landscape. When linked together, those patches cumulatively support biodiversity. To host a variety of native birds and butterflies in your yard, select plants that flower and fruit at different times of the year. Prune trees and shrubs in fall and early winter, rather than spring, to avoid destroying bird nests.
It is essential that landowners do not confine, or encroach on waterways. Keep buildings, septic systems, horses, livestock, fencing, agricultural and ornamental plantings out of waterways and away from channel banks.
Len Nunney
Water-wise Landscapes Conserve Water
Reduce water-use by replacing unnecessary lawn areas
with native or drought-tolerant plants and with hardscape (hard surfaces), such as walkways and patios of concrete, brick, stone, decomposed granite, and permeable paving.
For places where you do need a lawn, such as play areas, plant a low water-use turf variety.
When selecting a plant, find out:
! Is it water-thirsty or drought-tolerant?
! When is its growing season; when will it need water?
Most* local native plants are dormant or slow-growing
during the hot, dry summers; their growth occurs
during our rainy season. Once established, many
survive with rainfall alone. This is the opposite for nonnative, ornamental landscapes that grow slowly, or not at all during winter, but require irrigation throughout the summer. ! Group plants with similar watering needs together, and install water-saving irrigation systems (drip, micro-sprayers) to apply the correct amount for each hydro-zone or plant grouping. Trees require deep irrigation and may need separate irrigation lines. ! Readjust your irrigation schedule for season and weather conditions. Turn off automatic systems when it’s raining. Don’t run sprinklers when the wind is blowing. Water deeply and only when needed. Water plants in the early morning or evening. Adjust irrigation systems to water soil, not concrete and pavement.
! Apply mulch (bark, compost, sawdust, gravel) to reduce evaporation from the soil surface and to control weeds.
For information about conserving water in landscapes and using native and drought tolerant plants, refer to plant databases, such as the one at be wise.com. The website will also help you create a customized watering schedule for your yard. (See the Resources Directory insert for booklist and websites.)
*Not all native plants are dormant during summer: local riparian plants are the exception. They need water year round, as they are suited for waterways. Streamside vegetation, along dry or flowing waterways, is referred to as riparian.
water
Benefits of landscaping with local native plants:
! Most native plants are drought tolerant, so they require less water. ! Natives rarely require fertilizers.
! Patches of habitat support urban-adapted wildlife, such as birds, bats and insects that help pollinate plants.
! Natives rarely require pesticides. Native plants provide their own natural pest control by attracting beneficial insects that prey on troublesome bugs. ! Local natives help preserve genetic diversity and the integrity of local ecosystems.
Diana Ruiz
Fire-wise Landscaping
Zone 1:
0-30 ft. out from buildings. (
Zone 2:
Lean, Clean and Green
Zone 1 is from See diagram on prior page.)
Grow plants that are small or succulent, such as irrigated lawns or ground covers and low growing, high-moisture shrubs. If you use native plants, use those that can be trimmed back during the dry season or that stay small with little trimming. Native plants that tolerate summer watering (see native plant lists) should be kept well hydrated.* ! Keep plants well hydrated to help them resist fire. Well-trimmed and watered plants are less likely to ignite than desiccated plants that have a buildup of dry stems and leaves. ! Fire needs fuel to burn, so remove any unnecessary plant materials. Prune dead wood and clean the landscape of dead plants, dry leaves, dry brush, firewood, and combustibles.
! Strategically place hard surfaces in your landscape, such as concrete, brick, or stone patios, driveways, pools, walls, and non-flammable decks, to interrupt the spread of fire to buildings.
Create the reduced fuel zone beginning 30 ft. from buildings and extending 100 ft. or more, depending on steepness of slope and type/density of vegetation. ! Selectively remove large shrubby plants and dense groupings. Thin overcrowded plants. Mow grasses and weedy vegetation while they are green. ! Carefully remove excess plants without disturbing the soil; mow instead of disc, to prevent erosion and invasion of non-native plants.
! In chaparral plant communities, after thinning, reduce old, woody growth by cutting plants to their bases every few years, during the summer dormancy. Young plant tissues have higher moisture content and are less flammable. The heavy pruning eliminates mature, highly flammable vegetation but maintains root systems to protect the soil from erosion.
! Low branches and plants growing under trees create “ladders” for fire to climb.
