HomeMy WebLinkAboutSW1200601_2020-05-29 Sanstone Storm & EC Calcs_20200605
TABLE OF CONTENTS
Storm Water & Erosion Control Narrative……...……………...……………………… 1-3
NOAA Precipitation Charts, USGS, FEMA, and Soils………………………………..Appendix 1
Collection System Calculations…………………………………………………………Appendix 2
Hydrologic Model and BMP Design………………………………………….…………Appendix 3
Erosion Control Calculations and Specifications...……………………………………Appendix 4
NARRATIVE
Project Description
The proposed Sanstone Office & Storage Expansion is located on two adjacent parcels
(Henderson County PINs: 9632-48-7869 and 9632-48-9561) on Old Haywood Road in
Mills River, North Carolina. The development for the 6.02-acre site consists of one
office building and one storage building. The plans also incorporate a second storage
building to be constructed at a later date. Two driveway connections will be made to the
parking areas associated with the existing Sanstone office building and healthcare
facility.
This report addresses requirements to meet current NPDES Construction and Post
Construction Activities. The site is located outside of a Water Supply Watershed
Overlay District and is therefore designed based on NCDEQ design criteria.
Existing Site Conditions
The existing site is vacant and former farmland. The western half of the property is
wooded and the eastern portion along the Old Haywood Road frontage is a grass field.
The soils for the site are classified by the NRCS as Hayesville loam (HyB & HyC) and
Delanco (dillard) loam (DeB). HyB soils are classified as Hydrologic Soil Group (HSG)
Type B, whereas HyC and DeB are considered to by HSG Type C. The site primarily
drains from west to southeast to an existing drainage ditch along Old Haywood Road.
For analysis purposes, this drainage basin was split in to two areas because runoff exits
the site at two separate locations and rejoins at a common point offsite. The northern
portion of the site drains to the storm drainage system for the existing Sanstone office
building and healthcare facility.
Proposed Developed Conditions
The proposed development is considered high-density and is designed to achieve a
runoff treatment for the first inch with a piped stormwater conveyance system and a
bioretention cell. Runoff from impervious areas associated with buildings, paved drives
with curb & gutter, sidewalk, and parking are to be captured to the exten t practical.
Approximately 951 SF of impervious area is proposed to drain to storm drainage
infrastructure associated with the existing Sanstone office and healthcare facility. The
bioretention cell is designed to accommodate approximately 9,100 SF of impervious
area for a future storage building and associated pavement adjacent to the proposed
storage building. Due to site constraints a portion of offsite drainage (wooded and
grass) is captured by the storm drainage system and conveyed to the bioretention cell.
During construction a temporary construction entrance will be located along Old
Haywood Road in order to minimize construction traffic for the existing healthcare
facility.
Purpose of Report
The purpose of this analysis is to show that the site will be in compliance with NCDEQ
stormwater regulations.
Procedure
Collection System:
The proposed collection system was sized to adequately convey the 25-year, 24-hour
storm. Drainage areas were delineated for each proposed inlet in addition to Rational
‘C’ coefficients and time of concentration based on the TR-55 method. Energy
dissipation will be handled with riprap pads sized for the 25-year storm. Refer to the
provided plan set for a drainage summary.
Water Quantity:
The SCS Method using a 24-hour, Type II storm was used to determine the pre-
developed and developed annual peak stormwater discharges generated from this site.
The HydroCAD runoff routing program was used to determine these peak flows and
storm volumes as well as routing through the detention basin and bypass areas.
Stage/discharge rates for the ponds were determined based on storage, culvert and
broad crested weir equations within Hydrocad.
Calculations for the 25-year storm event were performed to show the pond is
adequately sized to pass the 25-year storm event. A vegetated spillway with matting
has been provided along with riser/barrel outlet control structures for primary drainage
from basin areas.
Water Quality:
The Simple Method was used to determine the runoff volume for the first-inch of rainfall.
The bioretention cell was then designed to allow a maximum of one-foot of ponding
above the media mix for this design volume. The underdrain system is designed to
discharge the first inch between 2-5 days after the rainfall event.
Seasonal High Water Table (SHWT):
Per NCDEQ MDC guidelines for bioretention cells, the lowest point shall be a minimum
of two feet above the SHWT. On April 21, 2020, Land Resources Manag ement
excavated a test pit at the location of the SCM. The pit was excavated to a depth of 75”
(6.25’) with no sign of the SHWT. Existing elevation at the pit location is approximately
2182.0’ and the proposed bottom of the bioretention underdrain system is 2178.75’.
Therefore, the bottom of the bioretention cell is at least 2 ’ above the SHWT.
Calculations
Drainage maps are included in the plans associated with this project. These maps
show the predeveloped and developed conditions. A summary of the entire drainage
area for the site and each individual drainage area within the site is included in this
report. Erosion Control calculations including skimmer basin design are included in
Appendix 4.
