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NC0002468_SARP_Rev0_Appx E_20161201
December 2016 Amec Foster Wheeler Environment & Infrastructure, Inc. Duke Energy Coal Combustion Residuals Management Program Dan River Steam Station Site Analysis and Removal Plan Revision 0 APPENDIX E: ENGINEERING EVALUATIONS AND ANALYSES - DAN RIVER DECOMMISSIONING PLAN Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 1 of 9 12/9/2016 (Initial Submittal) Calculation Title: Interim Conditions Stormwater Calculation Summary: Stormwater channels, culverts, and downdrains have been designed to convey stormwater for a 2 year, 24-hour design storm event considering short-term conditions after decommissioning of the Primary and Secondary Ash Basin dams. Notes: Revision Log: No. Description Originator Verifier Technical Reviewer 0 Initial Submittal – 12/9/2016 Chris Jordan Stephanie Stanwick Cedric H. Ruhl Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 2 of 9 12/9/2016 (Initial Submittal) OBJECTIVE: The objective of this calculation is to design the stormwater conveyance measures based on short-term conditions after decommissioning of the Primary and Secondary Ash Basin dams. METHOD: Stormwater flow rates will be calculated using SCS method. The hydraulic capacity of existing and proposed stormwater conveyances will be evaluated using Manning’s equation and HydroCAD modeling software. DEFINITION OF VARIABLES: = shear; A = area; b = bottom width; CN = curve number; d = flow depth; D = channel depth; i = rainfall depth; L = length; n = Manning’s n; P = wetted perimeter; Q = flow; R = hydraulic radius; S = longitudinal slope; t = time T = top width; Tc = time of concentration; V = velocity; and Z = channel side slope. CALCULATIONS: 1.0 Design conveyances for upstream tributary areas and ash basin closure channels Concentrated stormwater flow from upstream tributary areas was assumed to discharge across the closed ash basin at four locations shown in Figures 1 and 2, and is described in the “Final Conditions Stormwater Calculation. 1.1 Calculate time of concentration The time of concentration (Tc) is the time needed for water to flow from the most remote point in a drainage area to the drainage area outlet. The estimated time of concentration for the drainage areas is shown in Table 1. Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 3 of 9 12/9/2016 (Initial Submittal) The total time of concentration for a catchment generally consists of the following three components: sheet flow, shallow concentrated flow and channel flow. In the current analysis, sheet flow was assumed for the first 100 feet of the flow path, after which the flow was generally classified as shallow concentrated flow. However, if the flow entered a channel within the sub- catchment, then the flow was classified as channel flow. Several sub-catchments were relatively small and were hydrologically difficult to generate sheet flow, shallow concentrated flow or channel flow components for evaluation of time of concentration. A minimum time of concentration of 6 minutes (as described by TR-55, Ref. 5) was used for such relatively small sub-catchments. HydroCAD software [Ref. 2] was used to estimate time of concentration based on input parameters summarized in the following tables: Drainage Area ID Flow Length {L} (ft.) Surface Description Manning No. {n} Land Slope (ft/ft) Time of Concentration {Tc,sheet} (min) [Ref. 1] DA-1 Smooth surface 0.011 0.067 0.7 DA-2 0.150 0.050 6.5 DA-3 0.150 0.018 9.8 DA-4 0.150 0.074 5.6 DA-5A 0.011 0.003 2.5 DA-5B 0.011 0.020 1.2 DA-5C 0.011 0.012 1.4 DA-5D DA-6A 0.011 0.010 1.5 DA-6B 0.011 0.016 1.3 DA-6C 0.011 0.016 1.3 DA-6D 0.011 0.014 1.3 DA-6E 0.011 0.011 1.5 DA-6F 0.011 0.017 1.2 DA-6G DA-7A Bare Soil 0.011 0.088 0.6 DA-7B DA-7C 0.011 0.014 1.3 DA-7D 0.011 0.014 1.3 DA-7E 0.011 0.017 1.2 DA-7F 0.011 0.017 1.2 DA-7G DA-8A-1A DA-8A-1B DA-8A-1C DA-8A-1D Bare Soil 0.011 0.2 0.5 DA-8A-1E DA-8A-1F DA-8A-1G DA-8A 0.011 0.010 1.5 DA-8B 0.011 0.010 1.5 DA-8C 0.011 0.012 1.4 DA-8D -NA- Bare Soil -NA- -NA- -NA- Bare Soil Table 1: Time of Concentration from Sheet Flow -NA- -NA- -NA- Bare Soil 100 Grass:Short Bare Soil -NA- -NA- -NA- -NA- Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 4 of 9 12/9/2016 (Initial Submittal) Drainage Area ID Flow Length {L} (ft.) Surface Description Land Slope (ft/ft) Time of Concentration {Tc,scf} (min) [Ref. 1] DA-1 2,343 Unpaved 0.039 12.3 DA-2 752 Woodland 0.058 10.4 DA-3 665 Short Grass Pasture 0.051 7.0 DA-4 2,834 Grass Waterway 0.058 13.1 DA-5A 151 0.018 1.2 DA-5B 288 0.014 2.5 DA-5C 218 0.021 1.6 DA-5D DA-6A 98 0.031 0.6 DA-6B 168 0.027 1.1 DA-6C 168 0.022 1.2 DA-6D 329 0.015 2.8 DA-6E 224 0.020 1.6 DA-6F 148 0.021 1.1 DA-6G DA-7A 534 Unpaved 0.013 4.8 DA-7B DA-7C 226 0.024 1.5 DA-7D 277 0.017 2.2 DA-7E 139 0.021 1.0 DA-7F 498 0.008 5.8 DA-7G DA-8A-1A DA-8A-1B DA-8A-1C DA-8A-1D 576 Unpaved 0.024 3.8 DA-8A-1E DA-8A-1F DA-8A-1G DA-8A 695 0.052 3.2 DA-8B 252 0.020 1.8 DA-8C 320 0.013 2.9 DA-8D -NA- -NA- -NA- -NA- Table 2: Time of Concentration from Shallow Concentrated Flow -NA- -NA- -NA- Unpaved Unpaved Unpaved Unpaved -NA- -NA- -NA- -NA- Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 5 of 9 12/9/2016 (Initial Submittal) Drainage Area ID Flow Length {L} (ft.) Channel Velocity {V} (ft/s) [assumed] Time of Concentration {Tc,channel} (min) [Ref. 1] DA-1 0 DA-2 0 DA-3 0 DA-4 0 DA-5A 973 5.54 2.90 DA-5B 427 3.31 2.20 DA-5C 468 4.24 1.80 DA-5D DA-6A 212 7.97 0.40 DA-6B 202 8.11 0.40 DA-6C 318 6.10 0.90 DA-6D 269 5.73 0.80 DA-6E 552 3.89 2.40 DA-6F 289 5.40 0.90 DA-6G DA-7A 245 5.92 0.70 DA-7B DA-7C 245 4.44 0.90 DA-7D 241 4.44 0.90 DA-7E 289 5.40 0.90 DA-7F 432 4.43 1.60 DA-7G DA-8A-1A DA-8A-1B DA-8A-1C DA-8A-1D DA-8A-1E DA-8A-1F DA-8A-1G DA-8A 662 6.28 1.80 DA-8B 564 2.96 3.20 DA-8C 305 5.25 1.00 DA-8D -NA- -NA- Table 3: Time of Concentration from Channel Flow -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- 1.2 Describe land use conditions Land use conditions for the tributary drainage areas were delineated in the “Final Conditions Stormwater Calculation”. Land use conditions in drainage areas 5 through 8 were assumed to change during the ash removal phase and final grading process. Hence, stormwater analysis for the ash basin was divided in two phases. Under the initial phase of interim conditions, the basin area was assumed to be a newly graded area with hydric soil class C (Curve Number of 91), with no vegetative cover. Final long term conditions within the ash basin footprint were assumed to consist of at least 75% grass cover with hydric soil class C (Curve Number of 74), and are shown in the “Final Conditions Stormwater Calculation”. HydroCAD software was used to estimate long-term stormwater flows for drainage areas DA-1 through DA-8 for the 2-year, 24-hour storm event based on the SCS method. The 2 year storm resulted in 3.4 inch type II 24-hr rainfall [Ref. 1]. Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 6 of 9 12/9/2016 (Initial Submittal) 1.3 Stormwater channel capacity Stormwater channels in the ash basin area consist of interceptor ditches (INT), toe ditches (TD) and longitudinal ditches (LD). Interceptor ditches are used within the ash basin footprint to interrupt drainage lengths and reduce erosion potential. Toe ditches are located along the southern edge of the ash basin footprint to intercept stormwater and convey flow to the four defined outlet points which discharge into the Dan River. Longitudinal ditches are located within the ash basin footprint perpendicular to the slope and convey concentrated flows from upstream tributary drainage areas to two of the four defined outlet points which discharge into the Dan River. The proposed stormwater ditch dimensions are presented in the following table: Channel ID Channel Type Bottom Width {b} (ft) MIN. Depth {D} (ft) Left Side Slope {Z1H:V} Right Side Slope {Z 2H:V} Top Width {T} (ft) Upstream Invert (ft) Downstream Invert (ft) Length {L} (ft) Longitudinal Slope {S} (ft/ft) 5A INT 4 1.5 20 20 514 500 973 0.014 5B INT 0 1.5 20 20 506 504 379 0.005 6A INT 0 1.5 20 20 510 504 212 0.029 6B INT 0 1.5 20 20 510 504 202 0.030 6C INT 0 1.5 20 20 505 500 318 0.017 6D INT 0 1.5 20 20 504 500 269 0.015 7A INT 0 1.5 20 20 510 506 245 0.016 7B INT 0 1.5 20 20 510 509 312 0.006 7C INT 0 1.5 20 20 504 502 245 0.009 7D INT 0 1.5 20 20 504 502 241 0.009 8A INT 6 1.5 20 20 508 500 662 0.012 8B INT 0 1.5 20 20 529 526 381 0.007 DD-1 DIV 2 2 3 3 531 526 304 0.014 DD-2 DIV 2 2 3 3 531 528 48 0.056 DD-3 DIV 2 2 3 3 530 528 80 0.024 DD-4 DIV 2 2 3 3 530 529 94 0.011 DD-5 DIV 2 2 3 3 532 529 40 0.078 DD-6 DIV 2 2 3 3 532 529 40 0.078 5C TD 0 2 5 5 500 498 468 0.005 6E TD 0 2.5 3 3 500 498 552 0.005 6F TD 6 1.5 3 3 500 499 289 0.005 7E TD 6 1.5 3 3 500 499 289 0.005 7F TD 6 2 3 3 500 499 432 0.003 8C TD 6 1.5 3 3 500 499 305 0.005 LD-1A LD 6 6 3 3 508 504 335 0.012 LD-1B LD 6 4 3 3 504 500 312 0.013 LD-1C LD 6 4 3 3 500 498 184 0.010 LD-2A LD 6 4 3 3 510 506 282 0.014 LD-2B LD 6 3 3 3 506 502 306 0.014 LD-2C LD 6 3 3 3 501 498 166 0.018 Table 6: Channel Dimensions VARIES The capacity of the proposed stormwater channels was evaluated using Manning’s equation presented as follows: 𝑉=1.49 𝑛𝑃2/3 𝑃1/2 [Ref. 3] and Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 7 of 9 12/9/2016 (Initial Submittal) 𝑃=𝐴𝑉 [Ref. 3] The flow area “A” and wetted perimeter “P” were calculated using the following relationships based on the geometry of a trapezoidal channel with a flow depth “d”, bottom width “b”, left side slope “Z1”, and right side slope “Z2”: 𝐴=𝑏𝑑+0.5𝑍1 𝑑2 +0.5𝑍2 𝑑2 𝑃=𝑏+√[(𝑍1 𝑑)2 +𝑑2 ]+√[(𝑍2 𝑑)2 +𝑑2 ] The proposed stormwater channel capacities were evaluated assuming a soil channel lining for the 2-year storm. The trial flow depth and Manning’s n were iteratively modified until the channel capacity exceeded the peak runoff for the conditions modeled. Short-term straw matting with net conditions were assumed for the lining conditions of interceptor, toe-ditches, longitudinal ditches and the diversion ditch. Channel capacity was estimated as shown in the following table: Channel ID Channel Type Channel Lining Manning's n {n} [Ref. 2] Trial Flow Depth {d} (ft) Flow Area {A} (ft2) Wetted Perimeter {P} (ft) Hydraulic Radius {R} (ft) Velocity {V} (ft/s) Channel Capacity {Q} (cfs) Peak Runoff {Q} (cfs) Channel Capacity > Peak Runoff? Freeboard (in) 5A INT straw matting with net 0.033 0.51 7.2 24.4 0.3 2.4 17.25 17.16 yes 11.9 5B INT straw matting with net 0.033 0.57 6.5 22.8 0.3 1.4 9.22 8.89 yes 11.2 6A INT straw matting with net 0.033 0.35 2.5 14.0 0.2 2.4 5.85 5.75 yes 13.8 6B INT straw matting with net 0.033 0.47 4.4 18.8 0.2 3.0 13.17 12.71 yes 12.4 6C INT straw matting with net 0.033 0.5 5.0 20.0 0.2 2.3 11.57 11.40 yes 12.0 6D INT straw matting with net 0.033 0.51 5.2 20.4 0.3 2.2 11.68 11.62 yes 11.9 7A INT straw matting with net 0.033 0.62 7.7 24.8 0.3 2.6 20.31 19.49 yes 10.6 7B INT straw matting with net 0.033 0.52 5.4 20.8 0.3 1.4 7.44 7.32 yes 11.8 7C INT straw matting with net 0.033 0.55 6.1 22.0 0.3 1.8 11.14 11.08 yes 11.4 7D INT straw matting with net 0.033 0.56 6.3 22.4 0.3 1.9 11.71 11.68 yes 11.3 8A INT straw matting with net 0.033 0.52 8.5 26.8 0.3 2.3 19.47 19.01 yes 11.8 8B INT straw matting with net 0.033 0.67 9.0 26.8 0.3 1.8 16.14 11.87 yes 10.0 8A-1A DIV straw matting with net 0.033 0.31 0.9 4.0 0.2 2.0 1.83 1.29 yes 20.3 8A-1B DIV straw matting with net 0.033 0.29 0.8 3.8 0.2 3.8 3.20 1.57 yes 20.5 8A-1C DIV straw matting with net 0.033 0.1 0.2 2.6 0.1 1.4 0.31 0.27 yes 22.8 8A-1D DIV straw matting with net 0.033 0.42 1.4 4.7 0.3 2.1 2.83 2.77 yes 19.0 8A-1E DIV straw matting with net 0.033 0.21 0.6 3.3 0.2 3.8 2.10 0.75 yes 21.5 8A-1F DIV straw matting with net 0.033 0.2 0.5 3.3 0.2 3.7 1.92 1.06 yes 21.6 5C TD straw matting with net 0.033 1.08 5.8 11.0 0.5 2.2 12.59 12.27 yes 11.0 6E TD straw matting with net 0.033 1.41 6.0 8.9 0.7 2.3 13.86 13.71 yes 13.1 6F TD straw matting with net 0.033 0.56 4.3 9.5 0.5 1.9 8.23 8.11 yes 11.3 7E TD straw matting with net 0.033 0.55 4.2 9.5 0.4 1.9 7.97 7.47 yes 11.4 7F TD straw matting with net 0.033 0.76 6.3 10.8 0.6 1.9 11.67 11.51 yes 14.9 8C TD straw matting with net 0.033 0.49 3.7 9.1 0.4 1.7 6.32 6.16 yes 12.1 LD-1A LD straw matting with net 0.033 1.29 12.7 14.2 0.9 4.7 59.40 58.94 yes 56.5 LD-1B LD straw matting with net 0.033 1.46 15.2 15.2 1.0 5.1 76.73 75.75 yes 30.5 LD-1C LD straw matting with net 0.033 1.52 16.1 15.6 1.0 4.7 75.61 75.55 yes 29.8 LD-2A LD straw matting with net 0.033 1.36 13.7 14.6 0.9 5.2 70.86 70.67 yes 31.7 LD-2B LD straw matting with net 0.033 1.44 14.9 15.1 1.0 5.3 79.04 78.65 yes 18.7 LD-2C LD straw matting with net 0.033 1.36 13.7 14.6 0.9 5.8 79.78 78.57 yes 19.7 Table 7: Channel Capacity - 2 year Long-Term Straw with matting with Net Channels designed with straw matting with nets were checked for permissible shear stress, and actual flow shear as calculated using the following equation: 𝜏=𝛾𝑤𝑎𝑡𝑒𝑟𝑑𝑃 [Ref. 3] The maximum permissible shear for straw matting with nets is 2 psf [Ref. 3]. The calculated stability of the ditches was estimated as shown in the following table: Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 8 of 9 12/9/2016 (Initial Submittal) Channel ID Channel Type Channel Lining Unit Weight of Water {g water} (pcf) Flow Depth {d} (ft) Longitudinal Slope {S} (ft/ft) Shear Stress {} (psf) Permissible Shear {perm} (psf) Safe 5A INT straw matting with net 62.4 0.51 0.014 0.45 yes 5B INT straw matting with net 62.4 0.57 0.005 0.19 yes 6A INT straw matting with net 62.4 0.35 0.029 0.62 yes 6B INT straw matting with net 62.4 0.47 0.030 0.88 yes 6C INT straw matting with net 62.4 0.50 0.017 0.52 yes 6D INT straw matting with net 62.4 0.51 0.015 0.49 yes 7A INT straw matting with net 62.4 0.62 0.016 0.63 yes 7B INT straw matting with net 62.4 0.52 0.006 0.18 yes 7C INT straw matting with net 62.4 0.55 0.009 0.32 yes 7D INT straw matting with net 62.4 0.56 0.009 0.33 yes 8A INT straw matting with net 62.4 0.52 0.012 0.38 yes 8B INT straw matting with net 62.4 0.67 0.007 0.29 yes 8A-1A DIV straw matting with net 62.4 0.31 0.014 0.27 yes 8A-1B DIV straw matting with net 62.4 0.29 0.056 1.01 yes 8A-1C DIV straw matting with net 62.4 0.10 0.024 0.15 yes 8A-1D DIV straw matting with net 62.4 0.42 0.011 0.28 yes 8A-1E DIV straw matting with net 62.4 0.21 0.078 1.02 yes 8A-1F DIV straw matting with net 62.4 0.20 0.078 0.97 yes 5C TD straw matting with net 62.4 1.08 0.005 0.36 yes 6E TD straw matting with net 62.4 1.41 0.005 0.40 yes 6F TD straw matting with net 62.4 0.56 0.005 0.18 yes 7E TD straw matting with net 62.4 0.55 0.005 0.18 yes 7F TD straw matting with net 62.4 0.76 0.003 0.16 yes 8C TD straw matting with net 62.4 0.49 0.005 0.15 yes LD-1A LD straw matting with net 62.4 1.29 0.012 0.99 yes LD-1B LD straw matting with net 62.4 1.46 0.013 1.15 yes LD-1C LD straw matting with net 62.4 1.52 0.010 0.99 yes LD-2A LD straw matting with net 62.4 1.36 0.014 1.21 yes LD-2B LD straw matting with net 62.4 1.44 0.014 1.27 yes LD-2C LD straw matting with net 62.4 1.36 0.018 1.53 yes Table 8: Channel Lining Requirements - Straw Matting 2 DISCUSSION: The proposed stormwater features have capacity for the 2-year, 24-hour design storm for the conditions modeled. FIGURES: 1. Drainage area and time of concentration 2. Land use characteristics Interim Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 9 of 9 12/9/2016 (Initial Submittal) REFERENCES: 1. Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. 2. HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. 3. North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. 4. “Standard Specification for Roads and Structures”, North Carolina Department of Transportation, Raleigh, January 2012. 5. United States Department of Agriculture, “Urban Hydrology for Small W atersheds”, Technical Release 55, June 1986. FIGURE 1 Drainage Areas and Flow Paths D R A I N A G E A R E A S A N D F L O W P A T H S 1 N I S S U E / R E V I S I O N D E S C R I P T I O N YREV D M E N G . A P P R . C L I E N T L O G O : R E V I E W E D B Y : S C A L E : D A T U M : P R O J E C T I O N : T I T L E : P R O J E C T : D A T E : F I G U R E N O . R E V I S I O N N O . P R O J E C T N O . : D R A W N B Y : C L I E N T : 2 8 0 1 Y O R K M O N T R O A D , S U I T E 1 0 0 C H A R L O T T E , N C 2 8 2 0 8 T E L : ( 7 0 4 ) 3 5 7 - 8 6 0 0 F A X : ( 7 0 4 ) 3 5 7 - 8 6 3 8 L I C E N S U R E : N C E N G : F - 1 2 5 3 N C G E O L O G Y : C - 2 4 7 A m e c F o s t e r W h e e l e r E n v i r o n m e n t & I n f r a s t r u c t u r e , I n c . 7 8 1 0 - 1 4 - 0 0 6 5 D A M D E C O M M I S S I O N I N G P L A N D A N R I V E R S T E A M S T A T I O N D U K E E N E R G Y C A R O L I N A S R O C K I N G H A M C O U N T Y , N C A S S H O W N - - - - - - C S J C H R INITIA L S U B M I T T A L 20150 03 11 C H R K R D 0 1 1 / 3 / 2 0 1 5 FIGURE 2 Land Use L A N D U S E 2 N I S S U E / R E V I S I O N D E S C R I P T I O N YREV D M E N G . A P P R . C L I E N T L O G O : R E V I E W E D B Y : S C A L E : D A T U M : P R O J E C T I O N : T I T L E : P R O J E C T : D A T E : F I G U R E N O . R E V I S I O N N O . P R O J E C T N O . : D R A W N B Y : C L I E N T : 2 8 0 1 Y O R K M O N T R O A D , S U I T E 1 0 0 C H A R L O T T E , N C 2 8 2 0 8 T E L : ( 7 0 4 ) 3 5 7 - 8 6 0 0 F A X : ( 7 0 4 ) 3 5 7 - 8 6 3 8 L I C E N S U R E : N C E N G : F - 1 2 5 3 N C G E O L O G Y : C - 2 4 7 A m e c F o s t e r W h e e l e r E n v i r o n m e n t & I n f r a s t r u c t u r e , I n c . 7 8 1 0 - 1 4 - 0 0 6 5 D A M D E C O M M I S S I O N I N G P L A N D A N R I V E R S T E A M S T A T I O N D U K E E N E R G Y C A R O L I N A S R O C K I N G H A M C O U N T Y , N C A S S H O W N - - - - - - C S J C H R INITIA L S U B M I T T A L 20150 03 11 C H R K R D 0 1 1 / 3 / 2 0 1 5 REFERENCE 1 Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. Precipitation Frequency Data Server Page 1 of 3 NOAA Atlas 14, Volume 2, Version 3 Location name: Eden, North Carolina, US" Latitude: 36.4999°, Longitude:-79.7013° Elevation: 582 ft* * source: Google Maps "*�,�,,.t 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 I PF graphical I Maps & aerials PF tabular PDS-based point precipitation frequency estimates with 90% confidence intervals (in inches)' Average recurrence interval (years) Duration ��� 10 25 50 100 200 500 1000 0.363 0.433 0.512 0.567 0.633 0.676 0.717 0.754 0.796 0.826 5-min (0.331-0.397) (0.396-0.473) (0.467-0.560) (0.518-0.619) (0.575-0.688) (0.612-0.735) (0.646-0.781) (0.676-0.822) (0.708-0.869) (0.729-0.902) 0.579 0.692 0.820 0.908 1.01 1.08 1.14 1.20 1.26 1.30 10-min (0 .529-0.634) (0.633-0.757) (0.749-0.898) (0.829-0.991) (0.917-1.10) (0.974-1.17) 1 (1.03-1.24) 1 (1.07-1.30) 1 (1.12-1.38) 0.724 0.870 1.04 1.15 1.28 1.36 1.44 1.51 1.59 1.63 15-min (0.661-0.792) (0.796-0.951) (0.947-1.14) 1 (1.05-1.25) 1 (1.16-1.39) 1 (1.23-1.48) 1 (1.30-1.57) 1 (1.35-1.64) 1 (1.41-1.73) 1 (1.44-1.78) 0.993 1.20 1.47 1.66 1.89 2.05 2.21 2.35 2.52 2.64 30-min (0.906-1.09) 1 (1.10-1.31) 1 (1.35-1.61) 1 (1.52-1.82) 1 (1.72-2.06) (1.86-2.23) (1.99-2.40) (2.11-2.56) (2.24-2.75) (2.33-2.89) 1.24 1.51 1.89 2.17 2.52 2.78 3.04 3.29 3.62 3.86 60-min (1.13-1.35) (1.38-1.65) (1.73-2.07) (1.98-2.36) (2.29-2.74) (2.52-3.03) (2.74-3.31) (2.95-3.59) (3.22-3.95) (3.41-4.22) 1.47 1.79 2.25 2.61 3.08 3.45 3.83 4.20 4.71 5.10 2-hr (1.35-1.61) (1.63-1.96) (2.06-2.46) (2.38-2.85) (2.80-3.36) (3.12-3.75) (3.44-4.16) (3.75-4.57) (4.15-5.12) (4.45-5.56) 1.59 1.93 2.44 2.82 3.33 3.73 4.13 4.54 5.08 5.50 3-hr (1.46-1.73) (1.78-2.11) (2.24-2.66) (2.58-3.07) (3.03-3.62) (3.38-4.04) (3.72-4.48) (4.06-4.92) ( 4.49-5.52) ( 4.81-5.98) 1.96 2.37 2.99 3.48 4.15 4.70 5.28 5.87 6.71 7.38 6-hr (1.80-2.15) (2.18-2.61) (2.74-3.27) (3.17-3.80) (3.76-4.53) (4.22-5.12) (4.70-5.73) (5.18-6.37) (5.82-7.29) (6.31-8.02) 2.36 2.87 3.63 4.26 5.15 5.89 6.70 7.56 8.81 9.84 12-hr (2.17-2.59) (2.63-3.14) (3.32-3.96) (3.88-4.62) (4.65-5.57) (5.28-6.37) (5.94-7.21) (6.62-8.12) (7.57-9.48) (8.31-10.6 ) 2.81 3.40 4.33 5.10 6.22 7.17 8.20 9.32 11.0 12.4 24-hr (2.61-3.04) (3.16-3.68) (4.02-4.67) (4.72-5.48) (5.72-6.68) (6.55-7.69) (7.44-8.79) (8.39-10.0) (9.74-11.8) (10.9-13.3) 3.30 3.99 5.04 5.90 7.12 8.13 9.21 10.4 12.0 13.4 2-day (3.08-3.55) (3.72-4.30) (4.70-5.42) (5.48-6.33) (6.59-7.63) (7.48-8.71) (8.42-9.88) (9.40-11.1 ) ( 10.8-13.0 ) ( 11.9-14.5 ) 3.49 4.22 5.33 6.23 7.52 8.59 9.72 10.9 12.7 14.2 3-day (3.26-3.76) (3.93-4.55) (4.96-5.73) (5.79-6.69) (6.95-8.07) (7.89-9.21) (8.88-10.4) (9.92-11.8) (11.4-13.7) ( 12.6-15.3) 3.68 4.45 5.61 6.56 7.92 9.04 10.2 11.5 13.4 14.9 4-day (3.43-3.97) (4.15-4.80) (5.23-6.05) (6.10-7.06) (7.32-8.51) (8.31-9.71) (9.35-11.0) (10.4-12.4) (12.0-14.4) (13.2-16.1) 4.22 5.07 6.29 7.29 8.71 9.88 11.1 12.4 14.3 15.9 7-day (3.96-4.51) (4.75-5.42) (5.89-6.72) (6.81-7.78) (8.11-9.28) (9.14-10.5) (10.2-11.9) ( 11.4-13.3) ( 12.9-15.3) ( 14.2-17.0) 4.77 5.71 7.01 8.0 6 10.7 12.0 13.3 15.1 16.6 10-day ��69.53 (4.48-5.10 ) (5.37-6.10) (6.58-7.48 ) (7.55-8.60) (8.89-10.2 ) (9.96-11.4) (11.1-12.8) (12.2-14.2) (13.8-16.2) (15.0-17.8) 6.43 7.65 9.20 10.4 12.1 13.4 14.7 16.1 17.9 19.3 20-day (6.05-6.85) (7.21-8.16) (8.66-9.81) (9.79-11.1) (11.3-12.9) (12.5-14.3) (13.7-15.7) (14.9-172) (16.4-19.2) (17.6-20.8) 30-day 7.95 9.40 11.1 12.3 14.0 15.3 16.5 17.7 19.3 20.5 (7.53-8.41) (8.91-9.94) (10.5-11.7) (11.7-13.0) (13.2-14.8) (14.4-16.2) (15.5-17.5) (16.6-18.8) (18.0-20.5) (19.0-21.9) 45-day 10.0 11.8 13.7 15.2 17.1 18.5 19.8 21.1 22.8 24.0 (9.48-10.6) (11.2-12.5) (13.0-14.5) (14.4-16.0) (16.1-18.0) (17.4-19.5) (18.6-21.0) (19.8-22.4) (21.3-24.2) (22.3-25.6) 12.0 14.0 16.1 17.7 19.7 21.2 22.6 23.9 25.6 26.8 60-day ( 114-12.6) 1 (13.4-14.8) 1 U-15-3-1-7.0) I (16.8-18.6) 1 U-18-7-2-o.7) 1 (20.0-22.3) 1 U-21-3-2-3.8) 1 (22.5-25.2) J (24.0-27.1) 11 (25.1-28.4) 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. Back to Top PF graphical http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 Precipitation Frequency Data Server Page 2 of 3 25 ....:....:.....:.....:.....:... ... .. ..... c 20 __ -. ...... --.- ... ._._. .. r. 0 15 .2 i-I 10 IL 5 0 e c_ L ry s w Ce _c c` LL M IppC N T�'1 41S r��d N ra1 yy�--�� 7 ppE 0 .i O 6 rS7Vf 30 �64.d Diratidn 30 25 L 20 5 0 1 2 5 10 25 50 100 200 500 1000 ack tR To Average recurrence interval Maps & aerials NOAA Atlas 14, Volume 2, Version 3 created tGMTI: Mon Sep 15 14:27:08 2014 Small scale terrain Washrr 'i1101"" Grvrrs•✓ l Charlottesville's Nafirt t f Fvresir% °� i ~`cIFyn hhurgU! V i r.g i n i a. Ric _61a kslwr �` Peter e 9i "Roanoke gip ortt — — - 0dnvill F-Johnson Ctierokee Navonal rvresf' >_ td 7 bonne tree sboro . �iFis❑ah<. ,.. 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E 7W 1953 � Sti t962 17dT Td76 S 4h� ,vr � 7pp Aen 1779 _ 87� H 2 km Map OpNoUilreboangie Back to Too US Department of Commerce National Oceanic and Atmospheric Administration National Weather Service Office of Hvdroloaic Develooment 1325 East West Highway Silver Spring, MD 20910 Questions?: HDSC.Questions(a)noaa.aov Disclaimer http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 REFERENCE 2 HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. 1 DA-1 S-01 DA-5A S-02 DA-5B S-03 DA-5C S-04 DA-5D S-11 DA-6A S-12 DA-6B S-13 DA-6D S-14 DA-6C S-15 DA-6E S-16 DA-6F S-17 DA-6G R-11 LD-1A R-12 LD-1B R-13 LD-1C R01 Lateral Ditch 1PCB 36" Culvert 6P Sediment Basin (SB-2) 49P Sediment Basin 1 Routing Diagram for ST 1 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Runoff Area=22.679 ac 0.00% Impervious Runoff Depth>1.63"Subcatchment 1: DA-1 Flow Length=2,443' Tc=13.0 min CN=83 Runoff=55.79 cfs 3.085 af Runoff Area=4.000 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-01: DA-5A Flow Length=1,224' Tc=5.1 min CN=91 Runoff=17.16 cfs 0.763 af Runoff Area=2.130 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-02: DA-5B Flow Length=815' Tc=5.9 min CN=91 Runoff=8.89 cfs 0.406 af Runoff Area=2.830 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-03: DA-5C Flow Length=786' Tc=4.8 min CN=91 Runoff=12.27 cfs 0.540 af Runoff Area=2.180 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-04: DA-5D Tc=5.0 min CN=91 Runoff=9.39 cfs 0.416 af Runoff Area=1.230 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-11: DA-6A Flow Length=409' Tc=2.5 min CN=91 Runoff=5.75 cfs 0.235 af Runoff Area=2.700 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-12: DA-6B Flow Length=470' Tc=2.4 min CN=91 Runoff=12.67 cfs 0.516 af Runoff Area=2.700 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-13: DA-6D Flow Length=699' Tc=5.0 min CN=91 Runoff=11.62 cfs 0.515 af Runoff Area=2.510 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-14: DA-6C Flow Length=586' Tc=3.5 min CN=91 Runoff=11.36 cfs 0.479 af Runoff Area=3.250 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-15: DA-6E Flow Length=876' Tc=5.6 min CN=91 Runoff=13.71 cfs 0.620 af Runoff Area=1.780 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-16: DA-6F Flow Length=537' Tc=3.4 min CN=91 Runoff=8.08 cfs 0.340 af Runoff Area=2.610 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-17: DA-6G Tc=5.0 min CN=91 Runoff=11.24 cfs 0.498 af Avg. Flow Depth=1.33' Max Vel=4.46 fps Inflow=59.30 cfs 3.835 afReach R-11: LD-1A n=0.035 L=335.0' S=0.0123 '/' Capacity=1,495.75 cfs Outflow=59.09 cfs 3.828 af Avg. Flow Depth=1.50' Max Vel=4.83 fps Inflow=76.48 cfs 4.823 afReach R-12: LD-1B n=0.035 L=312.0' S=0.0127 '/' Capacity=599.39 cfs Outflow=75.96 cfs 4.816 af Avg. Flow Depth=1.57' Max Vel=4.51 fps Inflow=75.96 cfs 4.816 afReach R-13: LD-1C n=0.035 L=184.0' S=0.0105 '/' Capacity=545.58 cfs Outflow=75.76 cfs 4.811 af Avg. Flow Depth=0.55' Max Vel=2.36 fps Inflow=26.01 cfs 1.170 afReach R01: Lateral Ditch n=0.035 L=1,177.0' S=0.0144 '/' Capacity=223.50 cfs Outflow=19.26 cfs 1.160 af Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Peak Elev=514.19' Inflow=55.79 cfs 3.085 afPond 1P: 36" Culvert 36.0" Round Culvert n=0.012 L=157.0' S=0.0127 '/' Outflow=55.79 cfs 3.085 af Peak Elev=502.22' Storage=4.967 af Inflow=105.30 cfs 6.269 afPond 6P: Sediment Basin (SB-2) Primary=3.09 cfs 1.451 af Secondary=0.00 cfs 0.000 af Outflow=3.09 cfs 1.451 af Peak Elev=501.38' Storage=2.115 af Inflow=38.41 cfs 2.116 afPond 49P: Sediment Basin 1 Primary=0.00 cfs 0.000 af Secondary=0.00 cfs 0.000 af Outflow=0.00 cfs 0.000 af Total Runoff Area = 50.599 ac Runoff Volume = 8.413 af Average Runoff Depth = 2.00" 100.00% Pervious = 50.599 ac 0.00% Impervious = 0.000 ac Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 1: DA-1 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 55.79 cfs @ 12.05 hrs, Volume= 3.085 af, Depth> 1.63" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 0.322 73 Woods, Fair, HSG C 9.380 96 Gravel surface, HSG C 12.977 74 >75% Grass cover, Good, HSG C 22.679 83 Weighted Average 22.679 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 0.7 100 0.0670 2.30 Sheet Flow, TC for DA1 Smooth surfaces n= 0.011 P2= 3.40" 12.3 2,343 0.0390 3.18 Shallow Concentrated Flow, TC for DA1 Unpaved Kv= 16.1 fps 13.0 2,443 Total Subcatchment 1: DA-1 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 60 55 50 45 40 35 30 25 20 15 10 5 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=22.679 ac Runoff Volume=3.085 af Runoff Depth>1.63" Flow Length=2,443' Tc=13.0 min CN=83 55.79 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 5HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-01: DA-5A Runoff = 17.16 cfs @ 11.96 hrs, Volume= 0.763 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 4.000 91 Newly graded area, HSG C 4.000 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.0 100 0.0300 1.67 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.2 151 0.0183 2.18 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 2.9 973 0.0134 5.66 79.20 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.031 5.1 1,224 Total Subcatchment S-01: DA-5A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=4.000 ac Runoff Volume=0.763 af Runoff Depth>2.29" Flow Length=1,224' Tc=5.1 