HomeMy WebLinkAbout20140874 Ver 1_Stormwater Management Plan_20140813Stormwater Management Plan
Cedar Ridge Tract Subdivision &
Virginia Waters Drive
Roadway Improvements
Town of Rolesville, North Carolina
502 Southtown Cir, Rolesville, NC 27571
(919) 556 -3506
Contents Include:
Project Description
Project Area and Stormwater Runoff characteristics
Proposed Stream, wetland and buffer impacts.
Pre and Post development runoff
Nitrogen Reduction and TSS Treatment
Ditch calculations
Erosion Control Measures and Rip Rap calcs
Site Area Map
SCS Soils Map
Flood Map
Drainage Area Map (culverts)
Drainage Area Map (BMP)
(1� 64� ?� --X/-/'S '4V
SEAL
24951
8 -05 -14
Aiken & Yelle Associates, PA
Professional Engineers and Land Survey
3755 Benson Drive
Raleigh, North Carolina 27609
Phone: (919) 877 -9992 Fax: (919) 877 -9979
Project Description
The project includes transportation improvement and subdivision of the 70 acre parent tract. The
proposed improvements include a 2700 feet of a 36' wide curb and guttered roadway. The
roadway is part of the Town's collector street system that has been deemed to be critical for the
town's transportation infrastructure system. The tract will be subdivided into 4 pod tracts that
ultimately will be subdivided into 117 low density residential lots.
Tract Subdivision Stormwater Runoff characteristics
The 70 acre property is zoned low density residential. The predominant soil type is Louisburg
characteristic of sandy loam surface soil to a 2 feet depth and granite type bedrock at 2 -5 foot
depth. The property is wooded primarily with pines. The property will be limited to less than
24% post development.
Project Stream Impact Area and Stormwater Runoff characteristics:
Virginia Waters Drive is located through a the 70 acre. The area to be used for this roadway and
associated stormwater controls is 7.00 acres. There will be 79,130 sf. of impervious area
associated with the Virginia Waters Drive extension project. The stormwater runoff generated
consists of typical street and residential runoff. The location of the roadway is such that most
offsite (outside of right of way) runoff is directed away from the street.
There are 2 stream crossings of Harris Creek associated with this roadway. Stream crossing #1
occurs at station 12 +80 + -. Stream crossing #2 occurs at station 39 +00 + -. The stream has been
designated as a perennial stream at both locations.
Stream crossing 1 will be managed by a 60 inch concrete pipe culvert with a buried invert. The
drainage area to this culvert is 25.0 + - acres. The length of the culvert is 137.0'. Stream crossing
#2 will be managed by a ConSpan concrete bridge 25'(w) x 10'(h) culvert. The ConSpan Bridge
is used due to the presence of granite rock at this stream crossing location. The drainage area to
this culvert is 240.0 + - acres.
Each culvert crossing is located in only location possible as dictated by topography and location
of existing streams and ponds in the area. Due to the vertical design criteria of the proposed
roadway and the steep topography large fill area are required at the stream crossing locations.
All efforts have been made to minimize and or avoid wetland and stream impacts and still
maintain public health, safety and welfare.
The runoff volumes for culvert sizing were estimated using SCS 24 hr Type II storm and based
on current zoning full build out conditions. The estimated runoff flows at each stream crossing
are as follows:
Stream crossing 1- Q2 =14.5 cfs., Q10 =36.8 cfs., Q100 =77.3 cfs.
Stream crossing 2- Q2= 53.8 cfs., Q10= 145.2 cfs., Q100= 373.4 cfs.
Proposed Stream, wetland and buffer impacts.