Stormwater Results
The following table shows the pre/post runoff rates for the project. There is no increase
the annual discharge for Basins 1 & 2 that drain to Old Haywood Road. There is a 0.04
CFS increase in runoff from Basin 3 draining to the storm drainage system for the
existing office and healthcare facility. The 25-year storm calculations show the
proposed detention ponds are adequate to pass the 25-year storm event.
Basin Name 1-Year
(cfs)
25-Year
(cfs)
25-Year Ponding
(Elevation - feet)
Existing Basin 1 2.11 9.36
To BMP #1 4.91 19.72
Out BMP #1 0.34 16.22 2182.98
BMP Bypass 0.96 3.48
Proposed Basin 1 0.96 18.22
Existing Basin 2 0.33 4.35
Proposed Basin 2 0.19 1.79
Existing Basin 3 0.08 1.94
Proposed Basin 3 0.12 0.82
Recommendations
Brooks Engineering recommends that the proposed development utilize stormwater
management facilities as outlined in this study in order to mitigate developed peak
stormwater discharges per NCDEQ regulations. Routine maintenance will need to be
performed in order for the stormwater management areas to operate as designed.
Appendix “1”
4/14/2020 Precipitation Frequency Data Server
https://hdsc.nws.noaa.gov/hdsc/pfds/pfds_printpage.html?lat=35.4251&lon=-82.5765&data=depth&units=english&series=pds 1/4
NOAA Atlas 14, Volume 2, Version 3
Location name: Mills River, North Carolina, USA*
Latitude: 35.4251°, Longitude: -82.5765°
Elevation: 2225.91 ft**
* source: ESRI Maps
** source: USGS
POINT PRECIPITATION FREQUENCY ESTIMATES
G.M. Bonnin, D. Martin, B. Lin, T. Parzybok, M.Yekta, and D. Riley
NOAA, National Weather Service, Silver Spring, Maryland
PF_tabular | PF_graphical | Maps_&_aerials
PF tabular
PDS-based point precipitation frequency estimates with 90% confidence intervals (in inches)1
Duration Average recurrence interval (years)
1 2 5 10 25 50 100 200 500 1000
5-min 0.367
(0.331‑0.408)
0.437
(0.394‑0.484)
0.523
(0.472‑0.581)
0.589
(0.530‑0.652)
0.675
(0.602‑0.746)
0.740
(0.657‑0.818)
0.806
(0.712‑0.893)
0.872
(0.764‑0.968)
0.957
(0.829‑1.07)
1.03
(0.880‑1.15)
10-min 0.586
(0.528‑0.651)
0.698
(0.631‑0.775)
0.838
(0.755‑0.930)
0.942
(0.847‑1.04)
1.08
(0.960‑1.19)
1.18
(1.05‑1.30)
1.28
(1.13‑1.42)
1.38
(1.21‑1.54)
1.51
(1.31‑1.69)
1.62
(1.39‑1.82)
15-min 0.732
(0.660‑0.814)
0.878
(0.793‑0.974)
1.06
(0.955‑1.18)
1.19
(1.07‑1.32)
1.36
(1.22‑1.51)
1.49
(1.32‑1.65)
1.62
(1.43‑1.79)
1.74
(1.53‑1.94)
1.91
(1.65‑2.13)
2.03
(1.74‑2.28)
30-min 1.00
(0.905‑1.12)
1.21
(1.10‑1.35)
1.51
(1.36‑1.67)
1.73
(1.55‑1.91)
2.02
(1.80‑2.23)
2.25
(1.99‑2.48)
2.48
(2.19‑2.75)
2.71
(2.38‑3.02)
3.03
(2.63‑3.39)
3.29
(2.82‑3.69)
60-min 1.25
(1.13‑1.39)
1.52
(1.37‑1.69)
1.93
(1.74‑2.14)
2.25
(2.02‑2.49)
2.69
(2.40‑2.97)
3.05
(2.70‑3.37)
3.42
(3.02‑3.78)
3.81
(3.34‑4.23)
4.35
(3.77‑4.86)
4.80
(4.11‑5.39)
2-hr 1.47
(1.32‑1.63)
1.78
(1.61‑1.97)
2.25
(2.02‑2.48)
2.62
(2.34‑2.90)
3.14
(2.79‑3.48)
3.56
(3.15‑3.95)
4.01
(3.52‑4.45)
4.48