min CN=91 17.16 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 6HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-02: DA-5B Runoff = 8.89 cfs @ 11.97 hrs, Volume= 0.406 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.130 91 Newly graded area, HSG C 2.130 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.2 100 0.0200 1.42 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 2.5 288 0.0140 1.90 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 2.2 427 0.0048 3.18 44.53 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.033 5.9 815 Total Subcatchment S-02: DA-5B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.130 ac Runoff Volume=0.406 af Runoff Depth>2.29" Flow Length=815' Tc=5.9 min CN=91 8.89 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 7HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-03: DA-5C Runoff = 12.27 cfs @ 11.96 hrs, Volume= 0.540 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.830 91 Newly graded area, HSG C 2.830 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.4 100 0.0136 1.22 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.6 218 0.0193 2.24 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 1.8 468 0.0100 4.33 60.60 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 4.8 786 Total Subcatchment S-03: DA-5C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 12 10 8 6 4 2 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.830 ac Runoff Volume=0.540 af Runoff Depth>2.29" Flow Length=786' Tc=4.8 min CN=91 12.27 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 8HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-04: DA-5D Runoff = 9.39 cfs @ 11.96 hrs, Volume= 0.416 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.180 91 Newly graded area, HSG C 2.180 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-04: DA-5D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.180 ac Runoff Volume=0.416 af Runoff Depth>2.29" Tc=5.0 min CN=91 9.39 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 9HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-11: DA-6A Runoff = 5.75 cfs @ 11.93 hrs, Volume= 0.235 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.230 91 Newly graded area, HSG C 1.230 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.6 100 0.0091 1.03 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 0.6 97 0.0310 2.83 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 0.3 212 0.0500 11.29 158.09 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 2.5 409 Total Subcatchment S-11: DA-6A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=1.230 ac Runoff Volume=0.235 af Runoff Depth>2.29" Flow Length=409' Tc=2.5 min CN=91 5.75 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 10HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-12: DA-6B Runoff = 12.67 cfs @ 11.93 hrs, Volume= 0.516 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.700 91 Newly graded area, HSG C 2.700 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.0 100 0.0331 1.73 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.1 168 0.0270 2.65 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 0.3 202 0.0500 11.29 158.09 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 2.4 470 Total Subcatchment S-12: DA-6B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 14 12 10 8 6 4 2 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.700 ac Runoff Volume=0.516 af Runoff Depth>2.29" Flow Length=470' Tc=2.4 min CN=91 12.67 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 11HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-13: DA-6D Runoff = 11.62 cfs @ 11.96 hrs, Volume= 0.515 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.700 91 Newly graded area, HSG C 2.700 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.3 100 0.0150 1.26 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 2.8 329 0.0150 1.97 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 0.9 270 0.0090 4.79 67.07 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 5.0 699 Total Subcatchment S-13: DA-6D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 13 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.700 ac Runoff Volume=0.515 af Runoff Depth>2.29" Flow Length=699' Tc=5.0 min CN=91 11.62 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 12HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-14: DA-6C Runoff = 11.36 cfs @ 11.94 hrs, Volume= 0.479 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.510 91 Newly graded area, HSG C 2.510 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.3 100 0.0170 1.33 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.2 168 0.0220 2.39 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 1.0 318 0.0100 5.05 70.70 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 3.5 586 Total Subcatchment S-14: DA-6C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.510 ac Runoff Volume=0.479 af Runoff Depth>2.29" Flow Length=586' Tc=3.5 min CN=91 11.36 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 13HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-15: DA-6E Runoff = 13.71 cfs @ 11.97 hrs, Volume= 0.620 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 3.250 91 Newly graded area, HSG C 3.250 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.4 100 0.0120 1.16 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.6 224 0.0200 2.28 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 2.6 552 0.0050 3.57 49.99 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 5.6 876 Total Subcatchment S-15: DA-6E Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 14 12 10 8 6 4 2 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=3.250 ac Runoff Volume=0.620 af Runoff Depth>2.29" Flow Length=876' Tc=5.6 min CN=91 13.71 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 14HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-16: DA-6F Runoff = 8.08 cfs @ 11.94 hrs, Volume= 0.340 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.780 91 Newly graded area, HSG C 1.780 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.3 100 0.0170 1.33 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.1 148 0.0210 2.33 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 1.0 289 0.0090 4.79 67.07 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 3.4 537 Total Subcatchment S-16: DA-6F Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=1.780 ac Runoff Volume=0.340 af Runoff Depth>2.29" Flow Length=537' Tc=3.4 min CN=91 8.08 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 15HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-17: DA-6G Runoff = 11.24 cfs @ 11.96 hrs, Volume= 0.498 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.610 91 Newly graded area, HSG C 2.610 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-17: DA-6G Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.610 ac Runoff Volume=0.498 af Runoff Depth>2.29" Tc=5.0 min CN=91 11.24 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 16HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-11: LD-1A Inflow Area = 26.609 ac, 0.00% Impervious, Inflow Depth > 1.73" for 2-Year event Inflow = 59.30 cfs @ 12.01 hrs, Volume= 3.835 af Outflow = 59.09 cfs @ 12.04 hrs, Volume= 3.828 af, Atten= 0%, Lag= 1.3 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 4.46 fps, Min. Travel Time= 1.3 min Avg. Velocity = 1.37 fps, Avg. Travel Time= 4.1 min Peak Storage= 4,442 cf @ 12.04 hrs Average Depth at Peak Storage= 1.33' Bank-Full Depth= 6.00' Flow Area= 144.0 sf, Capacity= 1,495.75 cfs 6.00' x 6.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 42.00' Length= 335.0' Slope= 0.0123 '/' Inlet Invert= 508.00', Outlet Invert= 503.88' Reach R-11: LD-1A Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 65 60 55 50 45 40 35 30 25 20 15 10 5 0 Inflow Area=26.609 ac Avg. Flow Depth=1.33' Max Vel=4.46 fps n=0.035 L=335.0' S=0.0123 '/' Capacity=1,495.75 cfs 59.30 cfs59.09 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 17HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-12: LD-1B Inflow Area = 31.819 ac, 0.00% Impervious, Inflow Depth > 1.82" for 2-Year event Inflow = 76.48 cfs @ 11.98 hrs, Volume= 4.823 af Outflow = 75.96 cfs @ 11.99 hrs, Volume= 4.816 af, Atten= 1%, Lag= 0.9 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 4.83 fps, Min. Travel Time= 1.1 min Avg. Velocity = 1.45 fps, Avg. Travel Time= 3.6 min Peak Storage= 4,907 cf @ 11.99 hrs Average Depth at Peak Storage= 1.50' Bank-Full Depth= 4.00' Flow Area= 72.0 sf, Capacity= 599.39 cfs 6.00' x 4.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 30.00' Length= 312.0' Slope= 0.0127 '/' Inlet Invert= 503.88', Outlet Invert= 499.93' ‡ Reach R-12: LD-1B Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 80 70 60 50 40 30 20 10 0 Inflow Area=31.819 ac Avg. Flow Depth=1.50' Max Vel=4.83 fps n=0.035 L=312.0' S=0.0127 '/' Capacity=599.39 cfs 76.48 cfs75.96 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 18HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-13: LD-1C Inflow Area = 31.819 ac, 0.00% Impervious, Inflow Depth > 1.82" for 2-Year event Inflow = 75.96 cfs @ 11.99 hrs, Volume= 4.816 af Outflow = 75.76 cfs @ 12.00 hrs, Volume= 4.811 af, Atten= 0%, Lag= 0.5 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 4.51 fps, Min. Travel Time= 0.7 min Avg. Velocity = 1.36 fps, Avg. Travel Time= 2.3 min Peak Storage= 3,093 cf @ 12.00 hrs Average Depth at Peak Storage= 1.57' Bank-Full Depth= 4.00' Flow Area= 72.0 sf, Capacity= 545.58 cfs 6.00' x 4.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 30.00' Length= 184.0' Slope= 0.0105 '/' Inlet Invert= 499.93', Outlet Invert= 498.00' ‡ Reach R-13: LD-1C Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 80 70 60 50 40 30 20 10 0 Inflow Area=31.819 ac Avg. Flow Depth=1.57' Max Vel=4.51 fps n=0.035 L=184.0' S=0.0105 '/' Capacity=545.58 cfs 75.96 cfs75.76 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 19HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R01: Lateral Ditch Inflow Area = 6.130 ac, 0.00% Impervious, Inflow Depth > 2.29" for 2-Year event Inflow = 26.01 cfs @ 11.96 hrs, Volume= 1.170 af Outflow = 19.26 cfs @ 12.02 hrs, Volume= 1.160 af, Atten= 26%, Lag= 3.4 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 2.36 fps, Min. Travel Time= 8.3 min Avg. Velocity = 0.84 fps, Avg. Travel Time= 23.4 min Peak Storage= 9,596 cf @ 12.02 hrs Average Depth at Peak Storage= 0.55' Bank-Full Depth= 1.50' Flow Area= 51.0 sf, Capacity= 223.50 cfs 4.00' x 1.50' deep channel, n= 0.035 Side Slope Z-value= 20.0 '/' Top Width= 64.00' Length= 1,177.0' Slope= 0.0144 '/' Inlet Invert= 514.00', Outlet Invert= 497.00' ‡ Reach R01: Lateral Ditch Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 25 20 15 10 5 0 Inflow Area=6.130 ac Avg. Flow Depth=0.55' Max Vel=2.36 fps n=0.035 L=1,177.0' S=0.0144 '/' Capacity=223.50 cfs 26.01 cfs 19.26 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 20HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 1P: 36" Culvert Inflow Area = 22.679 ac, 0.00% Impervious, Inflow Depth > 1.63" for 2-Year event Inflow = 55.79 cfs @ 12.05 hrs, Volume= 3.085 af Outflow = 55.79 cfs @ 12.05 hrs, Volume= 3.085 af, Atten= 0%, Lag= 0.0 min Primary = 55.79 cfs @ 12.05 hrs, Volume= 3.085 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Peak Elev= 514.19' @ 12.05 hrs Flood Elev= 524.00' Device Routing Invert Outlet Devices #1 Primary 510.00'36.0" Round 36" RCP Culvert L= 157.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 510.00' / 508.00' S= 0.0127 '/' Cc= 0.900 n= 0.012, Flow Area= 7.07 sf Primary OutFlow Max=55.76 cfs @ 12.05 hrs HW=514.18' TW=509.33' (Dynamic Tailwater) 1=36" RCP Culvert (Inlet Controls 55.76 cfs @ 7.89 fps) Pond 1P: 36" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 60 55 50 45 40 35 30 25 20 15 10 5 0 Inflow Area=22.679 ac Peak Elev=514.19' 36.0" Round Culvert n=0.012 L=157.0' S=0.0127 '/' 55.79 cfs55.79 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 21HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 6P: Sediment Basin (SB-2) Inflow Area = 39.459 ac, 0.00% Impervious, Inflow Depth > 1.91" for 2-Year event Inflow = 105.30 cfs @ 11.98 hrs, Volume= 6.269 af Outflow = 3.09 cfs @ 15.68 hrs, Volume= 1.451 af, Atten= 97%, Lag= 222.2 min Primary = 3.09 cfs @ 15.68 hrs, Volume= 1.451 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 502.22' @ 15.68 hrs Surf.Area= 3.118 ac Storage= 4.967 af Plug-Flow detention time= 327.3 min calculated for 1.451 af (23% of inflow) Center-of-Mass det. time= 219.6 min ( 997.4 - 777.8 ) Volume Invert Avail.Storage Storage Description #1 499.50' 63.755 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.620 0.000 0.000 502.00 2.840 4.325 4.325 504.00 5.420 8.260 12.585 506.00 7.640 13.060 25.645 508.00 9.500 17.140 42.785 510.00 11.470 20.970 63.755 Device Routing Invert Outlet Devices #1 Primary 499.50'24.0" Round Culvert L= 103.0' CMP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 498.00' S= 0.0146 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 3.14 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=3.09 cfs @ 15.68 hrs HW=502.22' (Free Discharge) 1=Culvert (Passes 3.09 cfs of 19.81 cfs potential flow) 2=Orifice/Grate (Weir Controls 3.09 cfs @ 1.52 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 22HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 6P: Sediment Basin (SB-2) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 110 100 90 80 70 60 50 40 30 20 10 0 Inflow Area=39.459 ac Peak Elev=502.22' Storage=4.967 af 105.30 cfs 3.09 cfs3.09 cfs0.00 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 23HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 49P: Sediment Basin 1 Inflow Area = 11.140 ac, 0.00% Impervious, Inflow Depth > 2.28" for 2-Year event Inflow = 38.41 cfs @ 11.97 hrs, Volume= 2.116 af Outflow = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af, Atten= 100%, Lag= 0.0 min Primary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Peak Elev= 501.38' @ 20.00 hrs Surf.Area= 1.712 ac Storage= 2.115 af Plug-Flow detention time= (not calculated: initial storage exceeds outflow) Center-of-Mass det. time= (not calculated: no outflow) Volume Invert Avail.Storage Storage Description #1 499.50' 41.530 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.540 0.000 0.000 502.00 2.100 3.300 3.300 504.00 3.600 5.700 9.000 506.00 4.990 8.590 17.590 508.00 5.990 10.980 28.570 510.00 6.970 12.960 41.530 Device Routing Invert Outlet Devices #1 Primary 499.50'12.0" Round Culvert L= 116.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 497.00' S= 0.0216 '/' Cc= 0.900 n= 0.025, Flow Area= 0.79 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 1=Culvert ( Controls 0.00 cfs) 2=Orifice/Grate ( Controls 0.00 cfs) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 24HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 49P: Sediment Basin 1 Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 40 35 30 25 20 15 10 5 0 Inflow Area=11.140 ac Peak Elev=501.38' Storage=2.115 af 38.41 cfs 0.00 cfs0.00 cfs0.00 cfs 2 DA-2 3 DA4 4 DA-3 9S DA-8A-1A 10S DA-8A-1B 12S DA-8A-1C 13S DA-8A-1D 14S DA-8A-1E 15S DA-8A-1F 38S DA-8A-1G S-21 DA-7A S-22 DA-7B S-23 DA-7C S-24 DA-7D S-25 DA-7E S-26 DA-7F S-27 DA-7G S-41 DA-8A S-42 DA-8B S-43 DA-8DS-45 DA-8C 6R LD-4B R-21 LD-2A R-22 LD-2B R-23 LD-2C R-41 LD-4A 2PCB 24" Culvert 3P 36" Slope Drain Pipe 4PCB 36" Slope Drain Pipe 8P Sediment Basin (SB-3) 16PCB 18" Culvert 17PCB 18" Culvert 18PCB 18" Culvert 37P Sediment Basin (SB-4) Routing Diagram for ST 2 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points x 3 Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Runoff Area=6.060 ac 0.00% Impervious Runoff Depth>1.05"Subcatchment 2: DA-2 Flow Length=852' Tc=17.0 min CN=74 Runoff=8.34 cfs 0.532 af Runoff Area=74.120 ac 0.00% Impervious Runoff Depth>1.29"Subcatchment 3: DA4 Flow Length=4,921' Tc=22.0 min CN=78 Runoff=109.23 cfs 7.962 af Runoff Area=2.385 ac 0.00% Impervious Runoff Depth>1.00"Subcatchment 4: DA-3 Flow Length=765' Tc=16.9 min CN=73 Runoff=3.10 cfs 0.199 af Runoff Area=0.620 ac 0.00% Impervious Runoff Depth>1.06"Subcatchment 9S: DA-8A-1A Tc=6.0 min CN=74 Runoff=1.29 cfs 0.055 af Runoff Area=0.750 ac 0.00% Impervious Runoff Depth>1.06"Subcatchment 10S: DA-8A-1B Tc=6.0 min CN=74 Runoff=1.57 cfs 0.066 af Runoff Area=0.130 ac 0.00% Impervious Runoff Depth>1.06"Subcatchment 12S: DA-8A-1C Tc=6.0 min CN=74 Runoff=0.27 cfs 0.011 af Runoff Area=1.240 ac 0.00% Impervious Runoff Depth>1.06"Subcatchment 13S: DA-8A-1D Flow Length=676' Tc=12.7 min CN=74 Runoff=1.99 cfs 0.109 af Runoff Area=0.290 ac 0.00% Impervious Runoff Depth>1.06"Subcatchment 14S: DA-8A-1E Tc=0.0 min CN=74 Runoff=0.75 cfs 0.026 af Runoff Area=0.170 ac 0.00% Impervious Runoff Depth>1.06"Subcatchment 15S: DA-8A-1F Tc=6.0 min CN=74 Runoff=0.35 cfs 0.015 af Runoff Area=0.350 ac 0.00% Impervious Runoff Depth>1.06"Subcatchment 38S: DA-8A-1G Tc=6.0 min CN=74 Runoff=0.73 cfs 0.031 af Runoff Area=4.700 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-21: DA-7A Flow Length=879' Tc=6.1 min CN=91 Runoff=19.49 cfs 0.897 af Runoff Area=1.700 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-22: DA-7B Tc=5.0 min CN=91 Runoff=7.32 cfs 0.324 af Runoff Area=2.480 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-23: DA-7C Flow Length=571' Tc=3.9 min CN=91 Runoff=11.08 cfs 0.473 af Runoff Area=2.650 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-24: DA-7D Flow Length=618' Tc=4.3 min CN=91 Runoff=11.68 cfs 0.506 af Runoff Area=1.640 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-25: DA-7E Flow Length=528' Tc=3.3 min CN=91 Runoff=7.47 cfs 0.313 af Runoff Area=3.000 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-26: DA-7F Flow Length=1,030' Tc=8.4 min CN=91 Runoff=11.51 cfs 0.572 af Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Runoff Area=2.260 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-27: DA-7G Tc=5.0 min CN=91 Runoff=9.73 cfs 0.431 af Runoff Area=4.740 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-41: DA-8A Flow Length=1,457' Tc=7.1 min CN=91 Runoff=19.01 cfs 0.904 af Runoff Area=2.890 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-42: DA-8B Flow Length=916' Tc=6.4 min CN=91 Runoff=11.87 cfs 0.551 af Runoff Area=1.770 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-43: DA-8D Tc=5.0 min CN=91 Runoff=7.62 cfs 0.338 af Runoff Area=1.480 ac 0.00% Impervious Runoff Depth>2.29"Subcatchment S-45: DA-8C Flow Length=725' Tc=6.0 min CN=91 Runoff=6.16 cfs 0.282 af Inflow=26.98 cfs 1.948 afReach 6R: LD-4B Outflow=26.98 cfs 1.948 af Avg. Flow Depth=1.36' Max Vel=5.15 fps Inflow=71.30 cfs 9.706 afReach R-21: LD-2A n=0.033 L=282.0' S=0.0143 '/' Capacity=674.58 cfs Outflow=70.67 cfs 9.696 af Avg. Flow Depth=1.44' Max Vel=5.30 fps Inflow=79.03 cfs 10.675 afReach R-22: LD-2B n=0.033 L=306.0' S=0.0142 '/' Capacity=357.35 cfs Outflow=78.65 cfs 10.663 af Avg. Flow Depth=1.28' Max Vel=6.21 fps Inflow=78.65 cfs 10.663 afReach R-23: LD-2C n=0.033 L=165.0' S=0.0221 '/' Capacity=445.67 cfs Outflow=78.57 cfs 10.658 af Avg. Flow Depth=0.53' Max Vel=2.06 fps Inflow=26.90 cfs 1.416 afReach R-41: LD-4A n=0.035 L=1,410.0' S=0.0106 '/' Capacity=77.78 cfs Outflow=18.21 cfs 1.397 af Peak Elev=513.30' Inflow=8.34 cfs 0.532 afPond 2P: 24" Culvert 24.0" Round Culvert n=0.012 L=167.0' S=0.0240 '/' Outflow=8.34 cfs 0.532 af Peak Elev=536.50' Storage=59,457 cf Inflow=109.23 cfs 7.962 afPond 3P: 36" Slope Drain Pipe Outflow=58.01 cfs 7.953 af Peak Elev=529.59' Inflow=3.10 cfs 0.199 afPond 4P: 36" Slope Drain Pipe 36.0" Round Culvert n=0.013 L=150.0' S=0.1263 '/' Outflow=3.10 cfs 0.199 af Peak Elev=502.72' Storage=7.175 af Inflow=103.10 cfs 11.974 afPond 8P: Sediment Basin (SB-3) Primary=21.79 cfs 6.427 af Secondary=0.00 cfs 0.000 af Outflow=21.79 cfs 6.427 af Peak Elev=526.20' Inflow=2.86 cfs 0.121 afPond 16P: 18" Culvert Outflow=2.86 cfs 0.121 af Peak Elev=528.16' Inflow=2.16 cfs 0.121 afPond 17P: 18" Culvert Outflow=2.16 cfs 0.121 af Peak Elev=528.10' Inflow=0.98 cfs 0.041 afPond 18P: 18" Culvert Outflow=0.98 cfs 0.041 af Peak Elev=502.03' Storage=2.466 af Inflow=39.32 cfs 2.568 afPond 37P: Sediment Basin (SB-4) Primary=0.72 cfs 0.102 af Secondary=0.00 cfs 0.000 af Outflow=0.72 cfs 0.102 af Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Total Runoff Area = 115.425 ac Runoff Volume = 14.598 af Average Runoff Depth = 1.52" 100.00% Pervious = 115.425 ac 0.00% Impervious = 0.000 ac Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 5HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 2: DA-2 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 8.34 cfs @ 12.11 hrs, Volume= 0.532 af, Depth> 1.05" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.555 73 Woods, Fair, HSG C 0.140 96 Gravel surface, HSG C 4.365 74 >75% Grass cover, Good, HSG C 6.060 74 Weighted Average 6.060 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.6 100 0.0500 0.25 Sheet Flow, TC for DA2 Grass: Short n= 0.150 P2= 3.40" 10.4 752 0.0580 1.20 Shallow Concentrated Flow, TC for DA2 Woodland Kv= 5.0 fps 17.0 852 Total Subcatchment 2: DA-2 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=6.060 ac Runoff Volume=0.532 af Runoff Depth>1.05" Flow Length=852' Tc=17.0 min CN=74 8.34 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 6HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 3: DA4 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 109.23 cfs @ 12.15 hrs, Volume= 7.962 af, Depth> 1.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 9.930 73 Woods, Fair, HSG C 15.051 96 Gravel surface, HSG C 49.139 74 >75% Grass cover, Good, HSG C 74.120 78 Weighted Average 74.120 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.6 100 0.0740 0.30 Sheet Flow, TC for DA4 Grass: Short n= 0.150 P2= 3.40" 13.1 2,834 0.0580 3.61 Shallow Concentrated Flow, TC for DA4 Grassed Waterway Kv= 15.0 fps 3.3 1,987 10.00 Direct Entry, TC for DA4 22.0 4,921 Total Subcatchment 3: DA4 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 120 110 100 90 80 70 60 50 40 30 20 10 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=74.120 ac Runoff Volume=7.962 af Runoff Depth>1.29" Flow Length=4,921' Tc=22.0 min CN=78 109.23 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 7HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 4: DA-3 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 3.10 cfs @ 12.11 hrs, Volume= 0.199 af, Depth> 1.00" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.260 73 Woods, Fair, HSG C 0.000 96 Gravel surface, HSG C 1.125 74 >75% Grass cover, Good, HSG C 2.385 73 Weighted Average 2.385 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 9.9 100 0.0180 0.17 Sheet Flow, TC for DA3 Grass: Short n= 0.150 P2= 3.40" 7.0 665 0.0511 1.58 Shallow Concentrated Flow, TC for DA3 Short Grass Pasture Kv= 7.0 fps 16.9 765 Total Subcatchment 4: DA-3 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.385 ac Runoff Volume=0.199 af Runoff Depth>1.00" Flow Length=765' Tc=16.9 min CN=73 3.10 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 8HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 9S: DA-8A-1A Runoff = 1.29 cfs @ 11.98 hrs, Volume= 0.055 af, Depth> 1.06" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description * 0.620 74 0.620 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 9S: DA-8A-1A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=0.620 ac Runoff Volume=0.055 af Runoff Depth>1.06" Tc=6.0 min CN=74 1.29 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 9HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 10S: DA-8A-1B Runoff = 1.57 cfs @ 11.98 hrs, Volume= 0.066 af, Depth> 1.06" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description * 0.750 74 0.750 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 10S: DA-8A-1B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=0.750 ac Runoff Volume=0.066 af Runoff Depth>1.06" Tc=6.0 min CN=74 1.57 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 10HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 12S: DA-8A-1C Runoff = 0.27 cfs @ 11.98 hrs, Volume= 0.011 af, Depth> 1.06" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description * 0.130 74 0.130 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 12S: DA-8A-1C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 0.3 0.25 0.2 0.15 0.1 0.05 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=0.130 ac Runoff Volume=0.011 af Runoff Depth>1.06" Tc=6.0 min CN=74 0.27 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 11HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 13S: DA-8A-1D Runoff = 1.99 cfs @ 12.06 hrs, Volume= 0.109 af, Depth> 1.06" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description * 1.240 74 1.240 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 3.8 100 0.2000 0.44 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 8.9 576 0.0240 1.08 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 12.7 676 Total Subcatchment 13S: DA-8A-1D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=1.240 ac Runoff Volume=0.109 af Runoff Depth>1.06" Flow Length=676' Tc=12.7 min CN=74 1.99 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 12HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 14S: DA-8A-1E Runoff = 0.75 cfs @ 11.90 hrs, Volume= 0.026 af, Depth> 1.06" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description * 0.290 74 0.290 100.00% Pervious Area Subcatchment 14S: DA-8A-1E Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 0.8 0.7 0.6 0.5 0.4 0.3 0.2 0.1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=0.290 ac Runoff Volume=0.026 af Runoff Depth>1.06" Tc=0.0 min CN=74 0.75 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 13HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 15S: DA-8A-1F Runoff = 0.35 cfs @ 11.98 hrs, Volume= 0.015 af, Depth> 1.06" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description * 0.170 74 0.170 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 15S: DA-8A-1F Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 0.35 0.3 0.25 0.2 0.15 0.1 0.05 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=0.170 ac Runoff Volume=0.015 af Runoff Depth>1.06" Tc=6.0 min CN=74 0.35 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 14HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 38S: DA-8A-1G Runoff = 0.73 cfs @ 11.98 hrs, Volume= 0.031 af, Depth> 1.06" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description * 0.350 74 0.350 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 38S: DA-8A-1G Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 0.8 0.7 0.6 0.5 0.4 0.3 0.2 0.1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=0.350 ac Runoff Volume=0.031 af Runoff Depth>1.06" Tc=6.0 min CN=74 0.73 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 15HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-21: DA-7A Runoff = 19.49 cfs @ 11.97 hrs, Volume= 0.897 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 4.700 91 Newly graded area, HSG C 4.700 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 0.6 100 0.0880 2.56 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 4.8 534 0.0130 1.84 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 0.7 245 0.0186 5.90 82.65 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 6.1 879 Total Subcatchment S-21: DA-7A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 20 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=4.700 ac Runoff Volume=0.897 af Runoff Depth>2.29" Flow Length=879' Tc=6.1 min CN=91 19.49 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 16HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-22: DA-7B Runoff = 7.32 cfs @ 11.96 hrs, Volume= 0.324 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.700 91 Newly graded area, HSG C 1.700 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-22: DA-7B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=1.700 ac Runoff Volume=0.324 af Runoff Depth>2.29" Tc=5.0 min CN=91 7.32 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 17HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-23: DA-7C Runoff = 11.08 cfs @ 11.95 hrs, Volume= 0.473 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.480 91 Newly graded area, HSG C 2.480 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.4 100 0.0140 1.23 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.5 226 0.0242 2.50 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 1.0 245 0.0090 4.11 57.49 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 3.9 571 Total Subcatchment S-23: DA-7C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.480 ac Runoff Volume=0.473 af Runoff Depth>2.29" Flow Length=571' Tc=3.9 min CN=91 11.08 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 18HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-24: DA-7D Runoff = 11.68 cfs @ 11.95 hrs, Volume= 0.506 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.650 91 Newly graded area, HSG C 2.650 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.4 100 0.0140 1.23 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 2.2 277 0.0170 2.10 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 0.7 241 0.0167 5.59 78.31 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 4.3 618 Total Subcatchment S-24: DA-7D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 13 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.650 ac Runoff Volume=0.506 af Runoff Depth>2.29" Flow Length=618' Tc=4.3 min CN=91 11.68 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 19HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-25: DA-7E Runoff = 7.47 cfs @ 11.94 hrs, Volume= 0.313 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.640 91 Newly graded area, HSG C 1.640 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.2 100 0.0181 1.36 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.0 139 0.0213 2.35 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 1.1 289 0.0070 4.23 59.15 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 3.3 528 Total Subcatchment S-25: DA-7E Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=1.640 ac Runoff Volume=0.313 af Runoff Depth>2.29" Flow Length=528' Tc=3.3 min CN=91 7.47 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 20HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-26: DA-7F Runoff = 11.51 cfs @ 12.00 hrs, Volume= 0.572 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 3.000 91 Newly graded area, HSG C 3.000 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.3 100 0.0166 1.32 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 5.8 498 0.0080 1.44 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 1.3 432 0.0122 5.58 78.09 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.030 8.4 1,030 Total Subcatchment S-26: DA-7F Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=3.000 ac Runoff Volume=0.572 af Runoff Depth>2.29" Flow Length=1,030' Tc=8.4 min CN=91 11.51 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 21HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-27: DA-7G Runoff = 9.73 cfs @ 11.96 hrs, Volume= 0.431 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.260 91 Newly graded area, HSG C 2.260 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-27: DA-7G Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.260 ac Runoff Volume=0.431 af Runoff Depth>2.29" Tc=5.0 min CN=91 9.73 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 22HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-41: DA-8A Runoff = 19.01 cfs @ 11.98 hrs, Volume= 0.904 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 4.740 91 Newly graded area, HSG C 4.740 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.6 100 0.0100 1.07 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 3.2 695 0.0520 3.67 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 2.3 662 0.0118 4.70 65.83 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 7.1 1,457 Total Subcatchment S-41: DA-8A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 20 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=4.740 ac Runoff Volume=0.904 af Runoff Depth>2.29" Flow Length=1,457' Tc=7.1 min CN=91 19.01 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 23HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-42: DA-8B Runoff = 11.87 cfs @ 11.97 hrs, Volume= 0.551 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 2.890 91 Newly graded area, HSG C 2.890 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.5 100 0.0104 1.09 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 1.8 252 0.0204 2.30 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 3.1 564 0.0050 3.06 42.85 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 6.4 916 Total Subcatchment S-42: DA-8B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 13 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=2.890 ac Runoff Volume=0.551 af Runoff Depth>2.29" Flow Length=916' Tc=6.4 min CN=91 11.87 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 24HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-43: DA-8D Runoff = 7.62 cfs @ 11.96 hrs, Volume= 0.338 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.770 91 Newly graded area, HSG C 1.770 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-43: DA-8D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 8 7 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=1.770 ac Runoff Volume=0.338 af Runoff Depth>2.29" Tc=5.0 min CN=91 7.62 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 25HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-45: DA-8C Runoff = 6.16 cfs @ 11.97 hrs, Volume= 0.282 af, Depth> 2.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 2-Year Rainfall=3.40" Area (ac) CN Description 1.480 91 Newly graded area, HSG C 1.480 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 1.4 100 0.0120 1.16 Sheet Flow, Smooth surfaces n= 0.011 P2= 3.40" 2.9 320 0.0130 1.84 Shallow Concentrated Flow, Unpaved Kv= 16.1 fps 1.7 305 0.0050 3.06 42.85 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 6.0 725 Total Subcatchment S-45: DA-8C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 6 5 4 3 2 1 0 Type II 24-hr 2-Year Rainfall=3.40" Runoff Area=1.480 ac Runoff Volume=0.282 af Runoff Depth>2.29" Flow Length=725' Tc=6.0 min CN=91 6.16 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 26HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach 6R: LD-4B Inflow Area = 13.565 ac, 0.00% Impervious, Inflow Depth > 1.72" for 2-Year event Inflow = 26.98 cfs @ 12.01 hrs, Volume= 1.948 af Outflow = 26.98 cfs @ 12.01 hrs, Volume= 1.948 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Reach 6R: LD-4B Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 30 25 20 15 10 5 0 Inflow Area=13.565 ac 26.98 cfs26.98 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 27HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-21: LD-2A Inflow Area = 86.580 ac, 0.00% Impervious, Inflow Depth > 1.35" for 2-Year event Inflow = 71.30 cfs @ 12.08 hrs, Volume= 9.706 af Outflow = 70.67 cfs @ 12.09 hrs, Volume= 9.696 af, Atten= 1%, Lag= 0.7 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Max. Velocity= 5.15 fps, Min. Travel Time= 0.9 min Avg. Velocity = 1.92 fps, Avg. Travel Time= 2.5 min Peak Storage= 3,866 cf @ 12.09 hrs Average Depth at Peak Storage= 1.36' Bank-Full Depth= 4.00' Flow Area= 72.0 sf, Capacity= 674.58 cfs 6.00' x 4.00' deep channel, n= 0.033 Side Slope Z-value= 3.0 '/' Top Width= 30.00' Length= 282.0' Slope= 0.0143 '/' Inlet Invert= 510.00', Outlet Invert= 505.98' ‡ Reach R-21: LD-2A Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 70 60 50 40 30 20 10 0 Inflow Area=86.580 ac Avg. Flow Depth=1.36' Max Vel=5.15 fps n=0.033 L=282.0' S=0.0143 '/' Capacity=674.58 cfs 71.30 cfs70.67 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 28HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-22: LD-2B Inflow Area = 91.710 ac, 0.00% Impervious, Inflow Depth > 1.40" for 2-Year event Inflow = 79.03 cfs @ 11.99 hrs, Volume= 10.675 af Outflow = 78.65 cfs @ 12.00 hrs, Volume= 10.663 af, Atten= 0%, Lag= 0.8 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Max. Velocity= 5.30 fps, Min. Travel Time= 1.0 min Avg. Velocity = 1.99 fps, Avg. Travel Time= 2.6 min Peak Storage= 4,540 cf @ 12.00 hrs Average Depth at Peak Storage= 1.44' Bank-Full Depth= 3.00' Flow Area= 45.0 sf, Capacity= 357.35 cfs 6.00' x 3.00' deep channel, n= 0.033 Side Slope Z-value= 3.0 '/' Top Width= 24.00' Length= 306.0' Slope= 0.0142 '/' Inlet Invert= 505.98', Outlet Invert= 501.64' ‡ Reach R-22: LD-2B Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 80 70 60 50 40 30 20 10 0 Inflow Area=91.710 ac Avg. Flow Depth=1.44' Max Vel=5.30 fps n=0.033 L=306.0' S=0.0142 '/' Capacity=357.35 cfs 79.03 cfs78.65 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 29HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-23: LD-2C Inflow Area = 91.710 ac, 0.00% Impervious, Inflow Depth > 1.40" for 2-Year event Inflow = 78.65 cfs @ 12.00 hrs, Volume= 10.663 af Outflow = 78.57 cfs @ 12.01 hrs, Volume= 10.658 af, Atten= 0%, Lag= 0.3 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Max. Velocity= 6.21 fps, Min. Travel Time= 0.4 min Avg. Velocity = 2.31 fps, Avg. Travel Time= 1.2 min Peak Storage= 2,086 cf @ 12.01 hrs Average Depth at Peak Storage= 1.28' Bank-Full Depth= 3.00' Flow Area= 45.0 sf, Capacity= 445.67 cfs 6.00' x 3.00' deep channel, n= 0.033 Side Slope Z-value= 3.0 '/' Top Width= 24.00' Length= 165.0' Slope= 0.0221 '/' Inlet Invert= 501.64', Outlet Invert= 498.00' ‡ Reach R-23: LD-2C Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 80 70 60 50 40 30 20 10 0 Inflow Area=91.710 ac Avg. Flow Depth=1.28' Max Vel=6.21 fps n=0.033 L=165.0' S=0.0221 '/' Capacity=445.67 cfs 78.65 cfs78.57 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 30HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-41: LD-4A Inflow Area = 10.675 ac, 0.00% Impervious, Inflow Depth > 1.59" for 2-Year event Inflow = 26.90 cfs @ 11.99 hrs, Volume= 1.416 af Outflow = 18.21 cfs @ 12.07 hrs, Volume= 1.397 af, Atten= 32%, Lag= 4.8 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Max. Velocity= 2.06 fps, Min. Travel Time= 11.4 min Avg. Velocity = 0.73 fps, Avg. Travel Time= 32.0 min Peak Storage= 12,440 cf @ 12.07 hrs Average Depth at Peak Storage= 0.53' Bank-Full Depth= 1.00' Flow Area= 26.0 sf, Capacity= 77.78 cfs 6.00' x 1.00' deep channel, n= 0.035 Side Slope Z-value= 20.0 '/' Top Width= 46.00' Length= 1,410.0' Slope= 0.0106 '/' Inlet Invert= 512.00', Outlet Invert= 497.00' ‡ Reach R-41: LD-4A Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 30 25 20 15 10 5 0 Inflow Area=10.675 ac Avg. Flow Depth=0.53' Max Vel=2.06 fps n=0.035 L=1,410.0' S=0.0106 '/' Capacity=77.78 cfs 26.90 cfs 18.21 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 31HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 2P: 24" Culvert Inflow Area = 6.060 ac, 0.00% Impervious, Inflow Depth > 1.05" for 2-Year event Inflow = 8.34 cfs @ 12.11 hrs, Volume= 0.532 af Outflow = 8.34 cfs @ 12.11 hrs, Volume= 0.532 af, Atten= 0%, Lag= 0.0 min Primary = 8.34 cfs @ 12.11 hrs, Volume= 0.532 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 513.30' @ 12.11 hrs Flood Elev= 528.00' Device Routing Invert Outlet Devices #1 Primary 512.00'24.0" Round Culvert L= 167.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 512.00' / 508.00' S= 0.0240 '/' Cc= 0.900 n= 0.012, Flow Area= 3.14 sf Primary OutFlow Max=8.33 cfs @ 12.11 hrs HW=513.29' TW=511.36' (Dynamic Tailwater) 1=Culvert (Inlet Controls 8.33 cfs @ 3.87 fps) Pond 2P: 24" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 9 8 7 6 5 4 3 2 1 0 Inflow Area=6.060 ac Peak Elev=513.30' 24.0" Round Culvert n=0.012 L=167.0' S=0.0240 '/' 8.34 cfs8.34 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 32HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 3P: 36" Slope Drain Pipe Inflow Area = 74.120 ac, 0.00% Impervious, Inflow Depth > 1.29" for 2-Year event Inflow = 109.23 cfs @ 12.15 hrs, Volume= 7.962 af Outflow = 58.01 cfs @ 12.37 hrs, Volume= 7.953 af, Atten= 47%, Lag= 13.4 min Primary = 58.01 cfs @ 12.37 hrs, Volume= 7.953 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 536.50' @ 12.37 hrs Surf.Area= 64,287 sf Storage= 59,457 cf Plug-Flow detention time= 8.0 min calculated for 7.953 af (100% of inflow) Center-of-Mass det. time= 7.5 min ( 816.6 - 809.1 ) Volume Invert Avail.Storage Storage Description #1 535.00' 2,237,064 cf Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (sq-ft) (cubic-feet) (cubic-feet) 535.00 0 0 0 536.00 58,048 29,024 29,024 541.00 120,747 446,988 476,012 546.00 174,399 737,865 1,213,877 551.00 234,876 1,023,188 2,237,064 Device Routing Invert Outlet Devices #1 Primary 528.50'36.0" Round Culvert L= 207.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 528.50' / 510.00' S= 0.0894 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 7.07 sf #2 Device 1 530.00'36.0" Round Culvert L= 530.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 530.00' / 528.50' S= 0.0028 '/' Cc= 0.900 n= 0.012 Concrete pipe, finished, Flow Area= 7.07 sf #3 Device 2 535.00'60.0" x 60.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=58.01 cfs @ 12.37 hrs HW=536.50' TW=511.29' (Dynamic Tailwater) 1=Culvert (Passes 58.01 cfs of 86.76 cfs potential flow) 2=Culvert (Barrel Controls 58.01 cfs @ 8.21 fps) 3=Orifice/Grate (Passes 58.01 cfs of 119.83 cfs potential flow) Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 33HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 3P: 36" Slope Drain Pipe Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 120 110 100 90 80 70 60 50 40 30 20 10 0 Inflow Area=74.120 ac Peak Elev=536.50' Storage=59,457 cf 109.23 cfs 58.01 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 34HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 4P: 36" Slope Drain Pipe Inflow Area = 2.385 ac, 0.00% Impervious, Inflow Depth > 1.00" for 2-Year event Inflow = 3.10 cfs @ 12.11 hrs, Volume= 0.199 af Outflow = 3.10 cfs @ 12.11 hrs, Volume= 0.199 af, Atten= 0%, Lag= 0.0 min Primary = 3.10 cfs @ 12.11 hrs, Volume= 0.199 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 529.59' @ 12.11 hrs Flood Elev= 532.00' Device Routing Invert Outlet Devices #1 Primary 528.94'36.0" Round Culvert L= 150.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 528.94' / 510.00' S= 0.1263 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 7.07 sf Primary OutFlow Max=3.10 cfs @ 12.11 hrs HW=529.59' TW=512.52' (Dynamic Tailwater) 1=Culvert (Inlet Controls 3.10 cfs @ 2.75 fps) Pond 4P: 36" Slope Drain Pipe Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 3 2 1 0 Inflow Area=2.385 ac Peak Elev=529.59' 36.0" Round Culvert n=0.013 L=150.0' S=0.1263 '/' 3.10 cfs3.10 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 35HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 8P: Sediment Basin (SB-3) Inflow Area = 98.610 ac, 0.00% Impervious, Inflow Depth > 1.46" for 2-Year event Inflow = 103.10 cfs @ 11.99 hrs, Volume= 11.974 af Outflow = 21.79 cfs @ 13.14 hrs, Volume= 6.427 af, Atten= 79%, Lag= 69.2 min Primary = 21.79 cfs @ 13.14 hrs, Volume= 6.427 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 502.72' @ 13.14 hrs Surf.Area= 3.796 ac Storage= 7.175 af Plug-Flow detention time= 196.6 min calculated for 6.424 af (54% of inflow) Center-of-Mass det. time= 115.7 min ( 918.0 - 802.3 ) Volume Invert Avail.Storage Storage Description #1 499.50' 61.472 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.870 0.000 0.000 502.00 2.940 4.762 4.762 504.00 5.330 8.270 13.032 506.00 7.160 12.490 25.522 508.00 8.940 16.100 41.622 510.00 10.910 19.850 61.472 Device Routing Invert Outlet Devices #1 Primary 499.50'30.0" Round Culvert L= 91.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 496.00' S= 0.0385 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 4.91 sf #2 Device 1 502.00'42.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=21.79 cfs @ 13.14 hrs HW=502.72' (Free Discharge) 1=Culvert (Passes 21.79 cfs of 33.14 cfs potential flow) 2=Orifice/Grate (Weir Controls 21.79 cfs @ 2.77 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 36HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 8P: Sediment Basin (SB-3) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 110 100 90 80 70 60 50 40 30 20 10 0 Inflow Area=98.610 ac Peak Elev=502.72' Storage=7.175 af 103.10 cfs 21.79 cfs21.79 cfs 0.00 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 37HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 16P: 18" Culvert Inflow Area = 1.370 ac, 0.00% Impervious, Inflow Depth > 1.06" for 2-Year event Inflow = 2.86 cfs @ 11.98 hrs, Volume= 0.121 af Outflow = 2.86 cfs @ 11.98 hrs, Volume= 0.121 af, Atten= 0%, Lag= 0.0 min Primary = 2.86 cfs @ 11.98 hrs, Volume= 0.121 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 526.20' @ 11.98 hrs Flood Elev= 528.00' Device Routing Invert Outlet Devices #1 Primary 524.00'18.0" Round Culvert L= 100.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 524.00' / 510.00' S= 0.1400 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 1.77 sf #2 Device 1 526.00'24.0" x 36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Device 2 526.00'1.2" x 16.5" Horiz. Orifice/Grate X 2.00 columns X 8 rows C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=2.86 cfs @ 11.98 hrs HW=526.20' TW=512.47' (Dynamic Tailwater) 1=Culvert (Passes 2.86 cfs of 10.23 cfs potential flow) 2=Orifice/Grate (Weir Controls 2.86 cfs @ 1.45 fps) 3=Orifice/Grate (Passes 2.86 cfs of 4.70 cfs potential flow) Pond 16P: 18" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 3 2 1 0 Inflow Area=1.370 ac Peak Elev=526.20' 2.86 cfs2.86 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 38HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 17P: 18" Culvert Inflow Area = 1.370 ac, 0.00% Impervious, Inflow Depth > 1.06" for 2-Year event Inflow = 2.16 cfs @ 12.04 hrs, Volume= 0.121 af Outflow = 2.16 cfs @ 12.04 hrs, Volume= 0.121 af, Atten= 0%, Lag= 0.0 min Primary = 2.16 cfs @ 12.04 hrs, Volume= 0.121 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 528.16' @ 12.04 hrs Flood Elev= 530.00' Device Routing Invert Outlet Devices #1 Device 2 528.00'24.0" x 36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #2 Primary 526.00'18.0" Round Culvert L= 70.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 526.00' / 512.00' S= 0.2000 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 1.77 sf #3 Device 1 528.00'1.2" x 16.5" Horiz. Orifice/Grate X 2.00 columns X 8 rows C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=2.16 cfs @ 12.04 hrs HW=528.16' TW=512.53' (Dynamic Tailwater) 2=Culvert (Passes 2.16 cfs of 10.11 cfs potential flow) 1=Orifice/Grate (Weir Controls 2.16 cfs @ 1.32 fps) 3=Orifice/Grate (Passes 2.16 cfs of 4.28 cfs potential flow) Pond 17P: 18" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 2 1 0 Inflow Area=1.370 ac Peak Elev=528.16' 2.16 cfs2.16 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 39HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 18P: 18" Culvert Inflow Area = 0.460 ac, 0.00% Impervious, Inflow Depth > 1.06" for 2-Year event Inflow = 0.98 cfs @ 11.90 hrs, Volume= 0.041 af Outflow = 0.98 cfs @ 11.90 hrs, Volume= 0.041 af, Atten= 0%, Lag= 0.0 min Primary = 0.98 cfs @ 11.90 hrs, Volume= 0.041 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 528.10' @ 11.90 hrs Flood Elev= 530.00' Device Routing Invert Outlet Devices #1 Device 2 528.00'24.0" x 36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #2 Primary 526.00'18.0" Round Culvert L= 70.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 526.00' / 510.00' S= 0.2286 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 1.77 sf #3 Device 1 528.00'1.2" x 16.5" Horiz. Orifice/Grate X 2.00 columns X 8 rows C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=0.97 cfs @ 11.90 hrs HW=528.10' TW=512.36' (Dynamic Tailwater) 2=Culvert (Passes 0.97 cfs of 9.87 cfs potential flow) 1=Orifice/Grate (Weir Controls 0.97 cfs @ 1.01 fps) 3=Orifice/Grate (Passes 0.97 cfs of 3.28 cfs potential flow) Pond 18P: 18" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 1 0 Inflow Area=0.460 ac Peak Elev=528.10' 0.98 cfs0.98 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 40HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 37P: Sediment Basin (SB-4) Inflow Area = 16.815 ac, 0.00% Impervious, Inflow Depth > 1.83" for 2-Year event Inflow = 39.32 cfs @ 11.99 hrs, Volume= 2.568 af Outflow = 0.72 cfs @ 19.56 hrs, Volume= 0.102 af, Atten= 98%, Lag= 454.2 min Primary = 0.72 cfs @ 19.56 hrs, Volume= 0.102 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 502.03' @ 19.56 hrs Surf.Area= 1.584 ac Storage= 2.466 af Plug-Flow detention time= 621.4 min calculated for 0.102 af (4% of inflow) Center-of-Mass det. time= 367.0 min ( 1,145.9 - 778.9 ) Volume Invert Avail.Storage Storage Description #1 499.50' 37.962 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.370 0.000 0.000 502.00 1.560 2.413 2.413 504.00 2.950 4.510 6.923 506.00 4.390 7.340 14.262 508.00 6.010 10.400 24.662 510.00 7.290 13.300 37.962 Device Routing Invert Outlet Devices #1 Primary 498.00'36.0" Round Culvert L= 150.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 498.00' / 495.00' S= 0.0200 '/' Cc= 0.900 n= 0.012 Concrete pipe, finished, Flow Area= 7.07 sf #2 Device 1 502.00'104.0" x 104.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=0.72 cfs @ 19.56 hrs HW=502.03' (Free Discharge) 1=Culvert (Passes 0.72 cfs of 54.18 cfs potential flow) 2=Orifice/Grate (Weir Controls 0.72 cfs @ 0.61 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 41HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 37P: Sediment Basin (SB-4) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 40 35 30 25 20 15 10 5 0 Inflow Area=16.815 ac Peak Elev=502.03' Storage=2.466 af 39.32 cfs 0.72 cfs0.72 cfs0.00 cfs REFERENCE 3 North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. Appendices This section addresses the design of stable conveyance channels and diversions using flexible linings. A stable channel is defined as a channel which is nonsilting and nonscouring. To minimize silting in the channel, flow velocities should remain constant or increase slightly throughout the channel length. This is especially important in designing diversion channels and can be accomplished by adjusting channel grade. Procedures presented in this section address the problems of erosion and scour. More advanced procedures for permanent, unlined channels may be found elsewhere. (References: Garde and Ranga Raju, 1980) Diversions are channels usually with a supporting ridge on the lower side. They are generally located to divert flows across a slope and are designed following the same procedures as other channels. Design tables for vegetated diversions and waterways are included at the end of this section. Flexible channel linings are generally preferred to rigid linings from an erosion control standpoint because they conform to changes in channel shape without failure and are less susceptible to damage from frost heaving, soil swelling and shrinking, and excessive soil pore water pressure from lack of drainage. Flexible linings also are generally less expensive to construct, and when vegetated, are more natural in appearance. On the other hand, flexible linings generally have higher roughness and require a larger cross section for the same discharge. EROSION CONtROL CRItERIa The minimum design criteria for conveyance channels require that two primary conditions be satisfied: the channel system must have capacity for the peak flow expected from the 10-year storm and the channel lining must be resistant to erosion for the design velocity. In some cases, out-of-bank flow may be considered a functional part of the channel system. In these cases, flow capacities and design velocities should be considered separately for out- of-bank flows and channel flows. Both the capacity of the channel and the velocity of flow are functions of the channel lining, cross-sectional area and slope. The channel system must carry the design flow, fit site conditions, and be stable. Sta BLE CHaNNEL DESIGN mEtHODS Two accepted procedures for designing stable channels with flexible linings are: (1) the permissible velocity approach; and (2) the tractive force approach. Under the permissible velocity approach, the channel is considered stable if the design, mean velocity is lower than the maximum permissible velocity. Under the tractive force approach, erosive stress evaluated at the boundary between flowing water and lining materials must be less than the minimum unit tractive force that will cause serious erosion of material from a level channel bed. 8.05 DESIGN Of Sta BLE CHaNNELS aND DIVERSIONS 8.05.1 8 8.05.2 The permissible velocity procedure is recommended for the design of vegetative channels because of common usage and the availability of reliable design tables. The tractive force approach is recommended for design of channels with temporary synthetic liners or riprap liners. The tractive force procedure is described in full in the U.S. Department of Transportation, Federal Highway Administration Bulletin, Design of Roadside Channels with Flexible Linings. Permissible Velocity Procedure The permissible velocity procedure uses two equations to calculate flow: Manning’s equation, V = 1.49 R2/3 S1/2 n where: V = average velocity in the channel in ft/sec. n = Manning’s roughness coefficient, based upon the lining of the channel R = hydraulic radius, wetted cross-sectional area/wetted perimeter in ft S = slope of the channel in ft/ft and the continuity equation, Q = AV where: Q = flow in the channel in cfs A = cross-sectional area of flow within the channel in ft2 V = average velocity in the channel in ft/sec. Manning’s equation and the continuity equation are used together to determine channel capacity and flow velocity. A nomograph for solving Manning’s equation is given in Figure 8.05a. Selecting Permanent Channel Lining Channel lining materials include such flexible materials as grass, riprap and gabions, as well as rigid materials such as paving blocks, flag stone, gunite, asphalt, and concrete. The design of concrete and similar rigid linings is generally not restricted by flow velocities. However, flexible channel linings do have maximum permissible flow velocities beyond which they are susceptible to erosion. The designer should select the type of liner that best fits site conditions. Table 8.05a lists maximum permissible velocities for established grass linings and soil conditions. Before grass is established, permissible velocity is determined by the choice of temporary liner. Permissible velocities for riprap linings are higher than for grass and depend on the stone size selected. Appendices 8.05.3 8 8.05.4 Table 8.05a Maximum Allowable Design Velocities1 for Vegetated Channels Typical Channel Slope Application Soil Characteristics2 Grass Lining Permissible Velocity3 for Established Grass Lining (ft/sec) 0-5%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 5.0 4.5 4.5 4.5 3.5 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 6.0 5.5 5.5 5.5 4.5 5-10%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 4.5 4.0 4.0 4.0 3.0 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 5.5 5.0 5.0 5.0 3.5 >10%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass 3.5 2.5 2.5 2.5 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass 4.5 3.5 3.5 3.5 Source: USDA-SCS Modified NOTE:1Permissible Velocity based on 10-year storm peak runoff 2Soil erodibility based on resistance to soil movement from concentrated flowing water. 