Eliminate ladder fuels, plants that serve as a link between grass and treetops. Prune the lower branches from the lower 1/3 of trees and shrubs. For trees or shrubs taller than 18 feet, prune the lower branches 6 feet above the ground. Remove dead leaves, twigs, and branches.
! In general, remove shrubs that are growing below trees, unless there is a space between the top of the shrub to the lowest branch of the tree that is three times the height of the shrub.
Reduced Fuel
Remove plants that ignite easily and burn hot, such as those with volatile oils (sages) and those that accumulate fine woody branches or many small, dry leaves (chamise). In Zone 1, remove highly volatile plants (partial list below). In Zone 2, remove or widely space volatile plant types, including:
Chamise, Adenostoma fasciculata
Brittlebrush, Encelia farinosa
California buckwheat, Eriogonum fasciculatum
White sage, Salvia apiana
Some Eucalyptus and Acacia
Black sage, Salvia mellifera
Woolly blue curls, Trichostema lanatum
Mountain blue curls, Trichostema parishii
Red Shank, Adenostoma sparsifolium
All Pine, Cypress, Juniper, and Cedar species.
*For best results with native plants, water on overcast days during summer and fall.
Create a minimum distance of 100 ft. of defensible space, a landscape that deprives fire of fuel. Use fire-resistant plants and remove plants that are highly volatile.
Mild to moderate slope
(20% to 40% slope)
Four times (4x) the height of the shrub
(Two shrubs 2’ high should be
spaced 8’ apart)
Moderate to steep slope
(greater than 40% slope)
Six times (6x) the height of the shrub
(Two shrubs 2’ high should be
spaced 12’ apart)
Shrubs
Create Space Between Plants
From edge of one shrub to the edge of the next.
Flat to mild slope
(0% to 20% slope)
Mild to moderate slope
(20% to 40% slope)
Moderate to steep slope
(greater than 40% slope)
Trees
From edge of one tree canopy to the edge of the next.
Prevent erosion and stabilize eroding
areas. If you have exposed soil surfaces,
cover with mulch, and landscape as soon as
possible. (Plants break the impact of falling
rain, and their roots hold soil in place.) Eroding
soil becomes sediment in runoff water, which
pollutes waterways. Disturbed soil also
encourages the growth of non-native weed
species.
Retain thinned, deep-rooted native plants to
anchor the soil and maintain slope stability.
Generally, tall plants have deep, broad root
systems. A goal of fire-wise landscaping is to
maximize rooting depth while minimizing fuel
volume.
For site-specific advice, contact your local Resource Conservation District (RCD) or the USDA Natural Resources Conservation Service (NRCS). For recommendations of native grasses for erosion control, contact the California Native Grasslands Society. (See the Resources Directory insert for contact information.)
Flat to mild slope
(0% to 20% slope)
Two times (2x) the height of the shrub
(Two shrubs 2’ high should be
spaced 4’ apart)
Horizontal clearance information from the California Department of Forestry and Fire Protection.
Diana Ruiz
Shrubs that do not usually tolerate water during summer.
Low shrubs
Tall, deep-rooted shrubs that stay green during summer.
Bladder pod, Isomeris arborea
Bush monkeyflower, Mimulus aurantiacus
Chaparral honeysuckle, Lonicera subspicata
Hollyleaf redberry, Rhamnus illicifolia
Redberry, Rhamnus crocea
Yellow bush-penstemon, Keckiella antirrhinoides
Bigberry manzanita, Arctostaphylos glauca
Thick-leaved lilac, Ceanothus crassifolius
Buck brush, Ceanothus cuneatus
Hairy California lilac, Ceanothus oliganthus
Mountain mahogany, Cercocarpus betuloides
Laurel sumac, Malosma laurina
Scrub oak, Quercus berberidifolia
Sugarbush, Rhus ovata
Lemonade berry, Rhus integrifolia
California Flannel bush, Fremontodendron californicum
Coffeeberry
UDSA-NRCS PLANTS Database
Native Plants for Defensible Space Landscaping in the Inland Empire If you prefer to create a landscape of native, low water-use plants, use these lists to design a yard that is fire-wise. Maintenance is essential; dead and dry plant material must be removed during dry, summer dormancy. Some native plants cannot tolerate irrigation during their summer dormancy, so may die if watered too frequently. Some need only infrequent, deep watering to remain hydrated during the dry summer and fall. The low-growing, low-fuel volume plants are suitable for Zone 1 (0-30 ft.) and beyond.