(3.90‑4.98)
5.15
(4.42‑5.74)
5.68
(4.83‑6.38)
3-hr 1.57
(1.42‑1.76)
1.90
(1.71‑2.11)
2.38
(2.14‑2.64)
2.77
(2.48‑3.08)
3.35
(2.97‑3.72)
3.83
(3.37‑4.25)
4.33
(3.79‑4.82)
4.89
(4.22‑5.44)
5.68
(4.83‑6.37)
6.33
(5.33‑7.14)
6-hr 1.97
(1.80‑2.17)
2.35
(2.14‑2.58)
2.89
(2.64‑3.18)
3.36
(3.05‑3.69)
4.04
(3.64‑4.44)
4.62
(4.12‑5.07)
5.24
(4.63‑5.77)
5.92
(5.17‑6.52)
6.90
(5.93‑7.65)
7.73
(6.56‑8.62)
12-hr 2.48
(2.29‑2.71)
2.96
(2.72‑3.23)
3.63
(3.34‑3.96)
4.17
(3.82‑4.55)
4.92
(4.49‑5.37)
5.53
(5.03‑6.04)
6.16
(5.56‑6.74)
6.82
(6.11‑7.48)
7.72
(6.85‑8.55)
8.44
(7.42‑9.41)
24-hr 2.97
(2.75‑3.21)
3.56
(3.30‑3.85)
4.37
(4.05‑4.73)
5.02
(4.64‑5.43)
5.92
(5.45‑6.39)
6.65
(6.10‑7.18)
7.40
(6.76‑7.98)
8.18
(7.43‑8.84)
9.28
(8.35‑10.0)
10.2
(9.06‑11.0)
2-day 3.53
(3.29‑3.80)
4.21
(3.92‑4.53)
5.13
(4.78‑5.51)
5.86
(5.45‑6.29)
6.87
(6.36‑7.37)
7.68
(7.09‑8.24)
8.52
(7.83‑9.15)
9.38
(8.58‑10.1)
10.6
(9.60‑11.4)
11.5
(10.4‑12.5)
3-day 3.77
(3.52‑4.04)
4.49
(4.19‑4.81)
5.43
(5.06‑5.81)
6.17
(5.74‑6.60)
7.17
(6.66‑7.67)
7.97
(7.38‑8.54)
8.79
(8.11‑9.43)
9.63
(8.84‑10.3)
10.8
(9.82‑11.6)
11.7
(10.6‑12.6)
4-day 4.01
(3.75‑4.28)
4.77
(4.47‑5.10)
5.72
(5.35‑6.11)
6.47
(6.04‑6.91)
7.48
(6.96‑7.98)
8.27
(7.67‑8.83)
9.07
(8.38‑9.70)
9.88
(9.10‑10.6)
11.0
(10.0‑11.8)
11.9
(10.8‑12.8)
7-day 4.69
(4.40‑5.02)
5.57
(5.23‑5.96)
6.68
(6.26‑7.14)
7.56
(7.07‑8.08)
8.75
(8.16‑9.35)
9.70
(9.03‑10.4)
10.7
(9.89‑11.4)
11.7
(10.8‑12.5)
13.0
(11.9‑14.0)
14.1
(12.8‑15.2)
10-day 5.38
(5.08‑5.71)
6.37
(6.01‑6.76)
7.55
(7.14‑8.02)
8.49
(8.01‑9.01)
9.76
(9.18‑10.4)
10.8
(10.1‑11.4)
11.8
(11.0‑12.5)
12.8
(11.9‑13.6)
14.2
(13.1‑15.2)
15.3
(14.1‑16.4)
20-day 7.32
(6.94‑7.73)
8.61
(8.16‑9.10)
9.99
(9.47‑10.6)
11.1
(10.5‑11.7)
12.5
(11.8‑13.2)
13.5
(12.8‑14.3)
14.6
(13.7‑15.4)
15.6
(14.6‑16.5)
16.9
(15.8‑17.9)
17.9
(16.6‑19.0)
30-day 8.98
(8.53‑9.46)
10.5
(10.0‑11.1)
12.1
(11.5‑12.7)
13.2
(12.5‑13.9)
14.6
(13.9‑15.4)
15.7
(14.9‑16.5)
16.7
(15.8‑17.6)
17.7
(16.7‑18.6)
18.9
(17.7‑19.9)
19.7
(18.5‑20.9)
45-day 11.4
(10.9‑12.0)
13.4
(12.7‑14.0)
15.0
(14.3‑15.8)
16.3
(15.5‑17.1)
17.8
(16.9‑18.7)
18.8
(17.9‑19.8)
19.8
(18.8‑20.8)
20.7
(19.6‑21.7)
21.7
(20.6‑22.9)
22.5
(21.2‑23.7)
60-day 13.7
(13.1‑14.4)
16.0
(15.3‑16.8)
17.9
(17.0‑18.8)
19.2
(18.3‑20.2)
20.8
(19.8‑21.9)
21.9
(20.9‑23.1)
22.9
(21.8‑24.1)
23.8
(22.6‑25.1)
24.9
(23.6‑26.3)
25.6
(24.2‑27.1)
1 Precipitation frequency (PF) estimates in this table are based on frequency analysis of partial duration series (PDS).
Numbers in parenthesis are PF estimates at lower and upper bounds of the 90% confidence interval. The probability that precipitation frequency estimates (for
a given duration and average recurrence interval) will be greater than the upper bound (or less than the lower bound) is 5%. Estimates at upper bounds are
not checked against probable maximum precipitation (PMP) estimates and may be higher than currently valid PMP values.