3Before grass is established, permissible velocity is determined by the type of temporary liner used. Selecting Channel Cross-Section Geometry To calculate the required size of an open channel, assume the design flow is uniform and does not vary with time. Since actual flow conditions change throughout the length of a channel, subdivide the channel into design reaches, and design each reach to carry the appropriate capacity. The three most commonly used channel cross-sections are “V”-shaped, parabolic, and trapezoidal. Figure 8.05b gives mathematical formulas for the area, hydraulic radius and top width of each of these shapes. Appendices 8.05.5 8 8.05.6 Rev. 12/93 Design Procedure- Permissible Velocity The following is a step-by-step procedure for designing a runoff conveyance channel using Manning’s equation and the continuity equation: Step 1. Determine the required flow capacity, Q, by estimating peak runoff rate for the design storm (Appendix 8.03). Step 2. Determine the slope and select channel geometry and lining. Step 3. Determine the permissible velocity for the lining selected, or the desired velocity, if paved. (see Table 8.05a, page 8.05.4) Step 4. Make an initial estimate of channel size—divide the required Q by the permissible velocity to reach a “first try” estimate of channel flow area. Then select a geometry, depth, and top width to fit site conditions. Step 5. Calculate the hydraulic radius, R, from channel geometry (Figure 8.05b, page 8.05.5). Step 6. Determine roughness coefficient n. Structural Linings—see Table 8.05b, page 8.05.6. Grass Lining: a. Determine retardance class for vegetation from Table 8.05c, page 8.05.8. To meet stability requirement, use retardance for newly mowed condition (generally C or D). To determine channel capacity, use at least one retardance class higher. b. Determine n from Figure 8.05c, page 8.05.7. Step 7. Calculate the actual channel velocity, V, using Manning’s equation (Figure 8.05a, pg. 8.05.3), and calculate channel capacity, Q, using the continuity equation. Step 8. Check results against permissible velocity and required design capacity to determine if design is acceptable. Step 9. If design is not acceptable, alter channel dimensions as appropriate. For trapezoidal channels, this adjustment is usually made by changing the bottom width. Table 8.05b Manning’s n for Structural Channel Linings Channel Lining Recommended n values Asphaltic concrete, machine placed Asphalt, exposed prefabricated Concrete Metal, corrugated Plastic Shotcrete Gabion Earth 0.014 0.015 0.015 0.024 0.013 0.017 0.030 0.020 Source: American Society of Civil Engineers (modified) Appendices Rev. 12/93 8.05.7 Step 10. For grass-lined channels once the appropriate channel dimensions have been selected for low retardance conditions, repeat steps 6 through 8 using a higher retardance class, corresponding to tall grass. Adjust capacity of the channel by varying depth where site conditions permit. NOTE 1: If design velocity is greater than 2.0 ft/sec., a temporary lining may be required to stabilize the channel until vegetation is established. The temporary liner may be designed for peak flow from the 2-year storm. If a channel requires a temporary lining, the designer should analyze shear stresses in the channel to select the liner that provides protection and promotes establishment of vegetation. For the design of temporary liners, use tractive force procedure. NOTE 2: Design Tables—Vegetated Channels and Diversions at the end of this section may be used to design grass-lined channels with parabolic cross-sections. Step 11. Check outlet for carrying capacity and stability. If discharge velocities exceed allowable velocities for the receiving stream, an outlet protection structure will be required (Table 8.05d, page 8.05.9). Sample Problem 8.05a illustrates the design of a grass-lined channel. 8 8.05.8 Table 8.05c Retardance Classification for Vegetal Covers Retardance Cover Condition A Reed canarygrass Weeping lovegrass Excellent stand, tall (average 36”) Excellent stand, tall (average 30”) B Tall fescue Bermudagrass Grass-legume mixture (tall fescue,red fescue, sericea lespedeza) Grass mixture (timothy, smooth bromegrass or orchardgrass) Sericea lespedeza Reed canarygrass Alfalfa Good stand, uncut, (average 18”) Good stand, tall (average 12”) Good stand, uncut Good stand, uncut (average 20”) Good stand, not woody, tall (average 19”) Good stand, cut, (average 12-15”) Good stand, uncut (average 11”) C Tall fescue Bermudagrass Bahiagrass Grass-legume mixture-- summer (orchardgrass, redtop and annual lespedeza) Centipedegrass Kentucky bluegrass Redtop Good stand (8-12”) Good stand, cut (average 6”) Good stand, uncut (6-8”) Good stand, uncut (6-8”) Very dense cover (average 6”) Good stand, headed (6-12”) Good stand, uncut (15-20”) D Tall fescue Bermudagrass Bahiagrass Grass-legume mixture-- fall-spring (orchardgrass, redtop, and annual lespedeza) Red fescue Centipedegrass Kentucky bluegrass Good stand, cut (3-4”) Good stand, cut (2.5”) Good stand, cut (3-4”) Good stand, uncut (4-5”) Good stand, uncut (12-18”) Good stand, cut (3-4”) Good stand, cut (3-4”) E Bermudagrass Bermudagrass Good stand, cut (1.5”) Burned stubble Modified from: USDA-SCS, 1969. Engineering Field Manual. Appendices 8.05.9 Table 8.05d Maximum Permissible Velocities for Unprotected Soils in Existing Channels. Materials Maximum Permissible Velocities (fps) Fine Sand (noncolloidal) Sand Loam (noncolloidal) Silt Loam (noncolloidal) Ordinary Firm Loam Fine Gravel Stiff Clay (very colloidal) Graded, Loam to Cobbles (noncolloidal) Graded, Silt to Cobbles (colloidal) Alluvial Silts (noncolloidal) Alluvial Silts (colloidal) Coarse Gravel (noncolloidal) Cobbles and Shingles 2.5 2.5 3.0 3.5 5.0 5.0 5.0 5.5 3.5 5.0 6.0 5.5 Sample Problem 8.05a Design of a Grass-lined Channel. Given: Design Q10 = 16.6 cfs Proposed channel grade = 2% Proposed vegetation: Tall fescue Soil: Creedmoor (easily erodible) Permissible velocity, Vp = 4.5 ft/s (Table 8.05a) Retardance class: “B” uncut, “D” cut (Table 8.05c). Trapezoidal channel dimensions: designing for low retardance condition (retardance class D) design to meet Vp. Find: Channel dimensions Solution: Make an initial estimate of channel size A = Q/V, 16.6 cfs/4.5 ft/sec = 3.69 ft2 Try bottom width = 3.0 ft w/side slopes of 3:1 Z = 3 A = bd + Zd2 P = b + 2d Z2 + 1 R = AP An iterative solution using Figure 8.05a to relate flow depth to Manning’s n proceeds as follows: Manning’s equation is used to check velocities. *From Fig. 8.05c, pg. 8.05.7, Retardance Class d (VR=4.5x0.54=2.43) d (ft) A (ft 2) R (ft) *n Vt (fps) Q (cfs) Comments 0.8 4.32 0.54 0.043 3.25 14.0 V<Vp OK, Q<Q10 (too small, try deeper channel) 0.9 5.13 0.59 0.042 3.53 18.10 V<Vp, OK, Q>Q10, OK Now design for high retardance (class B): For the ease of construction and maintenance assume and try d = 1.5 ft and trial velocity Vt = 3.0 ft/sec d (ft) A (ft 2) R (ft)Vt (fps)n V (fps) Q (cfs) Comments 1.5 11.25 0.90 3.0 2.0 1.6 **1.5 0.08 0.11 0.12 0.13 2.5 1.8 1.6 1.5 28 20 18 17 reduce Vtreduce Vt Q>Q10 OK ** These assumptions = actual V (fps.) (chart continued on next page) 8 8.05.10 Rev. 12/93 (continued) Sample Problem 8.05a Design of a Grass-lined Channel. Channel summary: Trapezoidal shape, Z = 3, b = 3 ft, d = 1.5 ft, grade = 2% Note: In Sample Problem 8.05a the “n-value” is first chosen based on a permissible velocity and not a design velocity criteria. Therefore, the use of Table 8.05c may not be as accurate as individual retardance class charts when a design velocity is the determining factor. Tractive Force Procedure The design of riprap-lined channels and temporary channel linings is based on analysis of tractive force. NOTE: This procedure is for uniform flow in channels and is not to be used for design of deenergizing devices and may not be valid for larger channels. To calculate the required size of an open channel, assume the design flow is uniform and does not vary with time. Since actual flow conditions change through the length of a channel, subdivide the channel into design reaches as appropriate. PERMISSIBLE SHEAR STRESS The permissible shear stress, Td, is the force required to initiate movement of the lining material. Permissible shear stress for the liner is not related to the erodibility of the underlying soil. However, if the lining is eroded or broken, the bed material will be exposed to the erosive force of the flow. COMPUTING NORMAL DEPTH The first step in selecting an appropriate lining is to compute the design flow depth (the normal depth) and determine the shear stress. Normal depths can be calculated by Manning’s equation as shown for trapezoidal channels in Figure 8.05d. Values of the Manning’s roughness coefficient for different ranges of depth are provided in Table 8.05e for temporary linings and Table 8.05f for riprap. The coefficient of roughness generally decreases with increasing flow depth. n value for Depth Ranges* Table 8.05e Manning’s Roughness Coefficients for Temporary Lining Materials 0-0.5 ft 0.5-2.0 ft >2.0 ft Lining Type Woven Paper Net Jute Net Fiberglass Roving Straw with Net Curled Wood Mat Synthetic Mat 0.016 0.028 0.028 0.065 0.066 0.036 0.015 0.022 0.021 0.033 0.035 0.025 0.015 0.019 0.019 0.025 0.028 0.021 * Adapted from: FHWA-HEC 15, Pg. 37 - April 1988 Appendices Rev. 12/93 8.05.11 8 8.05.12 Rev. 12/93 Table 8.05f Manning’s Roughness Coefficient n - value n value for Depth Ranges Lining Category Lining Type 0-0.5 ft (0-15 cm) 0.5-2.0 ft (15-60 cm) 2.0 ft (>60 cm) Rigid Concrete Grouted Riprap Stone Masonry Soil Cement Asphalt 0.015 0.040 0.042 0.025 0.018 0.013 0.030 0.032 0.022 0.016 0.013 0.028 0.030 0.020 0.016 Unlined Bare Soil Rock Cut 0.023 0.045 0.020 0.035 0.020 0.025 Gravel Riprap 1-inch (2.5-cm) D502-inch (5-cm) D50 0.044 0.066 0.033 0.041 0.030 0.034 Rock Riprap 6-inch (15-cm) D5012-inch (30-cm) D50 0.104 -- 0.069 0.078 0.035 0.040 Note: Values listed are representative values for the respective depth ranges. Manning’s roughness coefficients, n, vary with the flow depth. DETERMINING SHEAR STRESS Shear stress, T, at normal depth is computed for the lining by the following equation: T = yds Td = Permissible shear stress where: T = shear stress in lb/ft2 y = unit weight of water, 62.4 lb/ft3 d = flow depth in ft s = channel gradient in ft/ft If the permissible shear stress, Td, given in Table 8.05g is greater than the computed shear stress, the riprap or temporary lining is considered acceptable. If a lining is unacceptable, select a lining with a higher permissible shear stress and repeat the calculations for normal depth and shear stress. In some cases it may be necessary to alter channel dimensions to reduce the shear stress. Computing tractive force around a channel bend requires special considerations because the change in flow direction imposes higher shear stress on the channel bottom and banks. The maximum shear stress in a bend, Tb, is given by the following equation: Tb = KbT where: Tb = bend shear stress in lb/ft2 kb = bend factor T = computed stress for straight channel in lb/ft2 The value of kb is related to the radius of curvature of the channel at its center line, Rc, and the bottom width of the channel, B, Figure 8.05e. The length of channel requiring protection downstream from a bend, Lp, is a function of the roughness of the lining material and the hydraulic radius as shown in Figure 8.05f. Appendices Rev. 12/93 8.05.13 Table 8.05g Permissible Shear Stresses for Riprap and Temporary Liners Permissible Unit Shear Stress, Td Lining Category Lining Type (lb/ft2) Temporary Woven Paper Net Jute Net Fiberglass Roving: Single Double Straw with Net Curled Wood mat Synthetic Mat 0.15 0.45 0.60 0.85 1.45 1.55 2.00 d50 Stone Size (inches) Gravel Riprap 1 2 0.33 0.67 Rock Riprap 6 9 12 15 18 21 24 2.00 3.00 4.00 5.00 6.00 7.80 8.00 Adapted From: FHWA, HEC-15, April 1983, pgs. 17 & 37. Design Procedure- Temporary Liners The following is a step-by-step procedure for designing a temporary liner for a channel. Because temporary liners have a short period of service, the design Q may be reduced. For liners that are needed for six months or less, the 2-year frequency storm is recommended. Step 1. Select a liner material suitable for site conditions and application. Determine roughness coefficient from manufacturer’s specifications or Table 8.05e, page 8.05.10. Step 2. Calculate the normal flow depth using Manning’s equation (Figure 8.05d). Check to see that depth is consistent with that assumed for selection of Manning’s n in Figure 8.05d, page 8.05.11. For smaller runoffs Figure 8.05d is not as clearly defined. Recommended solutions can be determined by using the Manning equation. Step 3. Calculate shear stress at normal depth. Step 4. Compare computed shear stress with the permissible shear stress for the liner. Step 5. If computed shear is greater than permissible shear, adjust channel dimensions to reduce shear, or select a more resistant lining and repeat steps 1 through 4. Design of a channel with temporary lining is illustrated in Sample Problem 8.05b, page 8.05.14. 8 8.05.14 Rev. 12/93 Sample Problem 8.05b Design of a Temporary Liner for a Vegetated Channel Given: Q2 = 16.6 cfs Bottom width = 3.0 ft Z = 3 n = 0.02 (Use basic n value for channels cut in earth (Table 8.05b) Vp = 2.0 ft/sec maximum allowable velocity for bare soil (pg. 6.30.1) Channel gradient = 2% Find: Suitable temporary liner material Solution: Using Manning’s equation: b(ft) d(ft) A(ft 2) R(ft) V(fps) Q(cfs) Comments 3.0 0.59 2.82 0.42 5.88 16.60 V>Vp, (needs protection) Q Q2, OK Velocity >2.0 fps channel requires temporary liner:* Calculate channel design with straw with net as temporary liner. n = 0.033 (Table 8.05e). Td = 1.45 (Table 8.05g, pg. 8.05.13) b(ft) d(ft) A(ft 2) R(ft) V(fps) Q(cfs) Comments 3.0 0.76 4.05 1.94 4.10 16.60 V<Td, OK Calculate shear stress for Q2 conditions: T = yds where: y = unit weight of water (62.4 lb/ft3) d = flow depth in ft s = channel gradient in ft/ft T = (62.4)(0.76)(0.02) = 0.95 T<Td, OK Temporary liner: straw with net. *In some cases the solution is not as clearly defined; the use of a more conservative material is recommended. DESIGN OF RIPRAP LINING-MILD GRADIENT The mild gradient channel procedure is applicable for channel grades less than 10%. The method assumes that the channel cross section has been designed properly, including undercut and that the remaining problem is to provide a stable riprap lining. Side slope stability. As the angle of the side slope approaches the angle of repose of the channel lining, the lining material becomes less stable. The stability of a side slope is given by the tractive force ratio, K2, a function of the side slope and the angle of repose of the rock lining material. The rock size to be used for the channel lining can be determined by comparing the tractive force ratio, an indicator of side slope stability, to the shear stress on the sides and shear stress on the bottom of the channel. The angle of repose for different rock shapes and sized is shown in Figure 8.05g. The required rock size (mean diameter of the gradation, d50) for the side slopes is determined from the following equation: d50 (sides) = K1 d50 (bottom) K2where: K1 = ratio of shear stress on the sides, Ts, and bottom, T, of a trapezoidal channel (Figure 8.05h), K2 = tractive force ratio (Figure 8.05i). Appendices Rev. 12/93 8.05.15 8 8.05.16 Rev. 12/93 Appendices Rev. 12/93 8.05.17 Selection of riprap gradation and thickness. Riprap gradation should have a smooth size distribution curve. The largest stone size in the gradation should not exceed 1.5 times the d50 size. The most important criterion is that interstices formed by larger stones be filled with smaller sizes in an interlocking fashion, preventing the formation of open pockets. These gradation requirements apply regardless of the type of filter design used. In general, riprap constructed with angular stone performs best. Round stones are acceptable as riprap provided they are not placed on side slopes steeper than 3:1. Flat, slab-like stones should be avoided since they are easily dislodged by the flow. An approximate guide to stone shape is that neither the breadth nor the thickness of a single stone be less than one-third its length. The thickness of a riprap lining should equal 1.5 times the diameter of the largest rock size in the gradation. Filter design: When rock riprap is used, an appropriate underlying filter material must be selected. The filter material may be either a granular, gravel or sand filter blanket, or a geotextile fabric. 8 8.05.18 Rev. 12/93 For a granular filter blanket, the following criteria must be met: d15 filter d85 base < 5 5 <d15 filter d15 base < 40 d50 filter d50 base < 40 Where “filter” refers to the overlying riprap or gravel and “base” refers to the underlying soil, sand or gravel. The relationship must hold between the filter blanket and base material and between the riprap and filter blanket. The minimum thickness for a filter blanket should not be less than 6 inches. In selecting a filter fabric, the fabric should have a permeability at least equal to the soil and a pore structure that will hold back the base soil. The following properties are essential to assure performance under riprap: • For filter fabric covering a base with granular particles containing 50 percent or less (by weight) of fine particles (less than U.S. Standard Sieve No. 200): a. d85 base (mm)/EOS* filter cloth (mm) > 1. b. Total open area of filter is less than 36%. • Filter fabric covering other soils: a. EOS less than U.S. Standard Sieve No. 70. b. Total open area of filter less than 10%. *EOS - Equivalent Opening Size to a U.S. Standard Sieve Size Design Procedure- Riprap Lining, Mild Gradient The following is a step-by-step procedure for designing a riprap channel lining with mild gradients. This procedure is designed for smaller channels that are generally used as erosion control measures, and is not intended for conveyance channels. Additional design information for lined channels may be obtained from the National Technical Information Services (NTIS) by obtaining a copy of the National Cooperative Highway Research Program Report No. 108, titled “Tentative Design Procedure for Riprap - Lined Channels”. Step 1. Select a riprap size, and look up the Manning’s n value (Table 8.05f) and permissible shear stress, Td (Table 8.05g). Step 2. Calculate the normal flow depth in the channel, using Manning’s equation (Figure 8.05d). Check that the n value for the calculated normal depth is consistent with that determined in step 1. Step 3. Calculate shear stress at normal depth. REFERENCE 4 “Standard Specification for Roads and Structures”, North Carolina Department of Transportation, Raleigh, January 2012. Section 1043 10-62 All stone shall meet the approval of the Engineer. While no specific gradation is required, 1 there shall be equal distribution of the various sizes of the stone within the required size 2 range. The size of an individual stone particle will be determined by measuring its long 3 dimension. 4 Stone or broken concrete for rip rap shall meet Table 1042-1 for the class and size 5 distribution. 6 TABLE 1042-1 ACCEPTANCE CRITERIA FOR RIP RAP AND STONE FOR EROSION CONTROL Required Stone Sizes, inches Class Minimum Midrange Maximum A 2 4 6 B 5 8 12 1 5 10 17 2 9 14 23 No more than 5.0% of the material furnished can be less than the minimum size specified nor 7 no more than 10.0% of the material can exceed the maximum size specified. 8 SECTION 1043 9 AGGREGATE FROM CRUSHED CONCRETE 10 1043-1 GENERAL 11 Aggregate from crushed concrete is a recycled product made by crushing concrete obtained 12 from concrete truck clean out, demolition of existing concrete structures or pavement, or 13 similar sources and transported from a crushing facility. It does not include concrete 14 pavements that are rubblelized, broken or otherwise crushed in place on the roadway. 15 The crushed material must meet all sources approval requirements described in Sections 1005 16 and 1006 with the exception of the sodium sulfate test requirement. Deleterious materials 17 shall not be more than 3%. 18 Sampling and acceptance for the determination of gradaction, LL and PI will be performed as 19 described in the Aggregate QC/QA Program Manual and the Aggregate Sampling Manual. 20 1043-2 AGGREGATE BASE COURSE 21 The material shall meet the ABC gradation. The LL of the material shall be raised 5 points to 22 no more than 35. 23 1043-3 AGGREGATE SHOULDER BORROW 24 The material shall meet Section 1019. 25 1043-4 CLEAN COARSE AGGREGATE FOR ASPHALT 26 The material shall meet the gradation of a standard size in Table 1005-1. Use of the material 27 shall be approved by the Engineer, and the mix shall meet all requirements. 28 1043-5 CLEAN COARSE AGGREGATE FOR CONCRETE 29 The material shall meet the gradation of a standard size in Table 1005-1. Use of the material 30 is restricted to Class B concrete mixes only. Use of the material shall be approved by the 31 Engineer, and the concrete shall meet all requirements. 32 SECTION 1044 33 SUBSURFACE DRAINAGE MATERIALS 34 1044-1 SUBDRAIN FINE AGGREGATE 35 Subdrain fine aggregate shall meet No. 2S or 2MS in Table 1005-2. 36 NCDOT 2012 Standard Specifications REFERENCE 5 United States Department of Agriculture, “Urban Hydrology for Small Watersheds”, Technical Release 55, June 1986. Technical Release 55 Urban Hydrology for Small Watersheds Time of Concentration and Travel TimeChapter 3 3–4 (210-VI-TR-55, Second Ed., June 1986) Manning’s equation is: V rs n =149 2 3 1 2.[eq. 3-4] where: V = average velocity (ft/s) r = hydraulic radius (ft) and is equal to a/pw a = cross sectional flow area (ft 2) pw = wetted perimeter (ft) s = slope of the hydraulic grade line (channel slope, ft/ft) n = Manning’s roughness coefficient for open channel flow. Manning’s n values for open channel flow can be obtained from standard textbooks such as Chow (1959) or Linsley et al. (1982). After average velocity is computed using equation 3-4, Tt for the channel seg- ment can be estimated using equation 3-1. Reservoirs or lakes Sometimes it is necessary to estimate the velocity of flow through a reservoir or lake at the outlet of a watershed. This travel time is normally very small and can be assumed as zero. Limitations •Manning’s kinematic solution should not be used for sheet flow longer than 300 feet. Equation 3-3 was developed for use with the four standard rainfall intensity-duration relationships. •In watersheds with storm sewers, carefully identify the appropriate hydraulic flow path to estimate Tc. Storm sewers generally handle only a small portion of a large event. The rest of the peak flow travels by streets, lawns, and so on, to the outlet. Consult a standard hydraulics textbook to determine average velocity in pipes for either pressure or nonpressure flow. •The minimum Tc used in TR-55 is 0.1 hour. •A culvert or bridge can act as a reservoir outlet if there is significant storage behind it. The proce- dures in TR-55 can be used to determine the peak flow upstream of the culvert. Detailed storage routing procedures should be used to determine the outflow through the culvert. Example 3-1 The sketch below shows a watershed in Dyer County, northwestern Tennessee. The problem is to compute Tc at the outlet of the watershed (point D). The 2-year 24-hour rainfall depth is 3.6 inches. All three types of flow occur from the hydraulically most distant point (A) to the point of interest (D). To compute Tc, first determine Tt for each segment from the following information: Segment AB: Sheet flow; dense grass; slope (s) = 0.01 ft/ft; and length (L) = 100 ft. Segment BC: Shallow concentrated flow; unpaved; s = 0.01 ft/ft; and L = 1,400 ft. Segment CD: Channel flow; Manning’s n = .05; flow area (a) = 27 ft2; wetted perimeter (pw) = 28.2 ft; s = 0.005 ft/ft; and L = 7,300 ft. See figure 3-2 for the computations made on worksheet 3. A B C D 7,300 ft1,400 ft100 ft (Not to scale) Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 1 of 13 12/9/2016 (Initial Submittal) Calculation Title: Final Conditions Stormwater Calculation Summary: Stormwater channels, culverts, and downdrains were designed to convey stormwater for a 100 year, 24-hour design storm event considering long-term conditions after decommissioning of the Primary and Secondary Ash Basin dams. Notes: Revision Log: No. Description Originator Verifier Technical Reviewer 0 Initial Submittal – 12/9/2016 Chris Jordan Stephanie Stanwick Cedric H. Ruhl Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 2 of 13 12/9/2016 (Initial Submittal) OBJECTIVE: The objective of this calculation is to design the stormwater conveyance measures based on long- term conditions after decommissioning of the Primary and Secondary Ash Basin dams. METHOD: Stormwater flow rates will be calculated using the SCS method. The hydraulic capacity of existing and proposed stormwater conveyances will be evaluated using Manning’s equation and HydroCAD modeling software. DEFINITION OF VARIABLES: = shear; A = area; b = bottom width; CN = curve number; d = flow depth; D = channel depth; i = rainfall depth; L = length; n = Manning’s n; P = wetted perimeter; Q = flow; R = hydraulic radius; S = longitudinal slope; t = time T = top width; Tc = time of concentration; V = velocity; and Z = channel side slope. CALCULATIONS: 1.0 Design conveyances for upstream tributary areas and ash basin closure channels Concentrated stormwater flow from upstream tributary areas was assumed to discharge across the closed ash basin at five locations shown in Figures 1 and 2, and are described below. Drainage area DA-1 is the area draining to the inlet of the existing 48-inch diameter corrugated metal pipe (CMP) west of Edgewood Road. The 48-inch CMP historically conveyed stormwater flow underneath the primary ash basin and into the Dan River. The CMP has been grouted, and water from this area is currently discharged by pumping. A proposed channel will convey additional stormwater flow from additional tributary areas west of the 48-inch CMP pipe inlet. Upon completion of basin closure activities, a new pipe will restore flow from the area of the inlet at the existing grouted 48-inch diameter CMP to the ash basin closure area. The new pipe will Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 3 of 13 12/9/2016 (Initial Submittal) discharge into a channel that will convey stormwater flow across the closed ash basin area and into the Dan River. Drainage area DA-2 is the area flowing into the inlet of the existing 54-inch diameter RCP. The 54-inch pipe connects to a drop inlet which conveys water through a 36-inch diameter RCP and outlets into the secondary ash basin in the vicinity of the intermediate dike. The upstream end of the 54-inch diameter RCP pipe has been temporarily sealed with a grout plug. Upon completion of basin closure activities, the grout plug will be removed and a new section of pipe will restore flow to the ash basin closure area. The new pipe will discharge into a channel that will convey stormwater flow across the closed ash basin area and into the Dan River. Drainage area DA-3 has a 36-inch culvert which conveys stormwater underneath the railroad tracks and discharges into the secondary ash basin. Upon completion of basin closure activities, a slope drain will convey flow from the culvert to the ash basin closure area. The slope drain will discharge into a channel that will convey flow across the closed ash basin area and into the Dan River. Drainage area DA-4 is the area flowing into the outlet pipe for the dredge area between Ash Fills 1 and 2, which currently discharges into the secondary ash basin. Upon completion of basin closure activities, a slope drain will convey flow from the outlet pipe to the ash basin closure area. The slope drain will discharge into a channel that will convey stormwater flow into a channel that will convey flow across the closed ash basin area and into the Dan River. Drainage area DA-8A-1A is the area in between the 36-inch culvert and the ash basin. Upon completion of basin closure activities, a diversion ditch will be installed between the rail line and ash basin perimeter road, with multiple slope drains that discharge into the ash basin footprint. The existing ash basin area was divided in four main drainage areas based on post-closure stormwater discharge locations into the Dan River. The main drainage areas are numbered west to east as DA-5, DA-6, DA-7 and DA-8. The drainage areas were sub-divided to analyze stormwater flows to collector channels. These drainage areas within the footprint are assumed to be bare soil initially, and vegetated in the final conditions. The water flow path in the ash basin footprint was assumed to follow an inter-connected network of interceptor ditches, toe ditches and longitudinal ditches, which finally discharge the water to the Dan River. 