There are no proposed wetland impacts proposed for the proposed tract subdivision or roadway
improvements being requested at this time. As noted above there are 2 locations of stream and
buffer impacts. The impacts area as follows:
Stream crossing #1 occurs at station 12 +80
137 if stream impact including dissipater
514 sf of stream impact
8,431 sf of NRB Zone 1 impact
2,791 sf of NRB Zone 2 impact (north of stream)
2,694 sf of NRB Zone 2 impact (south of stream)
Stream crossing #2 occurs at station 39 +00 +-
0 if stream impact including dissipater
0 sf of stream impact
8,330 sf of NRB Zone 1 impact
3,098 sf of NRB Zone 2 impact (east of stream)
2,595 sf of NRB Zone 2 impact (west of stream)
Pre and Post development runoff Tract subdivision:
In the pre development and post development runoff patterns are basically unchanged. Most of
the runoff from the residential subdivision will be disconnect runoff. The street runoff is being
managed by grass bio retention areas prior to release into the buffer areas. The runoff into the
buffer areas is managed to the 1 year storm event.
The crass bioretention areas servinc the future subdivision are as follows:
Cedar
Ridge
Bioretentio
n area no.
Drainag
a area
(sq ft)
Drainag
a area
(ac)
Imperviou
s area
(sq ft)
la
Rv
Provided
WQV
(cu ft)
WQV by
Simple
Method
(cu ft)
1
18,700
0.43
5,400
0.29
0.310
693
483
2
60,300
1.38
35,500
0.59
0.580
2870
2,914
3
90,600
2.08
37,870
0.42
0.426
3210
3,218
4
24,400
0.56
16,800
0.69
0.670
1,588
1,362
5
84,500
1.94
26,959
0.32
0.337
2635
2,374
6
53,500
1.23
28,800
0.54
0.534
2338
2,383
7
31,400
0.72
9,600
0.31
0.325
938
851
8
43,100
0.99
9,100
0.21
0.240
1719
862
9
84,700
1.94
29,000
0.34
0.358
3080
2,528
10
82,900
1.90
17,500
0.21
0.240
1688
1,658
See plans for further details
Pre and Post development runoff Virginia Waters Drive:
In the pre development and post development runoff patterns are basically unchanged. All post
development runoff entering the streams at the culvert crossing will be managed by 4 grass
bioretention basins. The Bioretention basins are to be located in public drainage easements. The
bioretention areas have been designed to accommodate F runoff volume. The runoff in excess
of the WQV will be directed to the downstream headwall of each crossing via a flow split
manhole.
The grass bioretention areas are to be located as follows:
Bio area 1 Station 12 +10 north 50'
Bio area 2 Station 14 +50 north 50'
Bio area 3 Station 37 +50 north 60'
Bio area 4 Station 38 +15 south 62'
Virginia
Waters
Drive
Rolesville
NC
DS
PIP
E
SLOP
E
V
Dia
Bioretent
ion area
no.
Drainage
area
(sq ft)
Draina
ge area
(ac)
Imperviou
s area
(sq ft)
la
Rv
WQV
Provided
(cu ft)
WQV by
Simple
Method
(cu ft)
inlet
velocity
(fps)
Draw
down
time
(hours)
1
18,700
0.43
5,400
0.29
0.310
693
483
4.32
1.50
2
60,300
1.38
35,500
0.59
0.58
2,870
2,914
3.53
6.25
3
90,600
2.08
37,870
0.42
0.426
3,210
3,218
4.99
2.80
4
24,400
0.56
16,800
0.69
0.670
1,588
1,362
4.99
3.00
Totals
194,0002
1 4.45
1 95,570
17.6
14.93
18
0.015
RCP
SMH #61B
The Bioretention outflow for all storm events in excess of the first 1 inch of runoff including the
Q1OO storm are managed via a flow splitting manhole. The outflow of the manhole will be tied
into the adjacent headwalls to minimize buffer impacts associated with high velocity flows due
to steep topography. The flow chart below demonstrates the require pipe sizes to manage the
Q1OO storm event.
PIPE SECTION
Q100(c
fs)
Q100(cf
s)
RIM
US
DS
PIP
E
SLOP
E
V
Dia
Dia
use
n
TYP
E
FROM
TO
SUB
TOTAL
ELEV
INV
INV
(it)
%
fps
regd
(in)
SMH #10
HW #75
3.50
3.50
387.5
383.7
370.50
80
16.56
18.5
7.42
15
0.015
RCP
SMH #13
HW #75
18.98
18.98
385.5
378.0
370.50
64
11.72
17.6
14.93
18
0.015
RCP
SMH #61B
HW #76
11.92
11.92
352.0
346.0
332.00
78
17.95
19.3
11.58
15
0.015
RCP
SMH #64
HW #77
5.25
5.25
345.5
338.7
332.00
41
16.46
18.4
8.65
15
0.015
RCP
Nitrogen Reduction and TSS Treatment:
The nitrogen loading reductions and TSS removal is provided by the Bioretention areas shown
on plan. We have not provided loading calculations with this submittal.