Please refer to NOAA Atlas 14 document for more information.
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4/14/2020 Precipitation Frequency Data Server
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Large scale terrain
Large scale map
Large scale aerial
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4/14/2020 Precipitation Frequency Data Server
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NOAA Atlas 14, Volume 2, Version 3
Location name: Mills River, North Carolina, USA*
Latitude: 35.4251°, Longitude: -82.5765°
Elevation: 2225.91 ft**
* source: ESRI Maps
** source: USGS
POINT PRECIPITATION FREQUENCY ESTIMATES
G.M. Bonnin, D. Martin, B. Lin, T. Parzybok, M.Yekta, and D. Riley
NOAA, National Weather Service, Silver Spring, Maryland
PF_tabular | PF_graphical | Maps_&_aerials
PF tabular
PDS-based point precipitation frequency estimates with 90% confidence intervals (in inches/hour)1
Duration Average recurrence interval (years)
1 2 5 10 25 50 100 200 500 1000
5-min 4.40
(3.97‑4.90)
5.24
(4.73‑5.81)
6.28
(5.66‑6.97)
7.07
(6.36‑7.82)
8.10
(7.22‑8.95)
8.88
(7.88‑9.82)
9.67
(8.54‑10.7)
10.5
(9.17‑11.6)
11.5
(9.95‑12.8)
12.3
(10.6‑13.8)
10-min 3.52
(3.17‑3.91)
4.19
(3.79‑4.65)
5.03
(4.53‑5.58)
5.65
(5.08‑6.26)
6.46
(5.76‑7.14)
7.07
(6.28‑7.82)
7.69
(6.79‑8.51)
8.29
(7.27‑9.21)
9.08
(7.87‑10.2)
9.70
(8.31‑10.9)
15-min 2.93
(2.64‑3.26)
3.51
(3.17‑3.90)
4.24
(3.82‑4.71)
4.77
(4.28‑5.28)
5.45
(4.86‑6.03)
5.97
(5.30‑6.60)
6.48
(5.72‑7.17)
6.98
(6.12‑7.74)
7.62
(6.60‑8.52)
8.11
(6.96‑9.12)
30-min 2.01
(1.81‑2.23)
2.42
(2.19‑2.69)
3.01
(2.71‑3.34)
3.45
(3.10‑3.82)
4.04
(3.60‑4.47)
4.50
(3.99‑4.97)
4.96
(4.38‑5.49)
5.43
(4.76‑6.03)
6.07
(5.26‑6.78)
6.57
(5.63‑7.38)
60-min 1.25
(1.13‑1.39)
1.52
(1.37‑1.69)
1.93
(1.74‑2.14)
2.25
(2.02‑2.49)
2.69
(2.40‑2.97)
3.05
(2.70‑3.37)
3.42
(3.02‑3.78)
3.81
(3.34‑4.23)
4.35
(3.77‑4.86)
4.80
(4.11‑5.39)
2-hr 0.733
(0.660‑0.813)
0.890
(0.802‑0.984)
1.12
(1.01‑1.24)
1.31
(1.17‑1.45)
1.57
(1.40‑1.74)
1.78
(1.57‑1.97)
2.00
(1.76‑2.22)
2.24
(1.95‑2.49)
2.57
(2.21‑2.87)
2.84
(2.41‑3.19)
3-hr 0.524
(0.473‑0.585)
0.631
(0.569‑0.702)
0.792
(0.712‑0.879)
0.923
(0.827‑1.02)
1.12
(0.990‑1.24)
1.27
(1.12‑1.42)
1.44
(1.26‑1.60)
1.63
(1.41‑1.81)
1.89
(1.61‑2.12)
2.11
(1.77‑2.38)
6-hr 0.329
(0.301‑0.362)
0.392
(0.358‑0.431)
0.483
(0.440‑0.531)
0.562
(0.510‑0.617)
0.675
(0.607‑0.741)
0.771
(0.688‑0.846)
0.875
(0.773‑0.963)
0.988
(0.863‑1.09)
1.15
(0.990‑1.28)
1.29
(1.10‑1.44)
12-hr 0.206
(0.190‑0.225)
0.246
(0.226‑0.268)
0.301
(0.277‑0.329)
0.346
(0.317‑0.378)
0.408
(0.373‑0.446)
0.459
(0.417‑0.501)
0.511
(0.462‑0.559)
0.566
(0.507‑0.621)
0.641
(0.569‑0.709)
0.701
(0.615‑0.781)
24-hr 0.124