Larger shrubs and trees, for Zone 2 (30-100+ ft.), must be widely spaced (see diagram on previous page).
Shrubs for Zone 2
Shrubs that need or tolerate water during summer.
Carpenteria, Carpenteria californica
Western redbud, Cercis occidentalis
Toyon, Heteromeles arbutifolia
Nevin’s barberry, Mahonia nevinii
Coffeeberry, Rhamnus californica
Golden current, Ribes aureum.
California wild rose, Rosa californica
Western bridalwreath, Spiraea douglasii
Squawbush, Rhus trilobata
Trees for Zone 2
Trees that tolerate occasional water during summer.
Trees that need water during summer.
Catalina cherry, Prunus illicifolia ssp. Lyonii
Coast live oak, Quercus agrifolia
Valley oak, Quercus lobata
Engelman oak, Quercus engelmannii
Big leaf maple, Acer macrophyllum
White alder, Alnus rombifolia
So. California walnut, Juglans californica
California sycamore, Platanus racemosa
California black oak, Quercus kelloggii
Canyon live oak, Quercus chrysolepis
Willows: Salix laevigata, S. gooddingii
California bay laurel, Umbellularia californica
Sugarbush
Big leaf maple
J. S. Peterson @ UDSA-NRCS
Yellow bush-penstemon
Arlee M.Montalvo Paul Aigner
If you live near conservation easement land or a waterway, there are ways that you can help. Be observant of activities that might be harmful to your nearby habitat lands, or form a habitat-watch group in your neighborhood. Like a neighborhood-watch, property owners help look out for neighborhood habitat and waterways, report illegal activity, and help educate neighbors about human impacts. For help forming a habitat-watch group, contact your local Resource Conservation District or the Riverside Land Conservancy.
Habitat Land Stewards
This publication was developed by the Riverside-Corona
Resource Conservation District. www.RCRCD.com
1-07
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Printed on recycled paper
Succulents, Ground Covers, and Low Shrubs
Keep hydrated; if needed, water monthly during summer.
San Diego sedge, Carex spissa
Wild lilac, Ceanothus griseus ‘horizontalis’
California fuchsia, Epilobium canum =Zauschneria
Golden yarrow, Eriophyllum confertiflorum
Lance-leaved live-forever, Dudleya lanceolata
Chalk dudleya, Dudleya pulverulenta
Parry’s nolina, Nolina parryi
Creeping sage, Salvia sonomensis
Creeping snowberry, Symphoricarpos mollis
Chaparral yucca, Yucca whipplei = Hesperoyucca whipplei Valley cholla, Opuntia parryi
Coastal prickly pear, Opuntia littoralis
Annuals or summer-dormant perennials
No need for water during summer. There is little, if any, plant material above ground to burn.
California poppy, Eschscholzia californica
Larkspurs, delphinium, Delphinium parryi, D.cardinale
Wild Canterbury-bell, Phacelia minor
California figwort, Scrophularia californica
Baby blue eyes, Nemophila menziesii
Royal penstemon, Penstemon spectabilis
Lupine, Lupinus species (L. bicolor, L. succulentus,
L. truncatus, L. sparsiflorus)
Perennial herbs that tolerate or need water during summer Yarrow, Achillea millifolium
Columbine, Aquilegia formosa
Douglas iris, Iris douglasiana
Deer grass, Muhlenbergia rigens
Calif. blue-eyed grass, Sisyrinchium bellum
Meadow rue, Thalictrum fendleri var. polycarpum
Yerba mansa, Anemopsis californica
Coral bells, Heuchera ssp.
Common monkey flower, Mimulus guttatus
Scarlet bugler, Penstemon centranthifolius
California goldenrod, Solidago californica
Hedge nettle, Stachys bullata
Slender sedge, Carex praegracilis
Narrow-leaved milkweed, Asclepias fascicularis
Narrow-leaved milkweed
Chaparral yucca
Baby blue eyes
Low-growing, (low fuel volume) Plants for Zones 1 and 2 Arlee M.Montalvo Arlee M.Montalvo Arlee M.Montalvo
Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012