Ditch calculations
No ditches are proposed with this project.
Erosion Control Measures
The tract subdivision shall comply with all applicable standards for sediment and erosion control.
The project erosion control will be provided by skimmer type sediment basins. The sediment
basins will be temporarily located in the same location as the proposed bioretention location.
The pipe sizing calculations for Q1O storm events are on the site plans are the basis of the culvert
rip rap aprons.
Rip rap dissipation is provided at HW 75, HW 77 has no dissipation requirements due to the
proposed ConSpan bridge at this location . Sizing calculations are as follows:
HW 75
Estimation of Stone Size and Dimensions For Culvert Aprons
Step 1) Compute flow velocity N -' at culvert or pared channel outlet.
Step 2) For pipe culverts D. is diameter.
For pipe arch, arch and box culverts, and paved channel outlets.
Do = A. where A. = cross - sectional area of flow at outlet.
For multiple culverts, use D. = 1.25 x Do of single culvert.
Velocity (ft /s) 9.23
Opening type Pipe Culvert
Single or multiple openings? Single
Outlet pipe diameter, Do (ft) 5.0
NOTE 1: If opening type is anything other than "Pipe Culvert ", Do =Ao
(Cross - sectional area of flow at outlet).
NOTE 2: If multiple openings, Do =1.25 x Do of single culvert.
Step 3) For apron grades of 10 % or steeper, use recommendations
For next higher zone. (Zones 1 through b).
Zone
2 Figure 8.06c
Will apron have >/ =10% grade? No
NOTE: For apron slopes equal to or greater than 10 %, use next higher Zone in Figure 8.06d to
determine apron length.
Apron length (ft) 10 Figure 8.06d
Drainage Area map Culverts
Attached here in
Drainage Area map BMPs
Attached here in and in plan set
IN
ad
IN
IN
Nj
cn
% I / ♦ \1 1 \\ / wr
I _ O
I
Cedar Rida
St-
Stora..
Grass
Biorete=n
area
Drainage
area
Drainage
area
Impervious
area
Reported
WQV
WQV by
Simple
Method
inlet
velocity
1
18,700
0.43
&400
0.29
0,310
693
483
4.32
2
60,300
1.38
35,500
0.59
0.580
2870
2 914
3.53
3
90,600
2.08
37,870
0.42
0.426
3210
3,218
4.99
384.75
810
693
344.75
2.970
2635
374.75
1.362
3080
385.25
905
429
345
3.200
771
375
4.130
956
6
53,500
113
28 800
0.54
0.534
2338
2.383
4.32
8
41100
0.99
9,100
0.21
0,240
1719
862
3.95
Elev
Area
Volume
Elev
Area
Volume
I I Elev
Area
Volume
10
82 900
1.90
17,500
0.21
0.240
1688
1 658
3.22
Bio Area
St-
Stora..
1
Bev
Area
Volume
Elev
Area
Volume
Bev
Area
Volume
383.75
575
343.75
2.300
373.75
2.640
384.75
810
693
344.75
2.970
2635
374.75
3.520
3080
385.25
905
429
345
3.200
771
375
4.130
956
1121
3406
4036
z
Elev
Area
Volume
Elev
Area
Volume
I I Elev
Area
Volume
380
450
347
1.250
381
3 290
2870
354.75
700
2338
348
2125
1688
3 81.25
3,410
838
348.25
2 620
593
3708
3076
2281
3
Eley
Area
Volume
Eley
Area
Volume
5068
1263
a
Area
Volume
Elev
Area
Volume
438.75
960
440
1,580
1588
372
2,028
1719
440.25
1 880
430
37225
2 210
530
2018
1
2249
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