(0.115‑0.134)
0.148
(0.137‑0.161)
0.182
(0.169‑0.197)
0.209
(0.193‑0.226)
0.247
(0.227‑0.266)
0.277
(0.254‑0.299)
0.308
(0.282‑0.333)
0.341
(0.310‑0.368)
0.387
(0.348‑0.418)
0.423
(0.378‑0.459)
2-day 0.074
(0.069‑0.079)
0.088
(0.082‑0.094)
0.107
(0.099‑0.115)
0.122
(0.113‑0.131)
0.143
(0.132‑0.153)
0.160
(0.148‑0.172)
0.177
(0.163‑0.191)
0.195
(0.179‑0.210)
0.220
(0.200‑0.238)
0.240
(0.216‑0.260)
3-day 0.052
(0.049‑0.056)
0.062
(0.058‑0.067)
0.075
(0.070‑0.081)
0.086
(0.080‑0.092)
0.100
(0.092‑0.107)
0.111
(0.102‑0.119)
0.122
(0.113‑0.131)
0.134
(0.123‑0.144)
0.150
(0.136‑0.161)
0.163
(0.147‑0.175)
4-day 0.042
(0.039‑0.045)
0.050
(0.047‑0.053)
0.060
(0.056‑0.064)
0.067
(0.063‑0.072)
0.078
(0.072‑0.083)
0.086
(0.080‑0.092)
0.094
(0.087‑0.101)
0.103
(0.095‑0.110)
0.114
(0.105‑0.123)
0.124
(0.112‑0.133)
7-day 0.028
(0.026‑0.030)
0.033
(0.031‑0.035)
0.040
(0.037‑0.043)
0.045
(0.042‑0.048)
0.052
(0.049‑0.056)
0.058
(0.054‑0.062)
0.064
(0.059‑0.068)
0.069
(0.064‑0.074)
0.078
(0.071‑0.083)
0.084
(0.076‑0.090)
10-day 0.022
(0.021‑0.024)
0.027
(0.025‑0.028)
0.031
(0.030‑0.033)
0.035
(0.033‑0.038)
0.041
(0.038‑0.043)
0.045
(0.042‑0.048)
0.049
(0.046‑0.052)
0.053
(0.050‑0.057)
0.059
(0.055‑0.063)
0.064
(0.059‑0.068)
20-day 0.015
(0.014‑0.016)
0.018
(0.017‑0.019)
0.021
(0.020‑0.022)
0.023
(0.022‑0.024)
0.026
(0.025‑0.027)
0.028
(0.027‑0.030)
0.030
(0.029‑0.032)
0.032
(0.030‑0.034)
0.035
(0.033‑0.037)
0.037
(0.035‑0.040)
30-day 0.012
(0.012‑0.013)
0.015
(0.014‑0.015)
0.017
(0.016‑0.018)
0.018
(0.017‑0.019)
0.020
(0.019‑0.021)
0.022
(0.021‑0.023)
0.023
(0.022‑0.024)
0.025
(0.023‑0.026)
0.026
(0.025‑0.028)
0.027
(0.026‑0.029)
45-day 0.011
(0.010‑0.011)
0.012
(0.012‑0.013)
0.014
(0.013‑0.015)
0.015
(0.014‑0.016)
0.016
(0.016‑0.017)
0.017
(0.017‑0.018)
0.018
(0.017‑0.019)
0.019
(0.018‑0.020)
0.020
(0.019‑0.021)
0.021
(0.020‑0.022)
60-day 0.010
(0.009‑0.010)
0.011
(0.011‑0.012)
0.012
(0.012‑0.013)
0.013
(0.013‑0.014)
0.014
(0.014‑0.015)
0.015
(0.014‑0.016)
0.016
(0.015‑0.017)
0.017
(0.016‑0.017)
0.017
(0.016‑0.018)
0.018
(0.017‑0.019)
1 Precipitation frequency (PF) estimates in this table are based on frequency analysis of partial duration series (PDS).
Numbers in parenthesis are PF estimates at lower and upper bounds of the 90% confidence interval. The probability that precipitation frequency estimates (for a
given duration and average recurrence interval) will be greater than the upper bound (or less than the lower bound) is 5%. Estimates at upper bounds are not
checked against probable maximum precipitation (PMP) estimates and may be higher than currently valid PMP values.
Please refer to NOAA Atlas 14 document for more information.