1.1 Estimate drainage areas Drainage areas were delineated to drain stormwater for long-term conditions after construction of the proposed Dan River Landfill and closure of the existing ash units (Ash Fills 1 and 2, Primary and Secondary Ash Basins). The drainage areas are defined in Figure 1 and are summarized in the following table: Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 4 of 13 12/9/2016 (Initial Submittal) Drainage Area ID Drainage Area {A} (ac) Curve Number (CN) Drainage Area ID Drainage Area {A} (ac) Curve Number (CN) DA-1 22.70 83 DA-7C 2.48 74 DA-2 6.10 74 DA-7D 2.65 74 DA-3 2.39 74 DA-7E 1.64 74 DA-4 74.10 78 DA-7F 3.00 74 DA-5A 4.03 74 DA-7G 2.26 74 DA-5B 2.13 74 DA-8A-1A 0.62 74 DA-5C 2.83 74 DA-8A-1B 0.75 74 DA-5D 2.18 74 DA-8A-1C 0.13 74 DA-6A 1.23 74 DA-8A-1D 1.24 74 DA-6B 2.78 74 DA-8A-1E 0.29 74 DA-6C 2.51 74 DA-8A-1F 0.17 74 DA-6D 2.70 74 DA-8A-1G 0.35 74 DA-6E 3.25 74 DA-8A 4.89 74 DA-6F 1.78 74 DA-8B 2.88 74 DA-6G 2.61 74 DA-8C 1.48 74 DA-7A 4.69 74 DA-8D 1.77 74 DA-7B 1.71 74 Table 1: Summary of Drainage Areas 1.2 Calculate time of concentration The time of concentration (Tc) is the time needed for water to flow from the most remote point in a drainage area to the drainage area outlet. The estimated time of concentration for the drainage areas is shown in Figure 1. The total time of concentration for a catchment generally consists of the following three components: sheet flow, shallow concentrated flow and channel flow. In the current analysis, sheet flow was assumed for the first 100 feet of the flow path, after which the flow was generally classified as shallow concentrated flow. However, if the flow entered a channel within the sub- catchment, then the flow was classified as channel flow. Several sub-catchments were relatively small and were hydrologically difficult to generate sheet flow, shallow concentrated flow or channel flow components for evaluation of time of concentration. A minimum time of concentration of 6 minutes (as described by TR-55, Ref. 5) was used for such relatively small sub-catchments. HydroCAD software [Ref. 2] was used to estimate time of concentration based on input parameters summarized in the following tables: Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 5 of 13 12/9/2016 (Initial Submittal) Drainage Area ID Flow Length {L} (ft.) Surface Description Manning No. {n} Land Slope (ft/ft) Time of Concentration {Tc,sheet} (min) DA-1 Smooth surface 0.011 0.067 0.7 DA-2 0.150 0.050 6.5 DA-3 0.150 0.074 5.6 DA-4 0.150 0.043 6.9 DA-5A 0.150 0.073 5.6 DA-5B 0.150 0.025 8.6 DA-5C 0.150 0.014 10.9 DA-5D DA-6A 0.150 0.010 12.8 DA-6B 0.150 0.033 7.7 DA-6C 0.150 0.017 10.0 DA-6D 0.150 0.015 10.5 DA-6E 0.150 0.012 11.5 DA-6F 0.150 0.017 10 DA-6G DA-7A Grass: Short 0.150 0.072 5.6 DA-7B DA-7C 0.150 0.016 10.4 DA-7D 0.150 0.011 12.1 DA-7E 0.150 0.018 9.8 DA-7F 0.150 0.017 10.1 DA-7G DA-8A-1A DA-8A-1B DA-8A-1C DA-8A-1D Grass: Short 0.150 0.200 3.8 DA-8A-1E DA-8A-1F DA-8A-1G DA-8A 0.150 0.100 4.9 DA-8B 0.150 0.010 12.2 DA-8C 0.150 0.014 10.7 DA-8D Table 2: Time of Concentration from Sheet Flow Grass: Short -NA- -NA- -NA- Grass: Short 100 Grass: Short -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- Grass: Short Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 6 of 13 12/9/2016 (Initial Submittal) Drainage Area ID Flow Length {L} (ft.) Surface Description Land Slope (ft/ft) Time of Concentration {Tc,scf} (min) DA-1 2,343 Unpaved 0.039 12.3 DA-2 752 Woodland 0.058 10.5 DA-3 665 Short Grass Pasture 0.051 7.0 DA-4 2,834 Grass Waterway 0.058 13.1 DA-5A 0 0.0 0.000 0.0 DA-5B 288 0.014 5.8 DA-5C 218 0.021 3.6 DA-5D DA-6A 98 0.031 1.3 DA-6B 168 0.027 2.4 DA-6C 168 0.022 2.7 DA-6D 329 0.015 6.4 DA-6E 224 0.020 3.8 DA-6F 148 0.021 2.4 DA-6G DA-7A 534 Short Grass Pasture 0.013 11.2 DA-7B DA-7C 226 0.024 3.5 DA-7D 277 0.017 5.1 DA-7E 139 0.021 2.3 DA-7F 498 0.008 13.3 DA-7G DA-8A-1A DA-8A-1B DA-8A-1C DA-8A-1D 576 Short Grass Pasture 0.024 8.9 DA-8A-1E DA-8A-1F DA-81-1G DA-8A 695 0.052 7.3 DA-8B 252 0.020 4.2 DA-8C 320 0.013 6.7 DA-8D -NA- -NA- Table 3: Time of Concentration from Shallow Concentrated Flow -NA- -NA- -NA- Short Grass Pasture Short Grass Pasture Short Grass Pasture Short Grass Pasture -NA- -NA- -NA- -NA- -NA- -NA- Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 7 of 13 12/9/2016 (Initial Submittal) Drainage Area ID Flow Length {L} (ft.) Channel Velocity {V} (ft/s) Time of Concentration {Tc,channel} (min) DA-1 0 DA-2 0 DA-3 0 DA-4 0 DA-5A 973 3.16 5.10 DA-5B 428 1.89 3.80 DA-5C 468 2.42 3.20 DA-5D DA-6A 212 4.55 0.80 DA-6B 202 4.63 0.70 DA-6C 318 3.49 1.50 DA-6D 269 3.28 1.40 DA-6E 552 2.23 4.10 DA-6F 289 3.09 1.60 DA-6G DA-7A 245 3.38 1.20 DA-7B DA-7C 245 2.54 1.60 DA-7D 241 2.54 1.60 DA-7E 289 3.09 1.60 DA-7F 432 2.53 2.80 DA-7G DA-8A-1A DA-8A-1B DA-8A-1C DA-8A-1D DA-8A-1E DA-8A-1F DA-8A-1G DA-8A 662 3.59 3.10 DA-8B 564 1.69 5.60 DA-8C 305 3.00 1.70 DA-8D -NA- -NA- -NA- -NA- Table 4: Time of Concentration from Channel Flow -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 8 of 13 12/9/2016 (Initial Submittal) Drainage Area ID Time of Concentration {Tc,sheet} (min) Time of Concentration {Tc,scf} (min) Time of Concentration {Tc,channel} (min) Total Time of Concentration {Tc,total} (min) DA-1 0.7 12.3 0.0 13.0 DA-2 6.5 10.5 0.0 17.0 DA-3 5.6 7.0 0.0 12.6 DA-4 6.9 13.1 0.0 20.0 DA-5A 5.6 0.0 5.1 10.7 DA-5B 8.6 5.8 3.8 18.2 DA-5C 10.9 3.6 3.2 17.7 DA-5D 6.0 DA-6A 12.8 1.3 0.8 14.9 DA-6B 7.7 2.4 0.7 10.8 DA-6C 10.0 2.7 1.5 14.2 DA-6D 10.5 6.4 1.4 18.3 DA-6E 11.5 3.8 4.1 19.4 DA-6F 10.0 2.4 1.6 14.0 DA-6G 6.0 DA-7A 5.6 11.2 1.2 18.0 DA-7B 6.0 DA-7C 10.4 3.5 1.6 15.5 DA-7D 12.1 5.1 1.6 18.8 DA-7E 9.8 2.3 1.6 13.7 DA-7F 10.1 13.3 2.8 26.2 DA-7G 6.0 DA-8A-1A 6.0 DA-8A-1B 6.0 DA-8A-1C 6.0 DA-8A-1D 3.8 8.9 0.0 12.7 DA-8A-1E 6.0 DA-8A-1F 6.0 DA-8A-1G 6.0 DA-8A 4.9 7.3 3.1 15.3 DA-8B 12.2 4.2 5.6 22.0 DA-8C 10.7 6.7 1.7 19.1 DA-8D 6.0-NA- Table 5: Total Time of Concentration -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- -NA- 1.3 Describe land use conditions Land use conditions were estimated based on anticipated long-term conditions as shown in Figure 2. For the purpose of this calculation, it was assumed that the post-closure use of the Ash Fill 2 area will consist of a gravel lay-down area consistent with the current land use. Site soils were assumed to consist of hydric soil class C. Land use conditions and associated curve numbers for tributary areas numbered DA-1 through DA-8A-1G are summarized in the following table: Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 9 of 13 12/9/2016 (Initial Submittal) Curve Number {CN} [Ref. 2] Area {A} (ac) Curve Number {CN} [Ref. 2] Area {A} (ac) Curve Number {CN} [Ref. 2] Area {A} (ac) Curve Number {CN} [Ref. 2] Area {A} (ac) DA-1 74 12.69 73 0.32 96 9.76 0 0.00 83 22.77 DA-2 74 4.35 73 1.53 96 0.14 0 0.00 74 6.03 DA-3 74 1.26 73 1.12 96 0.00 0 0.00 74 2.39 DA-4 74 49.19 73 9.94 96 14.96 0 0.00 78 74.10 DA-8A-1A 74 0.62 73 0 96 0 0 0.00 74 0.62 DA-8A-1B 74 0.75 73 0 96 0 0 0.00 74 0.75 DA-8A-1C 74 0.13 73 0 96 0 0 0.00 74 0.13 DA-8A-1D 74 1.24 73 0 96 0 0 0.00 74 1.24 DA-8A-1E 74 0.29 73 0 96 0 0 0.00 74 0.29 DA-8A-1F 74 0.17 73 0 96 0 0 0.00 74 0.17 DA-8A-1G 74 0.35 73 0 96 0 0 0.00 74 0.35 Table 6: Land use conditions for tributary areas Total Area {A} (ac) Drainage Area ID Land Use = Grass Land Use = Woods Land Use = Gravel Land Use = Impervious Composite Curve Number {CN} Land use conditions in drainage areas 5 through 8 were assumed to change during the ash removal phase and final grading process. Hence, stormwater analysis for the ash basin was divided in two phases. Under the initial phase of interim conditions, the basin area was assumed to be newly graded area with hydric soil class C (Curve Number of 91), and with no vegetative cover and are calculated in the “Interim Conditions Stormwater Calculation”. Final long term conditions within the ash basin footprint were assumed to consist of at least 75% grass cover with hydric soil class C (Curve Number of 74). HydroCAD software was used to estimate long-term stormwater flows for drainage areas DA-1 through DA-8 for the 100-year, 24-hour storm event based on the SCS method. The 100 year storm resulted in 8.4 inch type II 24-hr rainfall [Ref. 1]. 1.4 Stormwater channel capacity Stormwater channels in the ash basin area consist of interceptor ditches (INT), toe ditches (TD) and longitudinal ditches (LD). Interceptor ditches are used within the ash basin footprint to interrupt drainage lengths and reduce erosion potential. Toe ditches are located along the southern edge of the ash basin footprint to intercept stormwater and convey flow to the four defined outlet points which discharge into the Dan River. Longitudinal ditches are located within the ash basin footprint perpendicular to the slope and convey concentrated flows from upstream tributary drainage areas to two of the four defined outlet points which discharge into the Dan River. The proposed stormwater ditch dimensions are presented in the following table: Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 10 of 13 12/9/2016 (Initial Submittal) Channel ID Channel Type Bottom Width {b} (ft) MIN. Depth {D} (ft) Left Side Slope {Z1H:V} Right Side Slope {Z2H:V} Top Width {T} (ft) Upstream Invert (ft) Downstream Invert (ft) Length {L} (ft) Longitudinal Slope {S} (ft/ft) 5A INT 4 1.5 20 20 514 500 973 0.014 5B INT 0 1.5 20 20 506 504 379 0.005 6A INT 0 1.5 20 20 510 504 212 0.029 6B INT 0 1.5 20 20 510 504 202 0.030 6C INT 0 1.5 20 20 505 500 318 0.017 6D INT 0 1.5 20 20 504 500 269 0.015 7A INT 0 1.5 20 20 510 506 245 0.016 7B INT 0 1.5 20 20 510 509 312 0.006 7C INT 0 1.5 20 20 504 502 245 0.009 7D INT 0 1.5 20 20 504 502 241 0.009 8A INT 6 1.5 20 20 508 500 662 0.012 8B INT 0 1.5 20 20 504 502 564 0.004 DD-1 DIV 2 2 3 3 529 526 381 0.007 DD-2 DIV 2 2 3 3 531 526 304 0.014 DD-3 DIV 2 2 3 3 531 528 48 0.056 DD-4 DIV 2 2 3 3 530 528 80 0.024 DD-5 DIV 2 2 3 3 530 529 94 0.011 DD-6 DIV 2 2 3 3 532 529 40 0.078 5C TD 0 2 5 5 2.50 0 468 0.005 6E TD 0 2.5 3 3 2.68 0 552 0.005 6F TD 6 1.5 3 3 1.36 0 289 0.005 7E TD 6 1.5 3 3 1.40 0 289 0.005 7F TD 6 2 3 3 1.40 0 432 0.003 8C TD 6 1.5 3 3 1.39 0 305 0.005 LD-1A LD 6 6 3 3 508 504 335 0.012 LD-1B LD 6 4 3 3 504 500 312 0.013 LD-1C LD 6 4 3 3 500 498 184 0.010 LD-1D LD 6 4 3 3 498 497 107 0.009 LD-2A LD 6 4 3 3 510 506 282 0.014 LD-2B LD 6 3 3 3 506 502 306 0.014 LD-2C LD 6 3 3 3 501 498 166 0.018 LD-2D LD 6 3 3 3 498 496 107 0.019 Table 7: Channel Dimensions VARIES The capacity of the proposed stormwater channels was evaluated using Manning’s equation presented as follows: 𝑉=1.49 𝑛𝑃2/3 𝑃1/2 [Ref. 3] and 𝑃=𝐴𝑉 [Ref. 3] The flow area “A” and wetted perimeter “P” were calculated using the following relationships based on the geometry of a trapezoidal channel with a flow depth “d”, bottom width “b”, left side slope “Z1”, and right side slope “Z2”: 𝐴=𝑏𝑑+0.5𝑍1 𝑑2 +0.5𝑍2 𝑑2 𝑃=𝑏+√[(𝑍1 𝑑)2 +𝑑2 ]+√[(𝑍2 𝑑)2 +𝑑2 ] Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 11 of 13 12/9/2016 (Initial Submittal) The proposed stormwater channel capacities were evaluated assuming a soil channel lining for the 100-year storm. The trial flow depth and Manning’s n were iteratively modified until the channel capacity exceeded the peak runoff for the conditions modeled. The proposed stormwater channels are anticipated to be stable when vegetated for the conditions modeled. A vegetative class “C” was assumed for the long-term grass channel lining conditions of interceptor and toe- ditches. However, longitudinal ditches were assumed to be lined with rock rip-rap (d50 = 9 inch) as designed in a subsequent section of this calculation. Channel capacity was estimated as shown in the following table: Channel ID Channel Type Channel Lining Manning's n {n} Trial Flow Depth {d} (ft) Flow Area {A} (ft2) Wetted Perimeter {P} (ft) Hydraulic Radius {R} (ft) Velocity {V} (ft/s) Channel Capacity {Q} (cfs) Peak Runoff {Q} (cfs) Channel Capacity > Peak Runoff? Freeboard (in) 5A INT grass 0.132 1.04 25.8 45.7 0.6 0.9 23.60 23.07 yes 5.5 5B INT grass 0.24 1.36 37.0 54.5 0.7 0.3 12.89 12.69 yes 1.7 6A INT grass 0.212 0.8 12.8 32.0 0.4 0.6 8.25 8.06 yes 8.4 6B INT grass 0.108 0.87 15.1 34.8 0.4 1.4 20.78 20.34 yes 7.6 6C INT grass 0.125 0.96 18.4 38.4 0.5 0.9 17.40 16.91 yes 6.5 6D INT grass 0.13 0.97 18.8 38.8 0.5 0.9 16.46 15.99 yes 6.4 7A INT grass 0.112 1.1 24.2 44.1 0.5 1.1 27.60 26.01 yes 4.8 7B INT grass 0.201 1.33 35.4 53.3 0.7 0.4 14.95 14.90 yes 2.0 7C INT grass 0.16 1.15 26.5 46.1 0.6 0.6 16.43 16.03 yes 4.2 7D INT grass 0.2 1.23 30.3 49.3 0.6 0.5 15.75 15.43 yes 3.2 8A INT grass 0.102 1.13 32.3 51.3 0.6 1.2 37.68 30.78 yes 4.4 8B INT grass 0.205 1.47 43.2 58.9 0.7 0.4 15.64 15.49 yes 0.4 DD-1 DIV grass 0.125 1.21 6.8 9.7 0.7 0.8 5.32 5.54 no 9.5 DD-2 DIV grass 0.092 1 5.0 8.3 0.6 1.4 6.87 6.70 yes 12.0 DD-3 DIV grass 0.23 0.48 1.7 5.0 0.3 0.7 1.20 1.16 yes 18.2 DD-4 DIV grass 0.079 0.93 4.5 7.9 0.6 2.0 8.84 8.79 yes 12.8 DD-5 DIV grass 0.151 0.94 4.5 7.9 0.6 0.7 3.18 3.14 yes 12.7 DD-6 DIV grass 0.1 0.33 1.0 4.1 0.2 1.6 1.59 1.52 yes 20.0 5C TD grass 0.082 1.73 15.0 17.6 0.8 1.2 17.80 17.37 yes 3.2 6E TD grass 0.071 2.08 13.0 13.2 1.0 1.4 18.80 18.62 yes 5.0 6F TD grass 0.101 1.3 12.9 14.2 0.9 0.9 12.20 12.05 yes 2.4 7E TD grass 0.102 1.25 12.2 13.9 0.9 0.9 11.33 11.21 yes 3.0 7F TD grass 0.096 1.69 18.7 16.7 1.1 1.0 17.81 14.40 yes 3.7 8C TD grass 0.104 1.12 10.5 13.1 0.8 0.8 8.74 8.56 yes 4.6 LD-1A LD rock rip-rap 0.0375 2.59 35.7 22.4 1.6 6.0 214.40 213.37 yes 40.9 LD-1B LD rock rip-rap 0.0375 2.74 39.0 23.3 1.7 6.3 245.20 244.15 yes 15.1 LD-1C LD rock rip-rap 0.0375 2.86 41.7 24.1 1.7 5.9 244.64 243.77 yes 13.7 LD-1D LD rock rip-rap 0.0375 3.14 48.4 25.9 1.9 5.8 282.54 208.99 yes 10.3 LD-2A LD rock rip-rap 0.0375 2 24.0 18.6 1.3 5.6 134.71 133.14 yes 24.0 LD-2B LD rock rip-rap 0.0375 2.21 27.9 20.0 1.4 5.9 165.07 163.73 yes 9.5 LD-2C LD rock rip-rap 0.0375 2.09 25.6 19.2 1.3 6.5 166.02 163.69 yes 10.9 LD-2D LD rock rip-rap 0.0375 2.22 28.1 20.0 1.4 6.8 191.29 190.27 yes 9.4 Table 8: Channel Capacity - 100 year Long-Term Grassed Conditions The permissible velocity for a channel with grass lining (tall fescue), slope of 0% to 5%, and easily erodible soils is 4.5 feet per second [Ref. 3], which is greater than the calculated channel velocities for the conditions modeled. Hence, interceptor ditches, toe ditches and the diversion ditch have adequate lining stability for the conditions modeled. Longitudinal channels designed with rock rip-rap were checked for permissible shear stress, and actual flow shear as calculated using the following equation: 𝜏=𝛾𝑤𝑎𝑡𝑒𝑟𝑑𝑃 [Ref. 3] Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 12 of 13 12/9/2016 (Initial Submittal) The maximum permissible shear for rock rip-rap (d50 = 9 inch) is 3 psf [Ref. 3]. The calculated stability of the longitudinal ditches was estimated as shown in the following table: Channel ID Channel Type Channel Lining Unit Weight of Water {gwater} (pcf) Flow Depth {d} (ft) Longitudinal Slope {S} (ft/ft) Shear Stress {} (psf) Permissible Shear {perm} (psf) Safe LD-1A LD rock rip rap 62.4 2.59 0.0123 1.99 3 Yes LD-1B LD rock rip rap 62.4 2.74 0.0127 2.16 3 Yes LD-1C LD rock rip rap 62.4 2.86 0.0105 1.87 3 Yes LD-1D LD rock rip rap 62.4 3.14 0.0093 1.83 3 Yes LD-2A LD rock rip rap 62.4 2.00 0.0143 1.78 3 Yes LD-2B LD rock rip rap 62.4 2.21 0.0142 1.96 3 Yes LD-2C LD rock rip rap 62.4 2.09 0.0181 2.36 3 Yes LD-2D LD rock rip rap 62.4 2.22 0.0187 2.59 3 Yes Table 9: Channel Lining Requirements - Rock Rip-Rap (d 50 = 9 inch) The maximum particle size for the rock rip-rap lining should be greater than 1.5 times d50, i.e., 13.5 inch [Ref. 3]. Hence, NC-DOT Class 1 rock rip-rap (d50 = 10 inches, dmax = 17 inches) is proposed for the longitudinal channel lining [Ref. 4], and will be underlain with a filter fabric. 1.5 Design stormwater culverts and slope drains Culverts and slope drains will convey stormwater flows from the tributary drainage areas to the ash basin closure area. Drainage area DA-1 discharges to an existing grouted 48-inch diameter CMP which will be removed and replaced with a 48-inch diameter HDPE pipe to convey flow to a longitudinal ditch. Drainage area DA-2 discharges to an existing 54-inch RCP with a grout plug at the inlet. The 54- inch RCP connects to a drop inlet and a 36-inch diameter RCP. The existing drop inlet and 36- inch RCP will be removed and replaced with a 54-inch diameter HDPE culvert/downdrain to convey flow to a longitudinal ditch. The grout plug at the inlet of the existing 54-inch RCP will be removed to restore flow. Drainage area DA-3 discharges to an existing 36-inch diameter RCP which conveys flow into the secondary ash basin. A 36-inch diameter HDPE slope drain will be mechanically fastened to the existing 36-inch RCP to convey flow to an energy dissipater. Drainage area DA-4 discharges to an existing 36-inch diameter RCP which conveys flow into the secondary ash basin. A portion of the existing 36-inch diameter RCP will be removed. A 36-inch diameter HDPE slope drain will be mechanically fastened to the remaining portion of the existing 36-inch diameter RCP to convey flow to longitudinal ditch. Drainage area DA-8A-1 will discharge to a diversion ditch that runs along the outside perimeter road. The diversion ditch will have drop inlets placed along the bottom that discharge to slope drains which convey flow from DA-8A-1 to the ash basin. The drop inlets that will be placed in the diversion ditch will be 3’x2’x2’ deep precast concrete boxes covered by a metal grate with 2 rows of openings. Final Conditions Stormwater Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 13 of 13 12/9/2016 (Initial Submittal) The culverts and slope drains were designed using HydroCAD software as summarized in the following table: Slope Drain ID Drainage Area ID Culvert Diameter (inch) New Pipe Material Slope (ft/ft) Length (ft) Manning's n (-) Runoff - 100 year long term (cfs) Water Surface Elevation (ft) Flood Elevation (ft) Freeboard (ft) SD-1 DA-1 48 HDPE 0.02 157 0.013 186.5 522 524 2.5 SD-2 DA-2 54 HDPE 0.02 200 0.013 37.5 515 528 13.0 SD-3 DA-4 36 HDPE 0.01 577 0.013 81.3 541 558 17.0 SD-4 DA-8A-1AB 18 HDPE 0.14 100 0.013 12.24 527 528 0.7 SD-5 DA-3 36 HDPE 0.01 577 0.013 16.6 530 532 2.0 SD-6 DA-8A-1CD 18 HDPE 0.20 70 0.013 9.57 529 530 1.2 SD-7 DA-8A-1EF 18 HDPE 0.23 70 0.013 4.24 528 530 1.6 Table 11: Storm Water Culverts DISCUSSION: The proposed stormwater features have capacity for the 100-year, 24-hour design storm for the conditions modeled. FIGURES: 1. Drainage area and time of concentration 2. Land use characteristics REFERENCES: 1. Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. 2. HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. 3. North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. 4. “Standard Specification for Roads and Structures”, North Carolina Department of Transportation, Raleigh, January 2012. 5. United States Department of Agriculture, “Urban Hydrology for Small W atersheds”, Technical Release 55, June 1986. FIGURE 1 Drainage Areas and Flow Paths D R A I N A G E A R E A S A N D F L O W P A T H S 1 N I S S U E / R E V I S I O N D E S C R I P T I O N YREV D M E N G . A P P R . C L I E N T L O G O : R E V I E W E D B Y : S C A L E : D A T U M : P R O J E C T I O N : T I T L E : P R O J E C T : D A T E : F I G U R E N O . R E V I S I O N N O . P R O J E C T N O . : D R A W N B Y : C L I E N T : 2 8 0 1 Y O R K M O N T R O A D , S U I T E 1 0 0 C H A R L O T T E , N C 2 8 2 0 8 T E L : ( 7 0 4 ) 3 5 7 - 8 6 0 0 F A X : ( 7 0 4 ) 3 5 7 - 8 6 3 8 L I C E N S U R E : N C E N G : F - 1 2 5 3 N C G E O L O G Y : C - 2 4 7 A m e c F o s t e r W h e e l e r E n v i r o n m e n t & I n f r a s t r u c t u r e , I n c . 7 8 1 0 - 1 4 - 0 0 6 5 D A M D E C O M M I S S I O N I N G P L A N D A N R I V E R S T E A M S T A T I O N D U K E E N E R G Y C A R O L I N A S R O C K I N G H A M C O U N T Y , N C INITIA L S U B M I T T A L 20150 03 11 C H R K R D A S S H O W N - - - - - - C S J C H R C H R K R D 0 1 1 / 3 / 2 0 1 5 FIGURE 2 Land Use L A N D U S E 2 N I S S U E / R E V I S I O N D E S C R I P T I O N YREV D M E N G . A P P R . C L I E N T L O G O : R E V I E W E D B Y : S C A L E : D A T U M : P R O J E C T I O N : T I T L E : P R O J E C T : D A T E : F I G U R E N O . R E V I S I O N N O . P R O J E C T N O . : D R A W N B Y : C L I E N T : 2 8 0 1 Y O R K M O N T R O A D , S U I T E 1 0 0 C H A R L O T T E , N C 2 8 2 0 8 T E L : ( 7 0 4 ) 3 5 7 - 8 6 0 0 F A X : ( 7 0 4 ) 3 5 7 - 8 6 3 8 L I C E N S U R E : N C E N G : F - 1 2 5 3 N C G E O L O G Y : C - 2 4 7 A m e c F o s t e r W h e e l e r E n v i r o n m e n t & I n f r a s t r u c t u r e , I n c . 7 8 1 0 - 1 4 - 0 0 6 5 D A M D E C O M M I S S I O N I N G P L A N D A N R I V E R S T E A M S T A T I O N D U K E E N E R G Y C A R O L I N A S R O C K I N G H A M C O U N T Y , N C A S S H O W N - - - - - - C S J C H R INITIA L S U B M I T T A L 20150 03 11 C H R K R D 0 1 1 / 3 / 2 0 1 5 REFERENCE 1 Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. Precipitation Frequency Data Server Page 1 of 3 NOAA Atlas 14, Volume 2, Version 3 Location name: Eden, North Carolina, US" Latitude: 36.4999°, Longitude:-79.7013° Elevation: 582 ft* * source: Google Maps "*�,�,,.t 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 I PF graphical I Maps & aerials PF tabular PDS-based point precipitation frequency estimates with 90% confidence intervals (in inches)' Average recurrence interval (years) Duration ��� 10 25 50 100 200 500 1000 0.363 0.433 0.512 0.567 0.633 0.676 0.717 0.754 0.796 0.826 5-min (0.331-0.397) (0.396-0.473) (0.467-0.560) (0.518-0.619) (0.575-0.688) (0.612-0.735) (0.646-0.781) (0.676-0.822) (0.708-0.869) (0.729-0.902) 0.579 0.692 0.820 0.908 1.01 1.08 1.14 1.20 1.26 1.30 10-min (0 .529-0.634) (0.633-0.757) (0.749-0.898) (0.829-0.991) (0.917-1.10) (0.974-1.17) 1 (1.03-1.24) 1 (1.07-1.30) 1 (1.12-1.38) 0.724 0.870 1.04 1.15 1.28 1.36 1.44 1.51 1.59 1.63 15-min (0.661-0.792) (0.796-0.951) (0.947-1.14) 1 (1.05-1.25) 1 (1.16-1.39) 1 (1.23-1.48) 1 (1.30-1.57) 1 (1.35-1.64) 1 (1.41-1.73) 1 (1.44-1.78) 0.993 1.20 1.47 1.66 1.89 2.05 2.21 2.35 2.52 2.64 30-min (0.906-1.09) 1 (1.10-1.31) 1 (1.35-1.61) 1 (1.52-1.82) 1 (1.72-2.06) (1.86-2.23) (1.99-2.40) (2.11-2.56) (2.24-2.75) (2.33-2.89) 1.24 1.51 1.89 2.17 2.52 2.78 3.04 3.29 3.62 3.86 60-min (1.13-1.35) (1.38-1.65) (1.73-2.07) (1.98-2.36) (2.29-2.74) (2.52-3.03) (2.74-3.31) (2.95-3.59) (3.22-3.95) (3.41-4.22) 1.47 1.79 2.25 2.61 3.08 3.45 3.83 4.20 4.71 5.10 2-hr (1.35-1.61) (1.63-1.96) (2.06-2.46) (2.38-2.85) (2.80-3.36) (3.12-3.75) (3.44-4.16) (3.75-4.57) (4.15-5.12) (4.45-5.56) 1.59 1.93 2.44 2.82 3.33 3.73 4.13 4.54 5.08 5.50 3-hr (1.46-1.73) (1.78-2.11) (2.24-2.66) (2.58-3.07) (3.03-3.62) (3.38-4.04) (3.72-4.48) (4.06-4.92) ( 4.49-5.52) ( 4.81-5.98) 1.96 2.37 2.99 3.48 4.15 4.70 5.28 5.87 6.71 7.38 6-hr (1.80-2.15) (2.18-2.61) (2.74-3.27) (3.17-3.80) (3.76-4.53) (4.22-5.12) (4.70-5.73) (5.18-6.37) (5.82-7.29) (6.31-8.02) 2.36 2.87 3.63 4.26 5.15 5.89 6.70 7.56 8.81 9.84 12-hr (2.17-2.59) (2.63-3.14) (3.32-3.96) (3.88-4.62) (4.65-5.57) (5.28-6.37) (5.94-7.21) (6.62-8.12) (7.57-9.48) (8.31-10.6 ) 2.81 3.40 4.33 5.10 6.22 7.17 8.20 9.32 11.0 12.4 24-hr (2.61-3.04) (3.16-3.68) (4.02-4.67) (4.72-5.48) (5.72-6.68) (6.55-7.69) (7.44-8.79) (8.39-10.0) (9.74-11.8) (10.9-13.3) 3.30 3.99 5.04 5.90 7.12 8.13 9.21 10.4 12.0 13.4 2-day (3.08-3.55) (3.72-4.30) (4.70-5.42) (5.48-6.33) (6.59-7.63) (7.48-8.71) (8.42-9.88) (9.40-11.1 ) ( 10.8-13.0 ) ( 11.9-14.5 ) 3.49 4.22 5.33 6.23 7.52 8.59 9.72 10.9 12.7 14.2 3-day (3.26-3.76) (3.93-4.55) (4.96-5.73) (5.79-6.69) (6.95-8.07) (7.89-9.21) (8.88-10.4) (9.92-11.8) (11.4-13.7) ( 12.6-15.3) 3.68 4.45 5.61 6.56 7.92 9.04 10.2 11.5 13.4 14.9 4-day (3.43-3.97) (4.15-4.80) (5.23-6.05) (6.10-7.06) (7.32-8.51) (8.31-9.71) (9.35-11.0) (10.4-12.4) (12.0-14.4) (13.2-16.1) 4.22 5.07 6.29 7.29 8.71 9.88 11.1 12.4 14.3 15.9 7-day (3.96-4.51) (4.75-5.42) (5.89-6.72) (6.81-7.78) (8.11-9.28) (9.14-10.5) (10.2-11.9) ( 11.4-13.3) ( 12.9-15.3) ( 14.2-17.0) 4.77 5.71 7.01 8.0 6 10.7 12.0 13.3 15.1 16.6 10-day ��69.53 (4.48-5.10 ) (5.37-6.10) (6.58-7.48 ) (7.55-8.60) (8.89-10.2 ) (9.96-11.4) (11.1-12.8) (12.2-14.2) (13.8-16.2) (15.0-17.8) 6.43 7.65 9.20 10.4 12.1 13.4 14.7 16.1 17.9 19.3 20-day (6.05-6.85) (7.21-8.16) (8.66-9.81) (9.79-11.1) (11.3-12.9) (12.5-14.3) (13.7-15.7) (14.9-172) (16.4-19.2) (17.6-20.8) 30-day 7.95 9.40 11.1 12.3 14.0 15.3 16.5 17.7 19.3 20.5 (7.53-8.41) (8.91-9.94) (10.5-11.7) (11.7-13.0) (13.2-14.8) (14.4-16.2) (15.5-17.5) (16.6-18.8) (18.0-20.5) (19.0-21.9) 45-day 10.0 11.8 13.7 15.2 17.1 18.5 19.8 21.1 22.8 24.0 (9.48-10.6) (11.2-12.5) (13.0-14.5) (14.4-16.0) (16.1-18.0) (17.4-19.5) (18.6-21.0) (19.8-22.4) (21.3-24.2) (22.3-25.6) 12.0 14.0 16.1 17.7 19.7 21.2 22.6 23.9 25.6 26.8 60-day ( 114-12.6) 1 (13.4-14.8) 1 U-15-3-1-7.0) I (16.8-18.6) 1 U-18-7-2-o.7) 1 (20.0-22.3) 1 U-21-3-2-3.8) 1 (22.5-25.2) J (24.0-27.1) 11 (25.1-28.4) 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. Back to Top PF graphical http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 Precipitation Frequency Data Server Page 2 of 3 25 ....:....:.....:.....:.....:... ... .. ..... c 20 __ -. ...... --.- ... ._._. .. r. 0 15 .2 i-I 10 IL 5 0 e c_ L ry s w Ce _c c` LL M IppC N T�'1 41S r��d N ra1 yy�--�� 7 ppE 0 .i O 6 rS7Vf 30 �64.d Diratidn 30 25 L 20 5 0 1 2 5 10 25 50 100 200 500 1000 ack tR To Average recurrence interval Maps & aerials NOAA Atlas 14, Volume 2, Version 3 created tGMTI: Mon Sep 15 14:27:08 2014 Small scale terrain Washrr 'i1101"" Grvrrs•✓ l Charlottesville's Nafirt t f Fvresir% °� i ~`cIFyn hhurgU! V i r.g i n i a. Ric _61a kslwr �` Peter e 9i "Roanoke gip ortt — — - 0dnvill F-Johnson Ctierokee Navonal rvresf' >_ td 7 bonne tree sboro . �iFis❑ah<. ,.. Wiits[o sierra r-urFiam _ Large scale terrain Average recurrence interval (years) — 1 2 — S 10 25 50 100 200 500 1000 Duration — 5tnln — 2-day — Ia-Min — 3-4ay 15-mm — 4-day — 30-min — 7-4ay — Btr-cnin — 10-day — 2-11"lr — 2"ay — 34il — 30-day — "t — *15-day — 12-hr — 60-day — 24a'rr _EI http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 Precipitation Frequency Data Server Page 3 of 3 4 % cascad — �^ _ Virginia , — — — — — — -- — = yNarth Carafina — No, th C:,�, o1,all 1 e 'l) Ica i741 311 • r., 17111 17 77 ' d i MQa�l4'd 1746 �`_. E 7W 1953 � Sti t962 17dT Td76 S 4h� ,vr � 7pp Aen 1779 _ 87� H 2 km Map OpNoUilreboangie Back to Too US Department of Commerce National Oceanic and Atmospheric Administration National Weather Service Office of Hvdroloaic Develooment 1325 East West Highway Silver Spring, MD 20910 Questions?: HDSC.Questions(a)noaa.aov Disclaimer http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 REFERENCE 2 HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. 