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PF graphical
4/14/2020 Precipitation Frequency Data Server
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Maps & aerials
Small scale terrain
4/14/2020 Precipitation Frequency Data Server
https://hdsc.nws.noaa.gov/hdsc/pfds/pfds_printpage.html?lat=35.4251&lon=-82.5765&data=intensity&units=english&series=pds 3/4
Large scale terrain
Large scale map
Large scale aerial
+
–
3km
2mi
+
–
100km
60mi
+
–
100km
60mi
4/14/2020 Precipitation Frequency Data Server
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US Department of Commerce
National Oceanic and Atmospheric Administration
National Weather Service
National Water Center
1325 East West Highway
Silver Spring, MD 20910
Questions?: HDSC.Questions@noaa.gov
Disclaimer
+
–
100km
60mi
Hydrologic Soil Group—Henderson County, North Carolina
(SANSTONE_BOUNDARY)
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
4/3/2020
Page 1 of 43921180392121039212403921270392130039213303921360392139039211803921210392124039212703921300392133039213603921390356800356830356860356890356920356950356980357010357040357070357100357130
356800 356830 356860 356890 356920 356950 356980 357010 357040 357070 357100 357130
35° 25' 32'' N 82° 34' 39'' W35° 25' 32'' N82° 34' 25'' W35° 25' 25'' N
82° 34' 39'' W35° 25' 25'' N
82° 34' 25'' WN
Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 17N WGS84
0 50 100 200 300
Feet
0 20 40 80 120
Meters
Map Scale: 1:1,650 if printed on A landscape (11" x 8.5") sheet.
Soil Map may not be valid at this scale.
MAP LEGEND MAP INFORMATION
Area of Interest (AOI)
Area of Interest (AOI)
Soils
Soil Rating Polygons
A
A/D
B
B/D
C
C/D
D
Not rated or not available
Soil Rating Lines
A
A/D
B
B/D
C
C/D
D
Not rated or not available
Soil Rating Points
A
A/D
B
B/D
C
C/D
D
Not rated or not available
Water Features
Streams and Canals
Transportation
Rails
Interstate Highways
US Routes
Major Roads
Local Roads
Background
Aerial Photography
The soil surveys that comprise your AOI were mapped at
1:20,000.
Warning: Soil Map may not be valid at this scale.
Enlargement of maps beyond the scale of mapping can cause
misunderstanding of the detail of mapping and accuracy of soil
line placement. The maps do not show the small areas of
contrasting soils that could have been shown at a more detailed
scale.
Please rely on the bar scale on each map sheet for map
measurements.
Source of Map: Natural Resources Conservation Service
Web Soil Survey URL:
Coordinate System: Web Mercator (EPSG:3857)
Maps from the Web Soil Survey are based on the Web Mercator
projection, which preserves direction and shape but distorts
distance and area. A projection that preserves area, such as the
Albers equal-area conic projection, should be used if more
accurate calculations of distance or area are required.
This product is generated from the USDA-NRCS certified data as
of the version date(s) listed below.
Soil Survey Area: Henderson County, North Carolina
Survey Area Data: Version 19, Sep 16, 2019
Soil map units are labeled (as space allows) for map scales
1:50,000 or larger.
Date(s) aerial images were photographed: May 21, 2015—Nov
28, 2017
The orthophoto or other base map on which the soil lines were
compiled and digitized probably differs from the background
imagery displayed on these maps. As a result, some minor
shifting of map unit boundaries may be evident.
Hydrologic Soil Group—Henderson County, North Carolina
(SANSTONE_BOUNDARY)
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
4/3/2020
Page 2 of 4
Hydrologic Soil Group
Map unit symbol Map unit name Rating Acres in AOI Percent of AOI
DeB Delanco (dillard) loam, 2
to 7 percent slopes
C 0.2 2.7%
HyB Hayesville loam, 2 to 7
percent slopes
B 3.6 59.5%
HyC Hayesville loam, 7 to 15
percent slopes
C 2.3 37.8%
Totals for Area of Interest 6.0 100.0%
Description
Hydrologic soil groups are based on estimates of runoff potential. Soils are
assigned to one of four groups according to the rate of water infiltration when the
soils are not protected by vegetation, are thoroughly wet, and receive
precipitation from long-duration storms.
The soils in the United States are assigned to four groups (A, B, C, and D) and
three dual classes (A/D, B/D, and C/D). The groups are defined as follows:
Group A. Soils having a high infiltration rate (low runoff potential) when
thoroughly wet. These consist mainly of deep, well drained to excessively
drained sands or gravelly sands. These soils have a high rate of water
transmission.
Group B. Soils having a moderate infiltration rate when thoroughly wet. These
consist chiefly of moderately deep or deep, moderately well drained or well
drained soils that have moderately fine texture to moderately coarse texture.
These soils have a moderate rate of water transmission.
Group C. Soils having a slow infiltration rate when thoroughly wet. These consist
chiefly of soils having a layer that impedes the downward movement of water or
soils of moderately fine texture or fine texture. These soils have a slow rate of
water transmission.
Group D. Soils having a very slow infiltration rate (high runoff potential) when
thoroughly wet. These consist chiefly of clays that have a high shrink-swell
potential, soils that have a high water table, soils that have a claypan or clay
layer at or near the surface, and soils that are shallow over nearly impervious
material. These soils have a very slow rate of water transmission.
If a soil is assigned to a dual hydrologic group (A/D, B/D, or C/D), the first letter is
for drained areas and the second is for undrained areas. Only the soils that in
their natural condition are in group D are assigned to dual classes.
Hydrologic Soil Group—Henderson County, North Carolina SANSTONE_BOUNDARY
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
4/3/2020
Page 3 of 4
Rating Options
Aggregation Method: Dominant Condition
Component Percent Cutoff: None Specified
Tie-break Rule: Higher
Hydrologic Soil Group—Henderson County, North Carolina SANSTONE_BOUNDARY
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
4/3/2020
Page 4 of 4
1
bthomas@brooksea.com
To:mbrooks@brooksea.com
Subject:RE: Stormwater
From: mbrooks@brooksea.com <mbrooks@brooksea.com>
Sent: Tuesday, April 21, 2020 4:14 PM
To: Brandon Thomas <bthomas@brooksea.com>
Subject: FW: Stormwater
Here is location of pit for SW basin SHWT evaluation. Not sure if this is needed. But went to 75” and no sign of SHWT.
Mark C. Brooks, P.E.
Brooks Engineering Associates, P.A.
17 Arlington Street
Asheville, NC 28801
(828)232-4700
From: Seth Early <seth@landrm.com>
Sent: Tuesday, April 21, 2020 4:07 PM
To: mbrooks@brooksea.com
Cc: Walker Ferguson <walker@landrm.com>
Subject: Stormwater
Here's the info for the dropped pin on the stormwater pit.
Sent from my Verizon, Samsung Galaxy smartphone
Appendix “2”
Hydraulic Grade Line Computations -
Line Size Q Downstream Len Upstream Check JL Minor
coeff loss
Invert HGL Depth Area Vel Vel EGL Sf Invert HGL Depth Area Vel Vel EGL Sf Ave Enrgy
elev elev head elev elev elev head elev Sf loss
(in) (cfs) (ft) (ft) (ft) (sqft) (ft/s) (ft) (ft) (%) (ft) (ft) (ft) (ft) (sqft) (ft/s) (ft) (ft) (%) (%) (ft) (K) (ft) (1)(2) (3) (4) (5)(6) (7)(8) (9)(10) (11)(12) (13)(14) (15) (16)(17) (18)(19) (20) (21) (22) (23) (24)
Project File: I Number of lines: I Run Date:
Notes:
1 30 19.30 2181.00 2182.12 1.12 2.13 9.06 1.28 2183.40 0.00 27.96 2181.26 2182.38 1.12 2.13 9.06 1.28 0.92 0.26 0.00 0.442183.40 0.00
2 30 17.04 2181.26 2182.96 1.70 3.56 6.04 0.57 2183.32 0.19 24.00 2181.46 2182.96 1.50 3.08 4.78 0.36 0.26 0.06 0.00 0.272183.32 0.34
3 18 5.74 2182.46 2183.39 0.93 1.15 4.62 0.33 2183.78 0.42 5.00 2182.47 2183.46 0.99 1.24 4.97 0.38 0.39 0.02 0.00 0.122183.78 0.35
4 24 10.50 2181.96 2183.36 1.40 2.35 5.55 0.48 2183.67 0.22 166.03 2183.81 2184.97 1.16 1.89 4.47 0.31 0.30 0.49 0.00 0.272183.67 0.38
5 24 7.81 2183.81 2185.30 1.49 2.51 5.01 0.39 2185.45 0.10 202.98 2189.59 2190.58 0.99 1.56 3.12 0.15 0.23 0.46 0.00 0.002185.45 0.35
6 18 7.03 2191.09 2191.54 0.45 0.45 15.62 3.79 2195.33 0.00 100.90 2199.32 2199.77 0.45 0.45 15.62 3.79 8.10 8.18 0.00 1.712195.33 0.00
7 18 6.84 2201.50 2202.78 1.28 1.60 5.39 0.45 2203.06 0.28 88.86 2207.44 2208.45 1.01 1.27 4.26 0.28 0.38 0.34 0.00 0.002203.06 0.47