1 DA-1 S-01 DA-5A S-02 DA-5B S-03 DA-5C S-04 DA-5D S-11 DA-6A S-12 DA-6B S-13 DA-6D S-14 DA-6C S-15 DA-6E S-16 DA-6F S-17 DA-6G R-11 LD-1A R-12 LD-1B R-13 LD-1C R-15 Outlet-2 R01 Lateral Ditch R02 Outlet-1 1PCB 48" Culvert Routing Diagram for LT_1 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Runoff Area=22.679 ac 0.00% Impervious Runoff Depth>5.77"Subcatchment 1: DA-1 Flow Length=2,443' Tc=13.0 min CN=83 Runoff=186.52 cfs 10.909 af Runoff Area=3.330 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-01: DA-5A Flow Length=1,171' Tc=13.4 min CN=74 Runoff=23.07 cfs 1.313 af Runoff Area=2.130 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-02: DA-5B Flow Length=816' Tc=18.3 min CN=74 Runoff=12.69 cfs 0.839 af Runoff Area=2.830 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-03: DA-5C Flow Length=786' Tc=17.3 min CN=74 Runoff=17.37 cfs 1.115 af Runoff Area=2.180 ac 0.00% Impervious Runoff Depth>4.75"Subcatchment S-04: DA-5D Tc=5.0 min CN=74 Runoff=20.17 cfs 0.862 af Runoff Area=1.230 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-11: DA-6A Flow Length=410' Tc=15.1 min CN=74 Runoff=8.06 cfs 0.485 af Runoff Area=2.700 ac 0.00% Impervious Runoff Depth>4.74"Subcatchment S-12: DA-6B Flow Length=440' Tc=10.9 min CN=74 Runoff=20.34 cfs 1.066 af Runoff Area=2.700 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-13: DA-6D Flow Length=698' Slope=0.0150 '/' Tc=18.5 min CN=74 Runoff=15.99 cfs 1.063 af Runoff Area=2.510 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-14: DA-6C Flow Length=586' Tc=14.3 min CN=74 Runoff=16.91 cfs 0.990 af Runoff Area=3.250 ac 0.00% Impervious Runoff Depth>4.72"Subcatchment S-15: DA-6E Flow Length=876' Tc=19.6 min CN=74 Runoff=18.62 cfs 1.279 af Runoff Area=1.780 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-16: DA-6F Flow Length=537' Tc=14.1 min CN=74 Runoff=12.05 cfs 0.702 af Runoff Area=2.610 ac 0.00% Impervious Runoff Depth>4.75"Subcatchment S-17: DA-6G Tc=5.0 min CN=74 Runoff=24.15 cfs 1.032 af Avg. Flow Depth=2.50' Max Vel=6.30 fps Inflow=214.35 cfs 12.460 afReach R-11: LD-1A n=0.035 L=335.0' S=0.0123 '/' Capacity=1,495.75 cfs Outflow=213.37 cfs 12.447 af Avg. Flow Depth=2.65' Max Vel=6.60 fps Inflow=245.08 cfs 14.500 afReach R-12: LD-1B n=0.035 L=312.0' S=0.0127 '/' Capacity=599.39 cfs Outflow=244.15 cfs 14.487 af Avg. Flow Depth=2.77' Max Vel=6.16 fps Inflow=244.15 cfs 14.487 afReach R-13: LD-1C n=0.035 L=184.0' S=0.0105 '/' Capacity=545.58 cfs Outflow=243.77 cfs 14.479 af Inflow=280.99 cfs 17.492 afReach R-15: Outlet-2 Outflow=280.99 cfs 17.492 af Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Avg. Flow Depth=0.65' Max Vel=2.63 fps Inflow=35.01 cfs 2.152 afReach R01: Lateral Ditch n=0.035 L=1,177.0' S=0.0144 '/' Capacity=223.50 cfs Outflow=29.28 cfs 2.136 af Inflow=49.75 cfs 4.113 afReach R02: Outlet-1 Outflow=49.75 cfs 4.113 af Peak Elev=521.50' Inflow=186.52 cfs 10.909 afPond 1P: 48" Culvert 48.0" Round Culvert n=0.012 L=157.0' S=0.0127 '/' Outflow=186.52 cfs 10.909 af Total Runoff Area = 49.929 ac Runoff Volume = 21.656 af Average Runoff Depth = 5.20" 100.00% Pervious = 49.929 ac 0.00% Impervious = 0.000 ac Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 1: DA-1 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 186.52 cfs @ 12.04 hrs, Volume= 10.909 af, Depth> 5.77" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 0.322 73 Woods, Fair, HSG C 9.380 96 Gravel surface, HSG C 12.977 74 >75% Grass cover, Good, HSG C 22.679 83 Weighted Average 22.679 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 0.7 100 0.0670 2.30 Sheet Flow, TC for DA1 Smooth surfaces n= 0.011 P2= 3.40" 12.3 2,343 0.0390 3.18 Shallow Concentrated Flow, TC for DA1 Unpaved Kv= 16.1 fps 13.0 2,443 Total Subcatchment 1: DA-1 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 200 180 160 140 120 100 80 60 40 20 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=22.679 ac Runoff Volume=10.909 af Runoff Depth>5.77" Flow Length=2,443' Tc=13.0 min CN=83 186.52 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 5HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-01: DA-5A Runoff = 23.07 cfs @ 12.05 hrs, Volume= 1.313 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 3.330 74 >75% Grass cover, Good, HSG C 3.330 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.7 100 0.0730 0.29 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 2.7 151 0.0183 0.95 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 5.0 920 0.0134 3.10 61.92 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 Earth, dense weeds 13.4 1,171 Total Subcatchment S-01: DA-5A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 24 22 20 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=3.330 ac Runoff Volume=1.313 af Runoff Depth>4.73" Flow Length=1,171' Tc=13.4 min CN=74 23.07 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 6HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-02: DA-5B Runoff = 12.69 cfs @ 12.10 hrs, Volume= 0.839 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.130 74 >75% Grass cover, Good, HSG C 2.130 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 8.7 100 0.0250 0.19 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 5.8 288 0.0140 0.83 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 3.8 428 0.0050 1.89 37.83 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 Earth, dense weeds 18.3 816 Total Subcatchment S-02: DA-5B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.130 ac Runoff Volume=0.839 af Runoff Depth>4.73" Flow Length=816' Tc=18.3 min CN=74 12.69 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 7HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-03: DA-5C Runoff = 17.37 cfs @ 12.09 hrs, Volume= 1.115 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.830 74 >75% Grass cover, Good, HSG C 2.830 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 11.1 100 0.0136 0.15 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 3.6 218 0.0210 1.01 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 2.6 468 0.0050 3.03 47.54 Channel Flow, Area= 15.7 sf Perim= 15.5' r= 1.01' n= 0.035 Earth, dense weeds 17.3 786 Total Subcatchment S-03: DA-5C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.830 ac Runoff Volume=1.115 af Runoff Depth>4.73" Flow Length=786' Tc=17.3 min CN=74 17.37 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 8HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-04: DA-5D Runoff = 20.17 cfs @ 11.96 hrs, Volume= 0.862 af, Depth> 4.75" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.180 74 >75% Grass cover, Good, HSG C 2.180 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-04: DA-5D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 22 20 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.180 ac Runoff Volume=0.862 af Runoff Depth>4.75" Tc=5.0 min CN=74 20.17 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 9HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-11: DA-6A Runoff = 8.06 cfs @ 12.07 hrs, Volume= 0.485 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.230 74 >75% Grass cover, Good, HSG C 1.230 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 13.0 100 0.0091 0.13 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 1.3 98 0.0310 1.23 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 0.8 212 0.0290 4.55 91.09 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 Earth, dense weeds 15.1 410 Total Subcatchment S-11: DA-6A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=1.230 ac Runoff Volume=0.485 af Runoff Depth>4.73" Flow Length=410' Tc=15.1 min CN=74 8.06 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 10HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-12: DA-6B Runoff = 20.34 cfs @ 12.03 hrs, Volume= 1.066 af, Depth> 4.74" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.700 74 >75% Grass cover, Good, HSG C 2.700 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 7.8 100 0.0331 0.21 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 2.4 168 0.0270 1.15 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 0.7 172 0.0090 4.11 57.49 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 10.9 440 Total Subcatchment S-12: DA-6B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 22 20 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.700 ac Runoff Volume=1.066 af Runoff Depth>4.74" Flow Length=440' Tc=10.9 min CN=74 20.34 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 11HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-13: DA-6D Runoff = 15.99 cfs @ 12.11 hrs, Volume= 1.063 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.700 74 >75% Grass cover, Good, HSG C 2.700 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 10.7 100 0.0150 0.16 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 6.4 329 0.0150 0.86 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.4 269 0.0150 3.28 65.51 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 18.5 698 Total Subcatchment S-13: DA-6D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.700 ac Runoff Volume=1.063 af Runoff Depth>4.73" Flow Length=698' Slope=0.0150 '/' Tc=18.5 min CN=74 15.99 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 12HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-14: DA-6C Runoff = 16.91 cfs @ 12.06 hrs, Volume= 0.990 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.510 74 >75% Grass cover, Good, HSG C 2.510 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 10.1 100 0.0170 0.16 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 2.7 168 0.0226 1.05 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.5 318 0.0170 3.49 69.75 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 14.3 586 Total Subcatchment S-14: DA-6C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.510 ac Runoff Volume=0.990 af Runoff Depth>4.73" Flow Length=586' Tc=14.3 min CN=74 16.91 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 13HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-15: DA-6E Runoff = 18.62 cfs @ 12.12 hrs, Volume= 1.279 af, Depth> 4.72" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 3.250 74 >75% Grass cover, Good, HSG C 3.250 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 11.7 100 0.0120 0.14 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 3.8 224 0.0200 0.99 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 4.1 552 0.0027 2.23 34.93 Channel Flow, Area= 15.7 sf Perim= 15.5' r= 1.01' n= 0.035 19.6 876 Total Subcatchment S-15: DA-6E Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 20 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=3.250 ac Runoff Volume=1.279 af Runoff Depth>4.72" Flow Length=876' Tc=19.6 min CN=74 18.62 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 14HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-16: DA-6F Runoff = 12.05 cfs @ 12.06 hrs, Volume= 0.702 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.780 74 >75% Grass cover, Good, HSG C 1.780 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 10.1 100 0.0170 0.16 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 2.4 148 0.0210 1.01 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.6 289 0.0050 3.06 42.85 Channel Flow, Area= 14.0 sf Perim= 13.6' r= 1.03' n= 0.035 14.1 537 Total Subcatchment S-16: DA-6F Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 13 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=1.780 ac Runoff Volume=0.702 af Runoff Depth>4.73" Flow Length=537' Tc=14.1 min CN=74 12.05 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 15HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-17: DA-6G Runoff = 24.15 cfs @ 11.96 hrs, Volume= 1.032 af, Depth> 4.75" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.610 74 >75% Grass cover, Good, HSG C 2.610 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-17: DA-6G Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 25 20 15 10 5 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.610 ac Runoff Volume=1.032 af Runoff Depth>4.75" Tc=5.0 min CN=74 24.15 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 16HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-11: LD-1A Inflow Area = 26.609 ac, 0.00% Impervious, Inflow Depth > 5.62" for 100-Year event Inflow = 214.35 cfs @ 12.04 hrs, Volume= 12.460 af Outflow = 213.37 cfs @ 12.05 hrs, Volume= 12.447 af, Atten= 0%, Lag= 0.7 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 6.30 fps, Min. Travel Time= 0.9 min Avg. Velocity = 2.01 fps, Avg. Travel Time= 2.8 min Peak Storage= 11,336 cf @ 12.05 hrs Average Depth at Peak Storage= 2.50' Bank-Full Depth= 6.00' Flow Area= 144.0 sf, Capacity= 1,495.75 cfs 6.00' x 6.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 42.00' Length= 335.0' Slope= 0.0123 '/' Inlet Invert= 508.00', Outlet Invert= 503.88' Reach R-11: LD-1A Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 240 220 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=26.609 ac Avg. Flow Depth=2.50' Max Vel=6.30 fps n=0.035 L=335.0' S=0.0123 '/' Capacity=1,495.75 cfs 214.35 cfs213.37 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 17HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-12: LD-1B Inflow Area = 31.819 ac, 0.00% Impervious, Inflow Depth > 5.47" for 100-Year event Inflow = 245.08 cfs @ 12.06 hrs, Volume= 14.500 af Outflow = 244.15 cfs @ 12.07 hrs, Volume= 14.487 af, Atten= 0%, Lag= 0.6 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 6.60 fps, Min. Travel Time= 0.8 min Avg. Velocity = 2.11 fps, Avg. Travel Time= 2.5 min Peak Storage= 11,538 cf @ 12.07 hrs Average Depth at Peak Storage= 2.65' Bank-Full Depth= 4.00' Flow Area= 72.0 sf, Capacity= 599.39 cfs 6.00' x 4.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 30.00' Length= 312.0' Slope= 0.0127 '/' Inlet Invert= 503.88', Outlet Invert= 499.93' ‡ Reach R-12: LD-1B Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 250 200 150 100 50 0 Inflow Area=31.819 ac Avg. Flow Depth=2.65' Max Vel=6.60 fps n=0.035 L=312.0' S=0.0127 '/' Capacity=599.39 cfs 245.08 cfs244.15 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 18HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-13: LD-1C Inflow Area = 31.819 ac, 0.00% Impervious, Inflow Depth > 5.46" for 100-Year event Inflow = 244.15 cfs @ 12.07 hrs, Volume= 14.487 af Outflow = 243.77 cfs @ 12.07 hrs, Volume= 14.479 af, Atten= 0%, Lag= 0.4 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 6.16 fps, Min. Travel Time= 0.5 min Avg. Velocity = 1.98 fps, Avg. Travel Time= 1.5 min Peak Storage= 7,286 cf @ 12.07 hrs Average Depth at Peak Storage= 2.77' Bank-Full Depth= 4.00' Flow Area= 72.0 sf, Capacity= 545.58 cfs 6.00' x 4.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 30.00' Length= 184.0' Slope= 0.0105 '/' Inlet Invert= 499.93', Outlet Invert= 498.00' ‡ Reach R-13: LD-1C Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 250 200 150 100 50 0 Inflow Area=31.819 ac Avg. Flow Depth=2.77' Max Vel=6.16 fps n=0.035 L=184.0' S=0.0105 '/' Capacity=545.58 cfs 244.15 cfs243.77 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 19HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-15: Outlet-2 Inflow Area = 39.459 ac, 0.00% Impervious, Inflow Depth > 5.32" for 100-Year event Inflow = 280.99 cfs @ 12.07 hrs, Volume= 17.492 af Outflow = 280.99 cfs @ 12.07 hrs, Volume= 17.492 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Reach R-15: Outlet-2 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 300 250 200 150 100 50 0 Inflow Area=39.459 ac 280.99 cfs280.99 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 20HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R01: Lateral Ditch Inflow Area = 5.460 ac, 0.00% Impervious, Inflow Depth > 4.73" for 100-Year event Inflow = 35.01 cfs @ 12.07 hrs, Volume= 2.152 af Outflow = 29.28 cfs @ 12.14 hrs, Volume= 2.136 af, Atten= 16%, Lag= 4.5 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Max. Velocity= 2.63 fps, Min. Travel Time= 7.5 min Avg. Velocity = 1.03 fps, Avg. Travel Time= 19.0 min Peak Storage= 13,114 cf @ 12.14 hrs Average Depth at Peak Storage= 0.65' Bank-Full Depth= 1.50' Flow Area= 51.0 sf, Capacity= 223.50 cfs 4.00' x 1.50' deep channel, n= 0.035 Side Slope Z-value= 20.0 '/' Top Width= 64.00' Length= 1,177.0' Slope= 0.0144 '/' Inlet Invert= 514.00', Outlet Invert= 497.00' ‡ Reach R01: Lateral Ditch Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 35 30 25 20 15 10 5 0 Inflow Area=5.460 ac Avg. Flow Depth=0.65' Max Vel=2.63 fps n=0.035 L=1,177.0' S=0.0144 '/' Capacity=223.50 cfs 35.01 cfs 29.28 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 21HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R02: Outlet-1 Inflow Area = 10.470 ac, 0.00% Impervious, Inflow Depth > 4.71" for 100-Year event Inflow = 49.75 cfs @ 12.11 hrs, Volume= 4.113 af Outflow = 49.75 cfs @ 12.11 hrs, Volume= 4.113 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Reach R02: Outlet-1 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 55 50 45 40 35 30 25 20 15 10 5 0 Inflow Area=10.470 ac 49.75 cfs49.75 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 22HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 1P: 48" Culvert Inflow Area = 22.679 ac, 0.00% Impervious, Inflow Depth > 5.77" for 100-Year event Inflow = 186.52 cfs @ 12.04 hrs, Volume= 10.909 af Outflow = 186.52 cfs @ 12.04 hrs, Volume= 10.909 af, Atten= 0%, Lag= 0.0 min Primary = 186.52 cfs @ 12.04 hrs, Volume= 10.909 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Peak Elev= 521.50' @ 12.04 hrs Flood Elev= 524.00' Device Routing Invert Outlet Devices #1 Primary 510.00'48.0" Round 48" RCP Culvert L= 157.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 510.00' / 508.00' S= 0.0127 '/' Cc= 0.900 n= 0.012, Flow Area= 12.57 sf Primary OutFlow Max=186.37 cfs @ 12.04 hrs HW=521.49' TW=510.50' (Dynamic Tailwater) 1=48" RCP Culvert (Inlet Controls 186.37 cfs @ 14.83 fps) Pond 1P: 48" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=22.679 ac Peak Elev=521.50' 48.0" Round Culvert n=0.012 L=157.0' S=0.0127 '/' 186.52 cfs186.52 cfs 2 DA-2 3 DA4 4 DA-3 9S DA-8A-1A 10S DA-8A-1B 12S DA-8A-1C 13S DA-8A-1D 14S DA-8A-1E 15S DA-8A-1F 38S DA-8A-1G S-21 DA-7A S-22 DA-7B S-23 DA-7C S-24 DA-7D S-25 DA-7E S-26 DA-7F S-27 DA-7G S-41 DA-8A S-42 DA-8B S-43 DA-8DS-45 DA-8C 6R LD-4B R-21 LD-2A R-22 LD-2B R-23 LD-2C R-25 Outlet-3 R-41 LD-4A R-42 Outlet-4 2PCB 54" Slope Drain 3P 36" Slope Drain Pipe 4PCB 36" Slope Drain Pipe 16PCB 18" Culvert 17PCB 18" Culvert 18PCB 18" Culvert Routing Diagram for LT_2 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points x 2 Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Runoff Area=6.060 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment 2: DA-2 Flow Length=852' Tc=17.0 min CN=74 Runoff=37.45 cfs 2.387 af Runoff Area=71.320 ac 0.00% Impervious Runoff Depth>5.29"Subcatchment 3: DA4 Flow Length=4,921' Tc=23.4 min CN=79 Runoff=407.62 cfs 31.447 af Runoff Area=2.385 ac 0.00% Impervious Runoff Depth>4.62"Subcatchment 4: DA-3 Flow Length=765' Tc=12.6 min CN=73 Runoff=16.60 cfs 0.918 af Runoff Area=0.620 ac 0.00% Impervious Runoff Depth>4.74"Subcatchment 9S: DA-8A-1A Tc=6.0 min CN=74 Runoff=5.54 cfs 0.245 af Runoff Area=0.750 ac 0.00% Impervious Runoff Depth>4.74"Subcatchment 10S: DA-8A-1B Tc=6.0 min CN=74 Runoff=6.70 cfs 0.297 af Runoff Area=0.130 ac 0.00% Impervious Runoff Depth>4.74"Subcatchment 12S: DA-8A-1C Tc=6.0 min CN=74 Runoff=1.16 cfs 0.051 af Runoff Area=1.240 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment 13S: DA-8A-1D Flow Length=676' Tc=12.7 min CN=74 Runoff=8.79 cfs 0.489 af Runoff Area=0.290 ac 0.00% Impervious Runoff Depth>4.75"Subcatchment 14S: DA-8A-1E Tc=0.0 min CN=74 Runoff=3.14 cfs 0.115 af Runoff Area=0.170 ac 0.00% Impervious Runoff Depth>4.74"Subcatchment 15S: DA-8A-1F Tc=6.0 min CN=74 Runoff=1.52 cfs 0.067 af Runoff Area=0.350 ac 0.00% Impervious Runoff Depth>4.74"Subcatchment 38S: DA-8A-1G Tc=6.0 min CN=74 Runoff=3.13 cfs 0.138 af Runoff Area=4.350 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-21: DA-7A Flow Length=879' Tc=18.1 min CN=74 Runoff=26.01 cfs 1.713 af Runoff Area=1.610 ac 0.00% Impervious Runoff Depth>4.75"Subcatchment S-22: DA-7B Tc=5.0 min CN=74 Runoff=14.90 cfs 0.637 af Runoff Area=2.480 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-23: DA-7C Flow Length=571' Tc=15.6 min CN=74 Runoff=16.03 cfs 0.978 af Runoff Area=2.650 ac 0.00% Impervious Runoff Depth>4.72"Subcatchment S-24: DA-7D Flow Length=618' Tc=19.0 min CN=74 Runoff=15.43 cfs 1.043 af Runoff Area=1.640 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-25: DA-7E Flow Length=528' Tc=13.8 min CN=74 Runoff=11.21 cfs 0.647 af Runoff Area=3.000 ac 0.00% Impervious Runoff Depth>4.71"Subcatchment S-26: DA-7F Flow Length=1,030' Tc=26.4 min CN=74 Runoff=14.40 cfs 1.178 af Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Runoff Area=2.260 ac 0.00% Impervious Runoff Depth>4.75"Subcatchment S-27: DA-7G Tc=5.0 min CN=74 Runoff=20.91 cfs 0.894 af Runoff Area=4.740 ac 0.00% Impervious Runoff Depth>4.73"Subcatchment S-41: DA-8A Flow Length=1,457' Tc=15.4 min CN=74 Runoff=30.78 cfs 1.868 af Runoff Area=2.890 ac 0.00% Impervious Runoff Depth>4.72"Subcatchment S-42: DA-8B Flow Length=916' Tc=22.1 min CN=74 Runoff=15.49 cfs 1.137 af Runoff Area=1.770 ac 0.00% Impervious Runoff Depth>4.75"Subcatchment S-43: DA-8D Tc=5.0 min CN=74 Runoff=16.38 cfs 0.700 af Runoff Area=1.480 ac 0.00% Impervious Runoff Depth>4.72"Subcatchment S-45: DA-8C Flow Length=725' Tc=19.3 min CN=74 Runoff=8.56 cfs 0.583 af Inflow=70.33 cfs 5.289 afReach 6R: LD-4B Outflow=70.33 cfs 5.289 af Avg. Flow Depth=1.92' Max Vel=5.87 fps Inflow=133.30 cfs 36.146 afReach R-21: LD-2A n=0.035 L=282.0' S=0.0143 '/' Capacity=636.03 cfs Outflow=133.14 cfs 36.124 af Avg. Flow Depth=2.13' Max Vel=6.20 fps Inflow=163.94 cfs 38.145 afReach R-22: LD-2B n=0.035 L=306.0' S=0.0142 '/' Capacity=336.93 cfs Outflow=163.73 cfs 38.120 af Avg. Flow Depth=1.91' Max Vel=7.28 fps Inflow=163.73 cfs 38.120 afReach R-23: LD-2C n=0.035 L=165.0' S=0.0221 '/' Capacity=420.20 cfs Outflow=163.69 cfs 38.109 af Inflow=190.27 cfs 40.828 afReach R-25: Outlet-3 Outflow=190.27 cfs 40.828 af Avg. Flow Depth=0.86' Max Vel=2.74 fps Inflow=67.72 cfs 4.189 afReach R-41: LD-4A n=0.035 L=1,410.0' S=0.0106 '/' Capacity=77.78 cfs Outflow=55.22 cfs 4.152 af Inflow=81.99 cfs 6.571 afReach R-42: Outlet-4 Outflow=81.99 cfs 6.571 af Peak Elev=514.15' Inflow=37.45 cfs 2.387 afPond 2P: 54" Slope Drain 54.0" Round Culvert n=0.012 L=90.0' S=0.0222 '/' Outflow=37.45 cfs 2.387 af Peak Elev=541.31' Storage=513,893 cf Inflow=407.62 cfs 31.447 afPond 3P: 36" Slope Drain Pipe Outflow=81.28 cfs 31.408 af Peak Elev=530.54' Inflow=16.60 cfs 0.918 afPond 4P: 36" Slope Drain Pipe 36.0" Round Culvert n=0.013 L=150.0' S=0.1263 '/' Outflow=16.60 cfs 0.918 af Peak Elev=527.34' Inflow=12.24 cfs 0.542 afPond 16P: 18" Culvert Outflow=12.24 cfs 0.542 af Peak Elev=528.82' Inflow=9.57 cfs 0.541 afPond 17P: 18" Culvert Outflow=9.57 cfs 0.541 af Peak Elev=528.26' Inflow=4.24 cfs 0.182 afPond 18P: 18" Culvert Outflow=4.24 cfs 0.182 af Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Total Runoff Area = 112.185 ac Runoff Volume = 47.533 af Average Runoff Depth = 5.08" 100.00% Pervious = 112.185 ac 0.00% Impervious = 0.000 ac Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 5HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 2: DA-2 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 37.45 cfs @ 12.09 hrs, Volume= 2.387 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.555 73 Woods, Fair, HSG C 0.140 96 Gravel surface, HSG C 4.365 74 >75% Grass cover, Good, HSG C 6.060 74 Weighted Average 6.060 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.6 100 0.0500 0.25 Sheet Flow, TC for DA2 Grass: Short n= 0.150 P2= 3.40" 10.4 752 0.0580 1.20 Shallow Concentrated Flow, TC for DA2 Woodland Kv= 5.0 fps 17.0 852 Total Subcatchment 2: DA-2 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 40 35 30 25 20 15 10 5 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=6.060 ac Runoff Volume=2.387 af Runoff Depth>4.73" Flow Length=852' Tc=17.0 min CN=74 37.45 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 6HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 3: DA4 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 407.62 cfs @ 12.16 hrs, Volume= 31.447 af, Depth> 5.29" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 9.930 73 Woods, Fair, HSG C 15.051 96 Gravel surface, HSG C 46.339 74 >75% Grass cover, Good, HSG C 71.320 79 Weighted Average 71.320 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 7.0 100 0.0430 0.24 Sheet Flow, TC for DA4 Grass: Short n= 0.150 P2= 3.40" 13.1 2,834 0.0580 3.61 Shallow Concentrated Flow, TC for DA4 Grassed Waterway Kv= 15.0 fps 3.3 1,987 10.00 Direct Entry, TC for DA4 23.4 4,921 Total Subcatchment 3: DA4 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 450 400 350 300 250 200 150 100 50 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=71.320 ac Runoff Volume=31.447 af Runoff Depth>5.29" Flow Length=4,921' Tc=23.4 min CN=79 407.62 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 7HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 4: DA-3 I am not going to consider channel flow in this scenerio to more closely reflect insitu circumstances. Runoff = 16.60 cfs @ 12.04 hrs, Volume= 0.918 af, Depth> 4.62" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.260 73 Woods, Fair, HSG C 0.000 96 Gravel surface, HSG C 1.125 74 >75% Grass cover, Good, HSG C 2.385 73 Weighted Average 2.385 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.6 100 0.0740 0.30 Sheet Flow, TC for DA3 Grass: Short n= 0.150 P2= 3.40" 7.0 665 0.0511 1.58 Shallow Concentrated Flow, TC for DA3 Short Grass Pasture Kv= 7.0 fps 12.6 765 Total Subcatchment 4: DA-3 Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.385 ac Runoff Volume=0.918 af Runoff Depth>4.62" Flow Length=765' Tc=12.6 min CN=73 16.60 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 8HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 9S: DA-8A-1A Runoff = 5.54 cfs @ 11.97 hrs, Volume= 0.245 af, Depth> 4.74" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description * 0.620 74 0.620 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 9S: DA-8A-1A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 6 5 4 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=0.620 ac Runoff Volume=0.245 af Runoff Depth>4.74" Tc=6.0 min CN=74 5.54 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 9HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 10S: DA-8A-1B Runoff = 6.70 cfs @ 11.97 hrs, Volume= 0.297 af, Depth> 4.74" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description * 0.750 74 0.750 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 10S: DA-8A-1B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 7 6 5 4 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=0.750 ac Runoff Volume=0.297 af Runoff Depth>4.74" Tc=6.0 min CN=74 6.70 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 10HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 12S: DA-8A-1C Runoff = 1.16 cfs @ 11.97 hrs, Volume= 0.051 af, Depth> 4.74" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description * 0.130 74 0.130 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 12S: DA-8A-1C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=0.130 ac Runoff Volume=0.051 af Runoff Depth>4.74" Tc=6.0 min CN=74 1.16 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 11HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 13S: DA-8A-1D Runoff = 8.79 cfs @ 12.04 hrs, Volume= 0.489 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description * 1.240 74 1.240 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 3.8 100 0.2000 0.44 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 8.9 576 0.0240 1.08 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 12.7 676 Total Subcatchment 13S: DA-8A-1D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=1.240 ac Runoff Volume=0.489 af Runoff Depth>4.73" Flow Length=676' Tc=12.7 min CN=74 8.79 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 12HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 14S: DA-8A-1E Runoff = 3.14 cfs @ 11.90 hrs, Volume= 0.115 af, Depth> 4.75" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description * 0.290 74 0.290 100.00% Pervious Area Subcatchment 14S: DA-8A-1E Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=0.290 ac Runoff Volume=0.115 af Runoff Depth>4.75" Tc=0.0 min CN=74 3.14 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 13HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 15S: DA-8A-1F Runoff = 1.52 cfs @ 11.97 hrs, Volume= 0.067 af, Depth> 4.74" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description * 0.170 74 0.170 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 15S: DA-8A-1F Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=0.170 ac Runoff Volume=0.067 af Runoff Depth>4.74" Tc=6.0 min CN=74 1.52 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 14HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment 38S: DA-8A-1G Runoff = 3.13 cfs @ 11.97 hrs, Volume= 0.138 af, Depth> 4.74" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description * 0.350 74 0.350 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 6.0 Direct Entry, Subcatchment 38S: DA-8A-1G Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=0.350 ac Runoff Volume=0.138 af Runoff Depth>4.74" Tc=6.0 min CN=74 3.13 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 15HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-21: DA-7A Runoff = 26.01 cfs @ 12.10 hrs, Volume= 1.713 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 4.350 74 >75% Grass cover, Good, HSG C 4.350 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.7 100 0.0720 0.29 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 11.2 534 0.0130 0.80 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.2 245 0.0160 3.38 67.66 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 18.1 879 Total Subcatchment S-21: DA-7A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 25 20 15 10 5 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=4.350 ac Runoff Volume=1.713 af Runoff Depth>4.73" Flow Length=879' Tc=18.1 min CN=74 26.01 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 16HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-22: DA-7B Runoff = 14.90 cfs @ 11.96 hrs, Volume= 0.637 af, Depth> 4.75" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.610 74 >75% Grass cover, Good, HSG C 1.610 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-22: DA-7B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=1.610 ac Runoff Volume=0.637 af Runoff Depth>4.75" Tc=5.0 min CN=74 14.90 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 17HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-23: DA-7C Runoff = 16.03 cfs @ 12.08 hrs, Volume= 0.978 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.480 74 >75% Grass cover, Good, HSG C 2.480 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 10.5 100 0.0155 0.16 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 3.5 226 0.0242 1.09 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.6 245 0.0090 2.54 50.75 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 15.6 571 Total Subcatchment S-23: DA-7C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.480 ac Runoff Volume=0.978 af Runoff Depth>4.73" Flow Length=571' Tc=15.6 min CN=74 16.03 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 18HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-24: DA-7D Runoff = 15.43 cfs @ 12.11 hrs, Volume= 1.043 af, Depth> 4.72" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.650 74 >75% Grass cover, Good, HSG C 2.650 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 12.3 100 0.0106 0.14 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 5.1 277 0.0170 0.91 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.6 241 0.0090 2.54 50.75 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 19.0 618 Total Subcatchment S-24: DA-7D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.650 ac Runoff Volume=1.043 af Runoff Depth>4.72" Flow Length=618' Tc=19.0 min CN=74 15.43 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 19HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-25: DA-7E Runoff = 11.21 cfs @ 12.06 hrs, Volume= 0.647 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.640 74 >75% Grass cover, Good, HSG C 1.640 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 9.9 100 0.0181 0.17 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 2.3 139 0.0213 1.02 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.6 289 0.0050 3.03 47.54 Channel Flow, Area= 15.7 sf Perim= 15.5' r= 1.01' n= 0.035 13.8 528 Total Subcatchment S-25: DA-7E Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 12 11 10 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=1.640 ac Runoff Volume=0.647 af Runoff Depth>4.73" Flow Length=528' Tc=13.8 min CN=74 11.21 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 20HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-26: DA-7F Runoff = 14.40 cfs @ 12.20 hrs, Volume= 1.178 af, Depth> 4.71" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 3.000 74 >75% Grass cover, Good, HSG C 3.000 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 10.2 100 0.0166 0.16 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 13.3 498 0.0080 0.63 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 2.9 432 0.0035 2.51 39.44 Channel Flow, Area= 15.7 sf Perim= 15.7' r= 1.00' n= 0.035 26.4 1,030 Total Subcatchment S-26: DA-7F Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=3.000 ac Runoff Volume=1.178 af Runoff Depth>4.71" Flow Length=1,030' Tc=26.4 min CN=74 14.40 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 21HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-27: DA-7G Runoff = 20.91 cfs @ 11.96 hrs, Volume= 0.894 af, Depth> 4.75" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.260 74 >75% Grass cover, Good, HSG C 2.260 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-27: DA-7G Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 22 20 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.260 ac Runoff Volume=0.894 af Runoff Depth>4.75" Tc=5.0 min CN=74 20.91 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 22HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-41: DA-8A Runoff = 30.78 cfs @ 12.07 hrs, Volume= 1.868 af, Depth> 4.73" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 4.740 74 >75% Grass cover, Good, HSG C 4.740 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 100 0.1000 0.33 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 7.3 695 0.0520 1.60 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 3.1 662 0.0180 3.59 71.77 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 15.4 1,457 Total Subcatchment S-41: DA-8A Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 30 25 20 15 10 5 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=4.740 ac Runoff Volume=1.868 af Runoff Depth>4.73" Flow Length=1,457' Tc=15.4 min CN=74 30.78 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 23HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-42: DA-8B Runoff = 15.49 cfs @ 12.15 hrs, Volume= 1.137 af, Depth> 4.72" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 2.890 74 >75% Grass cover, Good, HSG C 2.890 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 12.3 100 0.0104 0.13 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 4.2 252 0.0204 1.00 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 5.6 564 0.0040 1.69 33.83 Channel Flow, Area= 20.0 sf Perim= 40.0' r= 0.50' n= 0.035 22.1 916 Total Subcatchment S-42: DA-8B Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=2.890 ac Runoff Volume=1.137 af Runoff Depth>4.72" Flow Length=916' Tc=22.1 min CN=74 15.49 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 24HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-43: DA-8D Runoff = 16.38 cfs @ 11.96 hrs, Volume= 0.700 af, Depth> 4.75" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.770 74 >75% Grass cover, Good, HSG C 1.770 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 5.0 Direct Entry, Subcatchment S-43: DA-8D Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 18 16 14 12 10 8 6 4 2 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=1.770 ac Runoff Volume=0.700 af Runoff Depth>4.75" Tc=5.0 min CN=74 16.38 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 25HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Subcatchment S-45: DA-8C Runoff = 8.56 cfs @ 12.12 hrs, Volume= 0.583 af, Depth> 4.72" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Type II 24-hr 100-Year Rainfall=8.20" Area (ac) CN Description 1.480 74 >75% Grass cover, Good, HSG C 1.480 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 10.9 100 0.0143 0.15 Sheet Flow, Grass: Short n= 0.150 P2= 3.40" 6.7 320 0.0130 0.80 Shallow Concentrated Flow, Short Grass Pasture Kv= 7.0 fps 1.7 305 0.0050 3.03 47.54 Channel Flow, Area= 15.7 sf Perim= 15.5' r= 1.01' n= 0.035 19.3 725 Total Subcatchment S-45: DA-8C Runoff Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 9 8 7 6 5 4 3 2 1 0 Type II 24-hr 100-Year Rainfall=8.20" Runoff Area=1.480 ac Runoff Volume=0.583 af Runoff Depth>4.72" Flow Length=725' Tc=19.3 min CN=74 8.56 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 26HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach 6R: LD-4B Inflow Area = 13.565 ac, 0.00% Impervious, Inflow Depth > 4.68" for 100-Year event Inflow = 70.33 cfs @ 12.12 hrs, Volume= 5.289 af Outflow = 70.33 cfs @ 12.12 hrs, Volume= 5.289 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Reach 6R: LD-4B Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 70 60 50 40 30 20 10 0 Inflow Area=13.565 ac 70.33 cfs70.33 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 27HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-21: LD-2A Inflow Area = 83.340 ac, 0.00% Impervious, Inflow Depth > 5.20" for 100-Year event Inflow = 133.30 cfs @ 12.11 hrs, Volume= 36.146 af Outflow = 133.14 cfs @ 12.12 hrs, Volume= 36.124 af, Atten= 0%, Lag= 0.5 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Max. Velocity= 5.87 fps, Min. Travel Time= 0.8 min Avg. Velocity = 3.19 fps, Avg. Travel Time= 1.5 min Peak Storage= 6,392 cf @ 12.12 hrs Average Depth at Peak Storage= 1.92' Bank-Full Depth= 4.00' Flow Area= 72.0 sf, Capacity= 636.03 cfs 6.00' x 4.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 30.00' Length= 282.0' Slope= 0.0143 '/' Inlet Invert= 510.00', Outlet Invert= 505.98' ‡ Reach R-21: LD-2A Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 140 120 100 80 60 40 20 0 Inflow Area=83.340 ac Avg. Flow Depth=1.92' Max Vel=5.87 fps n=0.035 L=282.0' S=0.0143 '/' Capacity=636.03 cfs 133.30 cfs133.14 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 28HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-22: LD-2B Inflow Area = 88.470 ac, 0.00% Impervious, Inflow Depth > 5.17" for 100-Year event Inflow = 163.94 cfs @ 12.11 hrs, Volume= 38.145 af Outflow = 163.73 cfs @ 12.12 hrs, Volume= 38.120 af, Atten= 0%, Lag= 0.6 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Max. Velocity= 6.20 fps, Min. Travel Time= 0.8 min Avg. Velocity = 3.23 fps, Avg. Travel Time= 1.6 min Peak Storage= 8,087 cf @ 12.12 hrs Average Depth at Peak Storage= 2.13' Bank-Full Depth= 3.00' Flow Area= 45.0 sf, Capacity= 336.93 cfs 6.00' x 3.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 24.00' Length= 306.0' Slope= 0.0142 '/' Inlet Invert= 505.98', Outlet Invert= 501.64' ‡ Reach R-22: LD-2B Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 180 160 140 120 100 80 60 40 20 0 Inflow Area=88.470 ac Avg. Flow Depth=2.13' Max Vel=6.20 fps n=0.035 L=306.0' S=0.0142 '/' Capacity=336.93 cfs 163.94 cfs163.73 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 29HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-23: LD-2C Inflow Area = 88.470 ac, 0.00% Impervious, Inflow Depth > 5.17" for 100-Year event Inflow = 163.73 cfs @ 12.12 hrs, Volume= 38.120 af Outflow = 163.69 cfs @ 12.12 hrs, Volume= 38.109 af, Atten= 0%, Lag= 0.3 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Max. Velocity= 7.28 fps, Min. Travel Time= 0.4 min Avg. Velocity = 3.77 fps, Avg. Travel Time= 0.7 min Peak Storage= 3,708 cf @ 12.12 hrs Average Depth at Peak Storage= 1.91' Bank-Full Depth= 3.00' Flow Area= 45.0 sf, Capacity= 420.20 cfs 6.00' x 3.00' deep channel, n= 0.035 Side Slope Z-value= 3.0 '/' Top Width= 24.00' Length= 165.0' Slope= 0.0221 '/' Inlet Invert= 501.64', Outlet Invert= 498.00' ‡ Reach R-23: LD-2C Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 180 160 140 120 100 80 60 40 20 0 Inflow Area=88.470 ac Avg. Flow Depth=1.91' Max Vel=7.28 fps n=0.035 L=165.0' S=0.0221 '/' Capacity=420.20 cfs 163.73 cfs163.69 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 30HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-25: Outlet-3 Inflow Area = 95.370 ac, 0.00% Impervious, Inflow Depth > 5.14" for 100-Year event Inflow = 190.27 cfs @ 12.11 hrs, Volume= 40.828 af Outflow = 190.27 cfs @ 12.11 hrs, Volume= 40.828 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Reach R-25: Outlet-3 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=95.370 ac 190.27 cfs190.27 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 31HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-41: LD-4A Inflow Area = 10.675 ac, 0.00% Impervious, Inflow Depth > 4.71" for 100-Year event Inflow = 67.72 cfs @ 12.03 hrs, Volume= 4.189 af Outflow = 55.22 cfs @ 12.11 hrs, Volume= 4.152 af, Atten= 18%, Lag= 5.1 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Max. Velocity= 2.74 fps, Min. Travel Time= 8.6 min Avg. Velocity = 1.07 fps, Avg. Travel Time= 22.0 min Peak Storage= 28,390 cf @ 12.11 hrs Average Depth at Peak Storage= 0.86' Bank-Full Depth= 1.00' Flow Area= 26.0 sf, Capacity= 77.78 cfs 6.00' x 1.00' deep channel, n= 0.035 Side Slope Z-value= 20.0 '/' Top Width= 46.00' Length= 1,410.0' Slope= 0.0106 '/' Inlet Invert= 512.00', Outlet Invert= 497.00' ‡ Reach R-41: LD-4A Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 70 60 50 40 30 20 10 0 Inflow Area=10.675 ac Avg. Flow Depth=0.86' Max Vel=2.74 fps n=0.035 L=1,410.0' S=0.0106 '/' Capacity=77.78 cfs 67.72 cfs 55.22 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 32HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-42: Outlet-4 Inflow Area = 16.815 ac, 0.00% Impervious, Inflow Depth > 4.69" for 100-Year event Inflow = 81.99 cfs @ 12.11 hrs, Volume= 6.571 af Outflow = 81.99 cfs @ 12.11 hrs, Volume= 6.571 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Reach R-42: Outlet-4 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 90 80 70 60 50 40 30 20 10 0 Inflow Area=16.815 ac 81.99 cfs81.99 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 33HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 2P: 54" Slope Drain Inflow Area = 6.060 ac, 0.00% Impervious, Inflow Depth > 4.73" for 100-Year event Inflow = 37.45 cfs @ 12.09 hrs, Volume= 2.387 af Outflow = 37.45 cfs @ 12.09 hrs, Volume= 2.387 af, Atten= 0%, Lag= 0.0 min Primary = 37.45 cfs @ 12.09 hrs, Volume= 2.387 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Peak Elev= 514.15' @ 12.09 hrs Flood Elev= 528.00' Device Routing Invert Outlet Devices #1 Primary 512.00'54.0" Round Culvert L= 90.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 512.00' / 510.00' S= 0.0222 '/' Cc= 0.900 n= 0.012, Flow Area= 15.90 sf Primary OutFlow Max=37.44 cfs @ 12.09 hrs HW=514.15' TW=511.92' (Dynamic Tailwater) 1=Culvert (Inlet Controls 37.44 cfs @ 4.99 fps) Pond 2P: 54" Slope Drain Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 40 35 30 25 20 15 10 5 0 Inflow Area=6.060 ac Peak Elev=514.15' 54.0" Round Culvert n=0.012 L=90.0' S=0.0222 '/' 37.45 cfs37.45 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 34HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 3P: 36" Slope Drain Pipe Inflow Area = 71.320 ac, 0.00% Impervious, Inflow Depth > 5.29" for 100-Year event Inflow = 407.62 cfs @ 12.16 hrs, Volume= 31.447 af Outflow = 81.28 cfs @ 12.70 hrs, Volume= 31.408 af, Atten= 80%, Lag= 32.7 min Primary = 81.28 cfs @ 12.70 hrs, Volume= 31.408 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Peak Elev= 541.31' @ 12.70 hrs Surf.Area= 124,068 sf Storage= 513,893 cf Plug-Flow detention time= 51.3 min calculated for 31.393 af (100% of inflow) Center-of-Mass det. time= 50.7 min ( 829.2 - 778.5 ) Volume Invert Avail.Storage Storage Description #1 535.00' 2,237,064 cf Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (sq-ft) (cubic-feet) (cubic-feet) 535.00 0 0 0 536.00 58,048 29,024 29,024 541.00 120,747 446,988 476,012 546.00 174,399 737,865 1,213,877 551.00 234,876 1,023,188 2,237,064 Device Routing Invert Outlet Devices #1 Primary 528.50'36.0" Round Culvert L= 207.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 528.50' / 510.00' S= 0.0894 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 7.07 sf #2 Device 1 530.00'36.0" Round Culvert L= 530.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 530.00' / 528.50' S= 0.0028 '/' Cc= 0.900 n= 0.012 Concrete pipe, finished, Flow Area= 7.07 sf #3 Device 2 535.00'60.0" x 60.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=81.28 cfs @ 12.70 hrs HW=541.31' TW=511.59' (Dynamic Tailwater) 1=Culvert (Passes 81.28 cfs of 114.46 cfs potential flow) 2=Culvert (Barrel Controls 81.28 cfs @ 11.50 fps) 3=Orifice/Grate (Passes 81.28 cfs of 302.36 cfs potential flow) Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 35HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 3P: 36" Slope Drain Pipe Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 450 400 350 300 250 200 150 100 50 0 Inflow Area=71.320 ac Peak Elev=541.31' Storage=513,893 cf 407.62 cfs 81.28 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 36HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 4P: 36" Slope Drain Pipe Inflow Area = 2.385 ac, 0.00% Impervious, Inflow Depth > 4.62" for 100-Year event Inflow = 16.60 cfs @ 12.04 hrs, Volume= 0.918 af Outflow = 16.60 cfs @ 12.04 hrs, Volume= 0.918 af, Atten= 0%, Lag= 0.0 min Primary = 16.60 cfs @ 12.04 hrs, Volume= 0.918 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Peak Elev= 530.54' @ 12.04 hrs Flood Elev= 532.00' Device Routing Invert Outlet Devices #1 Primary 528.94'36.0" Round Culvert L= 150.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 528.94' / 510.00' S= 0.1263 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 7.07 sf Primary OutFlow Max=16.59 cfs @ 12.04 hrs HW=530.54' TW=512.83' (Dynamic Tailwater) 1=Culvert (Inlet Controls 16.59 cfs @ 4.31 fps) Pond 4P: 36" Slope Drain Pipe Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 18 16 14 12 10 8 6 4 2 0 Inflow Area=2.385 ac Peak Elev=530.54' 36.0" Round Culvert n=0.013 L=150.0' S=0.1263 '/' 16.60 cfs16.60 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 37HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 16P: 18" Culvert Inflow Area = 1.370 ac, 0.00% Impervious, Inflow Depth > 4.74" for 100-Year event Inflow = 12.24 cfs @ 11.97 hrs, Volume= 0.542 af Outflow = 12.24 cfs @ 11.97 hrs, Volume= 0.542 af, Atten= 0%, Lag= 0.0 min Primary = 12.24 cfs @ 11.97 hrs, Volume= 0.542 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Peak Elev= 527.34' @ 11.97 hrs Flood Elev= 528.00' Device Routing Invert Outlet Devices #1 Primary 524.00'18.0" Round Culvert L= 100.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 524.00' / 510.00' S= 0.1400 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 1.77 sf #2 Device 1 526.00'24.0" x 36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Device 2 526.00'1.2" x 16.5" Horiz. Orifice/Grate X 2.00 columns X 8 rows C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=12.23 cfs @ 11.97 hrs HW=527.33' TW=512.71' (Dynamic Tailwater) 1=Culvert (Passes 12.23 cfs of 13.67 cfs potential flow) 2=Orifice/Grate (Passes 12.23 cfs of 33.34 cfs potential flow) 3=Orifice/Grate (Orifice Controls 12.23 cfs @ 5.56 fps) Pond 16P: 18" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 12 10 8 6 4 2 0 Inflow Area=1.370 ac Peak Elev=527.34' 12.24 cfs12.24 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 38HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 17P: 18" Culvert Inflow Area = 1.370 ac, 0.00% Impervious, Inflow Depth > 4.74" for 100-Year event Inflow = 9.57 cfs @ 12.03 hrs, Volume= 0.541 af Outflow = 9.57 cfs @ 12.03 hrs, Volume= 0.541 af, Atten= 0%, Lag= 0.0 min Primary = 9.57 cfs @ 12.03 hrs, Volume= 0.541 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Peak Elev= 528.82' @ 12.03 hrs Flood Elev= 530.00' Device Routing Invert Outlet Devices #1 Device 2 528.00'24.0" x 36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #2 Primary 526.00'18.0" Round Culvert L= 70.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 526.00' / 512.00' S= 0.2000 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 1.77 sf #3 Device 1 528.00'1.2" x 16.5" Horiz. Orifice/Grate X 2.00 columns X 8 rows C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=9.56 cfs @ 12.03 hrs HW=528.81' TW=512.82' (Dynamic Tailwater) 2=Culvert (Passes 9.56 cfs of 12.23 cfs potential flow) 1=Orifice/Grate (Passes 9.56 cfs of 24.04 cfs potential flow) 3=Orifice/Grate (Orifice Controls 9.56 cfs @ 4.35 fps) Pond 17P: 18" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 10 9 8 7 6 5 4 3 2 1 0 Inflow Area=1.370 ac Peak Elev=528.82' 9.57 cfs9.57 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 39HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 18P: 18" Culvert Inflow Area = 0.460 ac, 0.00% Impervious, Inflow Depth > 4.75" for 100-Year event Inflow = 4.24 cfs @ 11.90 hrs, Volume= 0.182 af Outflow = 4.24 cfs @ 11.90 hrs, Volume= 0.182 af, Atten= 0%, Lag= 0.0 min Primary = 4.24 cfs @ 11.90 hrs, Volume= 0.182 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Peak Elev= 528.26' @ 11.90 hrs Flood Elev= 530.00' Device Routing Invert Outlet Devices #1 Device 2 528.00'24.0" x 36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #2 Primary 526.00'18.0" Round Culvert L= 70.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 526.00' / 510.00' S= 0.2286 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 1.77 sf #3 Device 1 528.00'1.2" x 16.5" Horiz. Orifice/Grate X 2.00 columns X 8 rows C= 0.600 Limited to weir flow at low heads Primary OutFlow Max=4.23 cfs @ 11.90 hrs HW=528.26' TW=512.58' (Dynamic Tailwater) 2=Culvert (Passes 4.23 cfs of 10.44 cfs potential flow) 1=Orifice/Grate (Weir Controls 4.23 cfs @ 1.65 fps) 3=Orifice/Grate (Passes 4.23 cfs of 5.36 cfs potential flow) Pond 18P: 18" Culvert Inflow Primary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 4 3 2 1 0 Inflow Area=0.460 ac Peak Elev=528.26' 4.24 cfs4.24 cfs REFERENCE 3 North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. Appendices This section addresses the design of stable conveyance channels and diversions using flexible linings. A stable channel is defined as a channel which is nonsilting and nonscouring. To minimize silting in the channel, flow velocities should remain constant or increase slightly throughout the channel length. This is especially important in designing diversion channels and can be accomplished by adjusting channel grade. Procedures presented in this section address the problems of erosion and scour. More advanced procedures for permanent, unlined channels may be found elsewhere. (References: Garde and Ranga Raju, 1980) Diversions are channels usually with a supporting ridge on the lower side. They are generally located to divert flows across a slope and are designed following the same procedures as other channels. Design tables for vegetated diversions and waterways are included at the end of this section. Flexible channel linings are generally preferred to rigid linings from an erosion control standpoint because they conform to changes in channel shape without failure and are less susceptible to damage from frost heaving, soil swelling and shrinking, and excessive soil pore water pressure from lack of drainage. Flexible linings also are generally less expensive to construct, and when vegetated, are more natural in appearance. On the other hand, flexible linings generally have higher roughness and require a larger cross section for the same discharge. EROSION CONtROL CRItERIa The minimum design criteria for conveyance channels require that two primary conditions be satisfied: the channel system must have capacity for the peak flow expected from the 10-year storm and the channel lining must be resistant to erosion for the design velocity. In some cases, out-of-bank flow may be considered a functional part of the channel system. In these cases, flow capacities and design velocities should be considered separately for out- of-bank flows and channel flows. Both the capacity of the channel and the velocity of flow are functions of the channel lining, cross-sectional area and slope. The channel system must carry the design flow, fit site conditions, and be stable. Sta BLE CHaNNEL DESIGN mEtHODS Two accepted procedures for designing stable channels with flexible linings are: (1) the permissible velocity approach; and (2) the tractive force approach. Under the permissible velocity approach, the channel is considered stable if the design, mean velocity is lower than the maximum permissible velocity. Under the tractive force approach, erosive stress evaluated at the boundary between flowing water and lining materials must be less than the minimum unit tractive force that will cause serious erosion of material from a level channel bed. 8.05 DESIGN Of Sta BLE CHaNNELS aND DIVERSIONS 8.05.1 8 8.05.2 The permissible velocity procedure is recommended for the design of vegetative channels because of common usage and the availability of reliable design tables. The tractive force approach is recommended for design of channels with temporary synthetic liners or riprap liners. The tractive force procedure is described in full in the U.S. Department of Transportation, Federal Highway Administration Bulletin, Design of Roadside Channels with Flexible Linings. Permissible Velocity Procedure The permissible velocity procedure uses two equations to calculate flow: Manning’s equation, V = 1.49 R2/3 S1/2 n where: V = average velocity in the channel in ft/sec. n = Manning’s roughness coefficient, based upon the lining of the channel R = hydraulic radius, wetted cross-sectional area/wetted perimeter in ft S = slope of the channel in ft/ft and the continuity equation, Q = AV where: Q = flow in the channel in cfs A = cross-sectional area of flow within the channel in ft2 V = average velocity in the channel in ft/sec. Manning’s equation and the continuity equation are used together to determine channel capacity and flow velocity. A nomograph for solving Manning’s equation is given in Figure 8.05a. Selecting Permanent Channel Lining Channel lining materials include such flexible materials as grass, riprap and gabions, as well as rigid materials such as paving blocks, flag stone, gunite, asphalt, and concrete. The design of concrete and similar rigid linings is generally not restricted by flow velocities. However, flexible channel linings do have maximum permissible flow velocities beyond which they are susceptible to erosion. The designer should select the type of liner that best fits site conditions. Table 8.05a lists maximum permissible velocities for established grass linings and soil conditions. Before grass is established, permissible velocity is determined by the choice of temporary liner. Permissible velocities for riprap linings are higher than for grass and depend on the stone size selected. Appendices 8.05.3 8 8.05.4 Table 8.05a Maximum Allowable Design Velocities1 for Vegetated Channels Typical Channel Slope Application Soil Characteristics2 Grass Lining Permissible Velocity3 for Established Grass Lining (ft/sec) 0-5%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 5.0 4.5 4.5 4.5 3.5 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 6.0 5.5 5.5 5.5 4.5 5-10%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 4.5 4.0 4.0 4.0 3.0 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 5.5 5.0 5.0 5.0 3.5 >10%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass 3.5 2.5 2.5 2.5 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass 4.5 3.5 3.5 3.5 Source: USDA-SCS Modified NOTE:1Permissible Velocity based on 10-year storm peak runoff 2Soil erodibility based on resistance to soil movement from concentrated flowing water. 