8 18 5.13 2209.27 2209.68 0.41 0.40 12.98 2.62 2212.30 0.18 101.05 2215.57 2215.99 0.41 0.40 12.98 2.62 6.20 6.27 0.00 0.672212.30 0.41
9 18 4.09 2215.57 2216.71 1.14 1.44 4.44 0.31 2216.84 0.13 120.51 2216.74 2217.51 0.77 0.92 2.84 0.13 0.26 0.31 0.00 0.082216.84 0.39
10 18 3.80 2216.74 2217.67 0.93 1.15 4.34 0.29 2217.84 0.19 55.12 2217.25 2218.00 0.75 0.88 3.32 0.17 0.29 0.16 0.00 0.062217.84 0.38
11 18 3.64 2217.25 2218.13 0.88 1.08 4.28 0.28 2218.31 0.20 67.16 2217.88 2218.61 0.73 0.85 3.38 0.18 0.29 0.20 0.00 0.132218.31 0.38
12 18 3.02 2217.88 2218.78 0.90 1.11 4.02 0.25 2218.90 0.13 53.81 2218.38 2219.04 0.66 0.75 2.72 0.11 0.25 0.13 0.00 0.132218.90 0.37
13 18 1.30 2218.38 2219.18 0.80 0.96 3.14 0.15 2219.21 0.03 69.83 2219.04 2219.46 0.43 0.41 1.35 0.03 0.19 0.13 0.00 0.032219.21 0.35
14 18 1.53 2220.56 2220.87 0.31 0.27 5.70 0.51 2221.38 0.00 24.00 2220.96 2221.27 0.31 0.27 5.70 0.51 1.64 0.39 0.00 0.102221.38 0.00
15 18 1.48 2213.03 2213.34 0.31 0.26 5.67 0.50 2213.84 0.00 23.86 2213.43 2213.74 0.31 0.26 5.67 0.50 1.66 0.40 0.00 0.102213.84 0.00
16 18 0.50 2191.25 2191.43 0.18 0.12 4.11 0.26 2191.69 0.00 23.92 2191.65 2191.83 0.18 0.12 4.11 0.26 1.66 0.40 0.00 0.052191.69 0.00
17 18 2.21 2184.31 2185.26 0.95 1.18 3.66 0.21 2185.31 0.06 44.04 2185.31 2185.87 0.56 0.60 1.87 0.05 0.21 0.09 0.00 0.042185.31 0.35
4
D50 INTERSECT= 0.5FT
LENGTH INTERSECT L= 14FT
RIP RAP PAD PARAMETERS
L= 14 FT
W= 18 FT
d50= 0.5
depth= 14 in
25-YEAR FLOW= 19.3CFS
PIPE SIZE= 30IN.
POND RIPRAP OUTLET
ST1
4
D50 INTERSECT= 0.3FT
LENGTH INTERSECT L= 10FT
RIP RAP PAD PARAMETERS
L= 10 FT
W= 12 FT
d50= 0.3
depth= 12 in
25-YEAR FLOW= 16.22CFS
PIPE SIZE= 18IN.
POND RIPRAP OUTLET
BMP #1
Appendix “3”
Simple Method for RO Volume Rv = 0.05 + 0.9 * Ia
DV = 3630 * Rd * Rv * A
BMP #1
Rv 0.32
Ia 0.30
Rd (in)1.0
A (ac)5.07
Design Vol (CF)5,858
Design Vol (acre-ft)0.134
Temporary Pool Surface Area for Bioretention
BMP #1
Max. Allowable Ponding Depth (ft)1.0
Min. Required Surface Area (SF)5,858
Provided Surface Area at bottom (SF)5,873
Provided Surface Area 1 ft above bottom (SF)6,809
Calculated Ponding Depth for RO Volume (ft)0.92
Underdrain Sizing (Per NCDEQ Stormwater Design Manual Sec A-5)
Determine Flow Rate
Surface Area at top of Media 5873 SF
Hydraulic Conductivity of Media (5 in/hr)0.000116 ft/s
Flow Rate 0.680 cfs
Apply Safety Factor (2-10 times max. flow)2.00
Design Q 1.36 cfs
Calculate the Diameter of a Single Pipe needed
to carry all the water, D 8.94 in where,
D = diameter, in inches
n = Manning's roughness coefficent (0.011)
s = slope, ft/ft (0.005 ft/ft)
Q = discharge, in cfs
Per Section A-5 (Table 2) use 3 - 6" pipes for the underdrain system.
=16
⁄
IWS Drawdown Time Calculation
Use the following orifice equation to determine the necessary orifice size to
achieve a drawdown time between 2 - 5 days.
where:
Cd =0.60 orifice coefficient
a =0.0055 orifice area (ft2) when using a 1.00 in.orifice
g =32.2 accerelation of gravity (ft/sec2)
A0 =5873 area of pond at the orifice outlet elevation (ft2)
A1 =6809 area of pond at the beginning of drawdown (ft2)
H1 =1.00 maximum head (ft)
T =235,515 seconds =2.73 days
Okay, drawdown between 2-5 days.
=
×