3Before grass is established, permissible velocity is determined by the type of temporary liner used. Selecting Channel Cross-Section Geometry To calculate the required size of an open channel, assume the design flow is uniform and does not vary with time. Since actual flow conditions change throughout the length of a channel, subdivide the channel into design reaches, and design each reach to carry the appropriate capacity. The three most commonly used channel cross-sections are “V”-shaped, parabolic, and trapezoidal. Figure 8.05b gives mathematical formulas for the area, hydraulic radius and top width of each of these shapes. Appendices 8.05.5 8 8.05.6 Rev. 12/93 Design Procedure- Permissible Velocity The following is a step-by-step procedure for designing a runoff conveyance channel using Manning’s equation and the continuity equation: Step 1. Determine the required flow capacity, Q, by estimating peak runoff rate for the design storm (Appendix 8.03). Step 2. Determine the slope and select channel geometry and lining. Step 3. Determine the permissible velocity for the lining selected, or the desired velocity, if paved. (see Table 8.05a, page 8.05.4) Step 4. Make an initial estimate of channel size—divide the required Q by the permissible velocity to reach a “first try” estimate of channel flow area. Then select a geometry, depth, and top width to fit site conditions. Step 5. Calculate the hydraulic radius, R, from channel geometry (Figure 8.05b, page 8.05.5). Step 6. Determine roughness coefficient n. Structural Linings—see Table 8.05b, page 8.05.6. Grass Lining: a. Determine retardance class for vegetation from Table 8.05c, page 8.05.8. To meet stability requirement, use retardance for newly mowed condition (generally C or D). To determine channel capacity, use at least one retardance class higher. b. Determine n from Figure 8.05c, page 8.05.7. Step 7. Calculate the actual channel velocity, V, using Manning’s equation (Figure 8.05a, pg. 8.05.3), and calculate channel capacity, Q, using the continuity equation. Step 8. Check results against permissible velocity and required design capacity to determine if design is acceptable. Step 9. If design is not acceptable, alter channel dimensions as appropriate. For trapezoidal channels, this adjustment is usually made by changing the bottom width. Table 8.05b Manning’s n for Structural Channel Linings Channel Lining Recommended n values Asphaltic concrete, machine placed Asphalt, exposed prefabricated Concrete Metal, corrugated Plastic Shotcrete Gabion Earth 0.014 0.015 0.015 0.024 0.013 0.017 0.030 0.020 Source: American Society of Civil Engineers (modified) Appendices Rev. 12/93 8.05.7 Step 10. For grass-lined channels once the appropriate channel dimensions have been selected for low retardance conditions, repeat steps 6 through 8 using a higher retardance class, corresponding to tall grass. Adjust capacity of the channel by varying depth where site conditions permit. NOTE 1: If design velocity is greater than 2.0 ft/sec., a temporary lining may be required to stabilize the channel until vegetation is established. The temporary liner may be designed for peak flow from the 2-year storm. If a channel requires a temporary lining, the designer should analyze shear stresses in the channel to select the liner that provides protection and promotes establishment of vegetation. For the design of temporary liners, use tractive force procedure. NOTE 2: Design Tables—Vegetated Channels and Diversions at the end of this section may be used to design grass-lined channels with parabolic cross-sections. Step 11. Check outlet for carrying capacity and stability. If discharge velocities exceed allowable velocities for the receiving stream, an outlet protection structure will be required (Table 8.05d, page 8.05.9). Sample Problem 8.05a illustrates the design of a grass-lined channel. 8 8.05.8 Table 8.05c Retardance Classification for Vegetal Covers Retardance Cover Condition A Reed canarygrass Weeping lovegrass Excellent stand, tall (average 36”) Excellent stand, tall (average 30”) B Tall fescue Bermudagrass Grass-legume mixture (tall fescue,red fescue, sericea lespedeza) Grass mixture (timothy, smooth bromegrass or orchardgrass) Sericea lespedeza Reed canarygrass Alfalfa Good stand, uncut, (average 18”) Good stand, tall (average 12”) Good stand, uncut Good stand, uncut (average 20”) Good stand, not woody, tall (average 19”) Good stand, cut, (average 12-15”) Good stand, uncut (average 11”) C Tall fescue Bermudagrass Bahiagrass Grass-legume mixture-- summer (orchardgrass, redtop and annual lespedeza) Centipedegrass Kentucky bluegrass Redtop Good stand (8-12”) Good stand, cut (average 6”) Good stand, uncut (6-8”) Good stand, uncut (6-8”) Very dense cover (average 6”) Good stand, headed (6-12”) Good stand, uncut (15-20”) D Tall fescue Bermudagrass Bahiagrass Grass-legume mixture-- fall-spring (orchardgrass, redtop, and annual lespedeza) Red fescue Centipedegrass Kentucky bluegrass Good stand, cut (3-4”) Good stand, cut (2.5”) Good stand, cut (3-4”) Good stand, uncut (4-5”) Good stand, uncut (12-18”) Good stand, cut (3-4”) Good stand, cut (3-4”) E Bermudagrass Bermudagrass Good stand, cut (1.5”) Burned stubble Modified from: USDA-SCS, 1969. Engineering Field Manual. Appendices 8.05.9 Table 8.05d Maximum Permissible Velocities for Unprotected Soils in Existing Channels. Materials Maximum Permissible Velocities (fps) Fine Sand (noncolloidal) Sand Loam (noncolloidal) Silt Loam (noncolloidal) Ordinary Firm Loam Fine Gravel Stiff Clay (very colloidal) Graded, Loam to Cobbles (noncolloidal) Graded, Silt to Cobbles (colloidal) Alluvial Silts (noncolloidal) Alluvial Silts (colloidal) Coarse Gravel (noncolloidal) Cobbles and Shingles 2.5 2.5 3.0 3.5 5.0 5.0 5.0 5.5 3.5 5.0 6.0 5.5 Sample Problem 8.05a Design of a Grass-lined Channel. Given: Design Q10 = 16.6 cfs Proposed channel grade = 2% Proposed vegetation: Tall fescue Soil: Creedmoor (easily erodible) Permissible velocity, Vp = 4.5 ft/s (Table 8.05a) Retardance class: “B” uncut, “D” cut (Table 8.05c). Trapezoidal channel dimensions: designing for low retardance condition (retardance class D) design to meet Vp. Find: Channel dimensions Solution: Make an initial estimate of channel size A = Q/V, 16.6 cfs/4.5 ft/sec = 3.69 ft2 Try bottom width = 3.0 ft w/side slopes of 3:1 Z = 3 A = bd + Zd2 P = b + 2d Z2 + 1 R = AP An iterative solution using Figure 8.05a to relate flow depth to Manning’s n proceeds as follows: Manning’s equation is used to check velocities. *From Fig. 8.05c, pg. 8.05.7, Retardance Class d (VR=4.5x0.54=2.43) d (ft) A (ft 2) R (ft) *n Vt (fps) Q (cfs) Comments 0.8 4.32 0.54 0.043 3.25 14.0 V<Vp OK, Q<Q10 (too small, try deeper channel) 0.9 5.13 0.59 0.042 3.53 18.10 V<Vp, OK, Q>Q10, OK Now design for high retardance (class B): For the ease of construction and maintenance assume and try d = 1.5 ft and trial velocity Vt = 3.0 ft/sec d (ft) A (ft 2) R (ft)Vt (fps)n V (fps) Q (cfs) Comments 1.5 11.25 0.90 3.0 2.0 1.6 **1.5 0.08 0.11 0.12 0.13 2.5 1.8 1.6 1.5 28 20 18 17 reduce Vtreduce Vt Q>Q10 OK ** These assumptions = actual V (fps.) (chart continued on next page) 8 8.05.10 Rev. 12/93 (continued) Sample Problem 8.05a Design of a Grass-lined Channel. Channel summary: Trapezoidal shape, Z = 3, b = 3 ft, d = 1.5 ft, grade = 2% Note: In Sample Problem 8.05a the “n-value” is first chosen based on a permissible velocity and not a design velocity criteria. Therefore, the use of Table 8.05c may not be as accurate as individual retardance class charts when a design velocity is the determining factor. Tractive Force Procedure The design of riprap-lined channels and temporary channel linings is based on analysis of tractive force. NOTE: This procedure is for uniform flow in channels and is not to be used for design of deenergizing devices and may not be valid for larger channels. To calculate the required size of an open channel, assume the design flow is uniform and does not vary with time. Since actual flow conditions change through the length of a channel, subdivide the channel into design reaches as appropriate. PERMISSIBLE SHEAR STRESS The permissible shear stress, Td, is the force required to initiate movement of the lining material. Permissible shear stress for the liner is not related to the erodibility of the underlying soil. However, if the lining is eroded or broken, the bed material will be exposed to the erosive force of the flow. COMPUTING NORMAL DEPTH The first step in selecting an appropriate lining is to compute the design flow depth (the normal depth) and determine the shear stress. Normal depths can be calculated by Manning’s equation as shown for trapezoidal channels in Figure 8.05d. Values of the Manning’s roughness coefficient for different ranges of depth are provided in Table 8.05e for temporary linings and Table 8.05f for riprap. The coefficient of roughness generally decreases with increasing flow depth. n value for Depth Ranges* Table 8.05e Manning’s Roughness Coefficients for Temporary Lining Materials 0-0.5 ft 0.5-2.0 ft >2.0 ft Lining Type Woven Paper Net Jute Net Fiberglass Roving Straw with Net Curled Wood Mat Synthetic Mat 0.016 0.028 0.028 0.065 0.066 0.036 0.015 0.022 0.021 0.033 0.035 0.025 0.015 0.019 0.019 0.025 0.028 0.021 * Adapted from: FHWA-HEC 15, Pg. 37 - April 1988 8 8.05.12 Rev. 12/93 Table 8.05f Manning’s Roughness Coefficient n - value n value for Depth Ranges Lining Category Lining Type 0-0.5 ft (0-15 cm) 0.5-2.0 ft (15-60 cm) 2.0 ft (>60 cm) Rigid Concrete Grouted Riprap Stone Masonry Soil Cement Asphalt 0.015 0.040 0.042 0.025 0.018 0.013 0.030 0.032 0.022 0.016 0.013 0.028 0.030 0.020 0.016 Unlined Bare Soil Rock Cut 0.023 0.045 0.020 0.035 0.020 0.025 Gravel Riprap 1-inch (2.5-cm) D502-inch (5-cm) D50 0.044 0.066 0.033 0.041 0.030 0.034 Rock Riprap 6-inch (15-cm) D5012-inch (30-cm) D50 0.104 -- 0.069 0.078 0.035 0.040 Note: Values listed are representative values for the respective depth ranges. Manning’s roughness coefficients, n, vary with the flow depth. DETERMINING SHEAR STRESS Shear stress, T, at normal depth is computed for the lining by the following equation: T = yds Td = Permissible shear stress where: T = shear stress in lb/ft2 y = unit weight of water, 62.4 lb/ft3 d = flow depth in ft s = channel gradient in ft/ft If the permissible shear stress, Td, given in Table 8.05g is greater than the computed shear stress, the riprap or temporary lining is considered acceptable. If a lining is unacceptable, select a lining with a higher permissible shear stress and repeat the calculations for normal depth and shear stress. In some cases it may be necessary to alter channel dimensions to reduce the shear stress. Computing tractive force around a channel bend requires special considerations because the change in flow direction imposes higher shear stress on the channel bottom and banks. The maximum shear stress in a bend, Tb, is given by the following equation: Tb = KbT where: Tb = bend shear stress in lb/ft2 kb = bend factor T = computed stress for straight channel in lb/ft2 The value of kb is related to the radius of curvature of the channel at its center line, Rc, and the bottom width of the channel, B, Figure 8.05e. The length of channel requiring protection downstream from a bend, Lp, is a function of the roughness of the lining material and the hydraulic radius as shown in Figure 8.05f. Appendices Rev. 12/93 8.05.13 Table 8.05g Permissible Shear Stresses for Riprap and Temporary Liners Permissible Unit Shear Stress, Td Lining Category Lining Type (lb/ft2) Temporary Woven Paper Net Jute Net Fiberglass Roving: Single Double Straw with Net Curled Wood mat Synthetic Mat 0.15 0.45 0.60 0.85 1.45 1.55 2.00 d50 Stone Size (inches) Gravel Riprap 1 2 0.33 0.67 Rock Riprap 6 9 12 15 18 21 24 2.00 3.00 4.00 5.00 6.00 7.80 8.00 Adapted From: FHWA, HEC-15, April 1983, pgs. 17 & 37. Design Procedure- Temporary Liners The following is a step-by-step procedure for designing a temporary liner for a channel. Because temporary liners have a short period of service, the design Q may be reduced. For liners that are needed for six months or less, the 2-year frequency storm is recommended. Step 1. Select a liner material suitable for site conditions and application. Determine roughness coefficient from manufacturer’s specifications or Table 8.05e, page 8.05.10. Step 2. Calculate the normal flow depth using Manning’s equation (Figure 8.05d). Check to see that depth is consistent with that assumed for selection of Manning’s n in Figure 8.05d, page 8.05.11. For smaller runoffs Figure 8.05d is not as clearly defined. Recommended solutions can be determined by using the Manning equation. Step 3. Calculate shear stress at normal depth. Step 4. Compare computed shear stress with the permissible shear stress for the liner. Step 5. If computed shear is greater than permissible shear, adjust channel dimensions to reduce shear, or select a more resistant lining and repeat steps 1 through 4. Design of a channel with temporary lining is illustrated in Sample Problem 8.05b, page 8.05.14. REFERENCE 4 “Standard Specification for Roads and Structures”, North Carolina Department of Transportation, Raleigh, January 2012. Section 1043 10-62 All stone shall meet the approval of the Engineer. While no specific gradation is required, 1 there shall be equal distribution of the various sizes of the stone within the required size 2 range. The size of an individual stone particle will be determined by measuring its long 3 dimension. 4 Stone or broken concrete for rip rap shall meet Table 1042-1 for the class and size 5 distribution. 6 TABLE 1042-1 ACCEPTANCE CRITERIA FOR RIP RAP AND STONE FOR EROSION CONTROL Required Stone Sizes, inches Class Minimum Midrange Maximum A 2 4 6 B 5 8 12 1 5 10 17 2 9 14 23 No more than 5.0% of the material furnished can be less than the minimum size specified nor 7 no more than 10.0% of the material can exceed the maximum size specified. 8 SECTION 1043 9 AGGREGATE FROM CRUSHED CONCRETE 10 1043-1 GENERAL 11 Aggregate from crushed concrete is a recycled product made by crushing concrete obtained 12 from concrete truck clean out, demolition of existing concrete structures or pavement, or 13 similar sources and transported from a crushing facility. It does not include concrete 14 pavements that are rubblelized, broken or otherwise crushed in place on the roadway. 15 The crushed material must meet all sources approval requirements described in Sections 1005 16 and 1006 with the exception of the sodium sulfate test requirement. Deleterious materials 17 shall not be more than 3%. 18 Sampling and acceptance for the determination of gradaction, LL and PI will be performed as 19 described in the Aggregate QC/QA Program Manual and the Aggregate Sampling Manual. 20 1043-2 AGGREGATE BASE COURSE 21 The material shall meet the ABC gradation. The LL of the material shall be raised 5 points to 22 no more than 35. 23 1043-3 AGGREGATE SHOULDER BORROW 24 The material shall meet Section 1019. 25 1043-4 CLEAN COARSE AGGREGATE FOR ASPHALT 26 The material shall meet the gradation of a standard size in Table 1005-1. Use of the material 27 shall be approved by the Engineer, and the mix shall meet all requirements. 28 1043-5 CLEAN COARSE AGGREGATE FOR CONCRETE 29 The material shall meet the gradation of a standard size in Table 1005-1. Use of the material 30 is restricted to Class B concrete mixes only. Use of the material shall be approved by the 31 Engineer, and the concrete shall meet all requirements. 32 SECTION 1044 33 SUBSURFACE DRAINAGE MATERIALS 34 1044-1 SUBDRAIN FINE AGGREGATE 35 Subdrain fine aggregate shall meet No. 2S or 2MS in Table 1005-2. 36 NCDOT 2012 Standard Specifications REFERENCE 5 United States Department of Agriculture, “Urban Hydrology for Small Watersheds”, Technical Release 55, June 1986. Technical Release 55 Urban Hydrology for Small Watersheds Time of Concentration and Travel TimeChapter 3 3–4 (210-VI-TR-55, Second Ed., June 1986) Manning’s equation is: V rs n =149 2 3 1 2.[eq. 3-4] where: V = average velocity (ft/s) r = hydraulic radius (ft) and is equal to a/pw a = cross sectional flow area (ft 2) pw = wetted perimeter (ft) s = slope of the hydraulic grade line (channel slope, ft/ft) n = Manning’s roughness coefficient for open channel flow. Manning’s n values for open channel flow can be obtained from standard textbooks such as Chow (1959) or Linsley et al. (1982). After average velocity is computed using equation 3-4, Tt for the channel seg- ment can be estimated using equation 3-1. Reservoirs or lakes Sometimes it is necessary to estimate the velocity of flow through a reservoir or lake at the outlet of a watershed. This travel time is normally very small and can be assumed as zero. Limitations •Manning’s kinematic solution should not be used for sheet flow longer than 300 feet. Equation 3-3 was developed for use with the four standard rainfall intensity-duration relationships. •In watersheds with storm sewers, carefully identify the appropriate hydraulic flow path to estimate Tc. Storm sewers generally handle only a small portion of a large event. The rest of the peak flow travels by streets, lawns, and so on, to the outlet. Consult a standard hydraulics textbook to determine average velocity in pipes for either pressure or nonpressure flow. •The minimum Tc used in TR-55 is 0.1 hour. •A culvert or bridge can act as a reservoir outlet if there is significant storage behind it. The proce- dures in TR-55 can be used to determine the peak flow upstream of the culvert. Detailed storage routing procedures should be used to determine the outflow through the culvert. Example 3-1 The sketch below shows a watershed in Dyer County, northwestern Tennessee. The problem is to compute Tc at the outlet of the watershed (point D). The 2-year 24-hour rainfall depth is 3.6 inches. All three types of flow occur from the hydraulically most distant point (A) to the point of interest (D). To compute Tc, first determine Tt for each segment from the following information: Segment AB: Sheet flow; dense grass; slope (s) = 0.01 ft/ft; and length (L) = 100 ft. Segment BC: Shallow concentrated flow; unpaved; s = 0.01 ft/ft; and L = 1,400 ft. Segment CD: Channel flow; Manning’s n = .05; flow area (a) = 27 ft2; wetted perimeter (pw) = 28.2 ft; s = 0.005 ft/ft; and L = 7,300 ft. See figure 3-2 for the computations made on worksheet 3. A B C D 7,300 ft1,400 ft100 ft (Not to scale) Outlet Channel Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 1 of 4 12/9/2016 (Initial Submittal) Calculation Title: Outlet Channel Calculation Summary: The outlet channels for the Dan River dam decommissioning were designed for stability and capacity for a Type II 100-year, 24-hour design storm event of 8.20 inches while maintaining channel lining stability. Notes: Revision Log: No. Description Originator Verifier Technical Reviewer 0 Initial Submittal – 12/9/2016 Chris Jordan Stephanie Stanwick Cedric H Ruhl Outlet Channel Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 2 of 4 12/9/2016 (Initial Submittal) OBJECTIVE: The objective of this calculation is to design the outlet channels from the final closure conditions of the Primary and Secondary ash basins. The four outlet channels convey flow from the footprint of the decommissioned impoundment to gabion outlets into the Dan River. METHOD: The outlet channels were evaluated using Manning’s equation for the 100-year, 24 hour design storm event. DEFINITION OF VARIABLES: A = drainage area; AC = cross-section area of flow through channel; b = bottom width of flow through channel; d = depth of flow through channel; CN = curve number; D = channel depth; i = rainfall depth; n = Manning’s roughness co-efficient for flow through channel; P = wetted perimeter of flow through channel; Q = discharge flow; R = hydraulic radius of flow through channel; S = longitudinal slope of the channel flow; T = top width of flow through channel; V = velocity of flow through channel; and Z = channel side slope. CALCULATIONS: 1.0 Outlet Channels Four stormwater outlet channels will be constructed to convey flow from the footprint of the decommissioned impoundment to gabion outlets into the Dan River. Design criteria for the channels was first evaluated by estimating the peak flow to the channels using the SCS method, and then evaluating the channel capacity using Manning’s equation [Ref. 3]. The channels were designed for capacity for the 100-year design storm. 1.1 Channel peak flow rates The times of concentration from contributing drainage areas to the outlet channels are delineated and shown in the “Final Conditions Stormwater Calculation” package. Peak flow rates to the outlet channels have been calculated in HydroCAD for a 100-year, 24 hour design storm event and are shown in the following table: Outlet Channel Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 3 of 4 12/9/2016 (Initial Submittal) Channel ID Tributary Drainage Area Design Storm Event (years) Rainfall for 24-Hour Storm {i} (in) (Ref. 1) Design Flow {Q100} (cfs) OC-1 DA-5A - 5D 100 8.2 49.8 OC-2 DA-1, DA-6A - 6G 100 8.2 281.0 OC-3 DA-2, DA-4, DA-7A - 7G 100 8.2 190.3 OC-4 DA-3, DA-8A-1, DA-8A - 8D 100 8.2 82.0 Table 1: Peak Flow Rates 1.2 Channel capacity The stormwater outlet channels were assumed to be trapezoidal channels with dimensions as presented in the following table: Channel ID Channel Type Bottom Width {b} (ft) MIN. Depth {D} (ft) Left Side Slope {Z1H:V} Right Side Slope {Z2H:V} Top Width {T} (ft) Upstream Invert (ft) Downstream Invert (ft) Length {L} (ft) Longitudinal Slope {S} (ft/ft) OC-1 Outlet 3 2 3 3 499.5 497 116 0.022 OC-2 Outlet 9 2 3 3 499.5 496 103 0.034 OC-3 Outlet 9 2 3 3 499.5 497 91 0.027 OC-4 Outlet 3 2 3 3 498.0 495 150 0.020 Table 2: Channel Dimensions VARIES The capacity of each stormwater channel was evaluated using Manning’s equation [Ref. 3] as presented in the following equation: 𝑉=1.49 𝑛𝑃2/3 𝑃1/2 Where n is Manning’s coefficient, R is hydraulic radius and S is the longitudinal slope of the stormwater flow. The total discharge was given by: 𝑃=𝐴𝐶𝑉 The flow cross-section area “AC” and wetted perimeter “P” were calculated based on the geometry of a trapezoidal channel with a flow depth “d”, bottom width “b”, left side slope “Z1”, and right side slope “Z2”, using the following relationships: 𝐴𝐶=𝑏𝑑+0.5𝑍1 𝑑2 +0.5𝑍2 𝑑2 𝑃=𝑏+√[(𝑍1 𝑑)2 +𝑑2 ]+√[(𝑍2 𝑑)2 +𝑑2 ] Each channel was assumed to have rip-rap lining and was evaluated for capacity for the 100- year, 24-hour design storm event. The trial flow depth and Manning’s n were iteratively modified until the channel capacity exceeded the predicted peak runoff for the conditions modeled. Channel capacity estimated for the minimum channel grade is shown in the following table: Outlet Channel Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 4 of 4 12/9/2016 (Initial Submittal) Channel ID Channel Type Channel Lining Manning's n {n} [Ref. 2] Trial Flow Depth {d} (ft) Flow Area {A} (ft2) Wetted Perimeter {P} (ft) Hydraulic Radius {R} (ft) Velocity {V} (ft/s) Channel Capacity {Q} (cfs) Peak Runoff {Q} (cfs) Channel Capacity > Peak Runoff? Freeboard (in) OC-1 Outlet riprap 0.03 1.24 8.3 10.8 0.8 6.1 50.98 49.75 yes 9.1 OC-2 Outlet riprap 0.03 1.82 26.3 20.5 1.3 10.8 284.51 280.99 yes 2.2 OC-3 Outlet riprap 0.03 1.56 21.3 18.9 1.1 8.9 190.72 190.27 yes 5.3 OC-4 Outlet riprap 0.03 1.58 12.2 13.0 0.9 6.7 82.50 81.99 yes 5.0 Table 3: Channel Capacity - 100 years Long-Term Conditions The hydraulic analyses indicate that the outlet channels have capacity to pass the 100-year, 24- hour design storm. DISCUSSION: The outlet channels for the Dan River dam decommissioning were designed for stability and capacity for a Type II 100-year, 24-hour design storm event of 8.20 inches while maintaining channel lining stability. REFERENCES: 1. Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. 2. HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. 3. North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. REFERENCE 1 Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. Precipitation Frequency Data Server Page 1 of 3 NOAA Atlas 14, Volume 2, Version 3 Location name: Eden, North Carolina, US" Latitude: 36.4999°, Longitude:-79.7013° Elevation: 582 ft* * source: Google Maps "*�,�,,.t 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 I PF graphical I Maps & aerials PF tabular PDS-based point precipitation frequency estimates with 90% confidence intervals (in inches)' Average recurrence interval (years) Duration ��� 10 25 50 100 200 500 1000 0.363 0.433 0.512 0.567 0.633 0.676 0.717 0.754 0.796 0.826 5-min (0.331-0.397) (0.396-0.473) (0.467-0.560) (0.518-0.619) (0.575-0.688) (0.612-0.735) (0.646-0.781) (0.676-0.822) (0.708-0.869) (0.729-0.902) 0.579 0.692 0.820 0.908 1.01 1.08 1.14 1.20 1.26 1.30 10-min (0 .529-0.634) (0.633-0.757) (0.749-0.898) (0.829-0.991) (0.917-1.10) (0.974-1.17) 1 (1.03-1.24) 1 (1.07-1.30) 1 (1.12-1.38) 0.724 0.870 1.04 1.15 1.28 1.36 1.44 1.51 1.59 1.63 15-min (0.661-0.792) (0.796-0.951) (0.947-1.14) 1 (1.05-1.25) 1 (1.16-1.39) 1 (1.23-1.48) 1 (1.30-1.57) 1 (1.35-1.64) 1 (1.41-1.73) 1 (1.44-1.78) 0.993 1.20 1.47 1.66 1.89 2.05 2.21 2.35 2.52 2.64 30-min (0.906-1.09) 1 (1.10-1.31) 1 (1.35-1.61) 1 (1.52-1.82) 1 (1.72-2.06) (1.86-2.23) (1.99-2.40) (2.11-2.56) (2.24-2.75) (2.33-2.89) 1.24 1.51 1.89 2.17 2.52 2.78 3.04 3.29 3.62 3.86 60-min (1.13-1.35) (1.38-1.65) (1.73-2.07) (1.98-2.36) (2.29-2.74) (2.52-3.03) (2.74-3.31) (2.95-3.59) (3.22-3.95) (3.41-4.22) 1.47 1.79 2.25 2.61 3.08 3.45 3.83 4.20 4.71 5.10 2-hr (1.35-1.61) (1.63-1.96) (2.06-2.46) (2.38-2.85) (2.80-3.36) (3.12-3.75) (3.44-4.16) (3.75-4.57) (4.15-5.12) (4.45-5.56) 1.59 1.93 2.44 2.82 3.33 3.73 4.13 4.54 5.08 5.50 3-hr (1.46-1.73) (1.78-2.11) (2.24-2.66) (2.58-3.07) (3.03-3.62) (3.38-4.04) (3.72-4.48) (4.06-4.92) ( 4.49-5.52) ( 4.81-5.98) 1.96 2.37 2.99 3.48 4.15 4.70 5.28 5.87 6.71 7.38 6-hr (1.80-2.15) (2.18-2.61) (2.74-3.27) (3.17-3.80) (3.76-4.53) (4.22-5.12) (4.70-5.73) (5.18-6.37) (5.82-7.29) (6.31-8.02) 2.36 2.87 3.63 4.26 5.15 5.89 6.70 7.56 8.81 9.84 12-hr (2.17-2.59) (2.63-3.14) (3.32-3.96) (3.88-4.62) (4.65-5.57) (5.28-6.37) (5.94-7.21) (6.62-8.12) (7.57-9.48) (8.31-10.6 ) 2.81 3.40 4.33 5.10 6.22 7.17 8.20 9.32 11.0 12.4 24-hr (2.61-3.04) (3.16-3.68) (4.02-4.67) (4.72-5.48) (5.72-6.68) (6.55-7.69) (7.44-8.79) (8.39-10.0) (9.74-11.8) (10.9-13.3) 3.30 3.99 5.04 5.90 7.12 8.13 9.21 10.4 12.0 13.4 2-day (3.08-3.55) (3.72-4.30) (4.70-5.42) (5.48-6.33) (6.59-7.63) (7.48-8.71) (8.42-9.88) (9.40-11.1 ) ( 10.8-13.0 ) ( 11.9-14.5 ) 3.49 4.22 5.33 6.23 7.52 8.59 9.72 10.9 12.7 14.2 3-day (3.26-3.76) (3.93-4.55) (4.96-5.73) (5.79-6.69) (6.95-8.07) (7.89-9.21) (8.88-10.4) (9.92-11.8) (11.4-13.7) ( 12.6-15.3) 3.68 4.45 5.61 6.56 7.92 9.04 10.2 11.5 13.4 14.9 4-day (3.43-3.97) (4.15-4.80) (5.23-6.05) (6.10-7.06) (7.32-8.51) (8.31-9.71) (9.35-11.0) (10.4-12.4) (12.0-14.4) (13.2-16.1) 4.22 5.07 6.29 7.29 8.71 9.88 11.1 12.4 14.3 15.9 7-day (3.96-4.51) (4.75-5.42) (5.89-6.72) (6.81-7.78) (8.11-9.28) (9.14-10.5) (10.2-11.9) ( 11.4-13.3) ( 12.9-15.3) ( 14.2-17.0) 4.77 5.71 7.01 8.0 6 10.7 12.0 13.3 15.1 16.6 10-day ��69.53 (4.48-5.10 ) (5.37-6.10) (6.58-7.48 ) (7.55-8.60) (8.89-10.2 ) (9.96-11.4) (11.1-12.8) (12.2-14.2) (13.8-16.2) (15.0-17.8) 6.43 7.65 9.20 10.4 12.1 13.4 14.7 16.1 17.9 19.3 20-day (6.05-6.85) (7.21-8.16) (8.66-9.81) (9.79-11.1) (11.3-12.9) (12.5-14.3) (13.7-15.7) (14.9-172) (16.4-19.2) (17.6-20.8) 30-day 7.95 9.40 11.1 12.3 14.0 15.3 16.5 17.7 19.3 20.5 (7.53-8.41) (8.91-9.94) (10.5-11.7) (11.7-13.0) (13.2-14.8) (14.4-16.2) (15.5-17.5) (16.6-18.8) (18.0-20.5) (19.0-21.9) 45-day 10.0 11.8 13.7 15.2 17.1 18.5 19.8 21.1 22.8 24.0 (9.48-10.6) (11.2-12.5) (13.0-14.5) (14.4-16.0) (16.1-18.0) (17.4-19.5) (18.6-21.0) (19.8-22.4) (21.3-24.2) (22.3-25.6) 12.0 14.0 16.1 17.7 19.7 21.2 22.6 23.9 25.6 26.8 60-day ( 114-12.6) 1 (13.4-14.8) 1 U-15-3-1-7.0) I (16.8-18.6) 1 U-18-7-2-o.7) 1 (20.0-22.3) 1 U-21-3-2-3.8) 1 (22.5-25.2) J (24.0-27.1) 11 (25.1-28.4) 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. Back to Top PF graphical http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 Precipitation Frequency Data Server Page 2 of 3 25 ....:....:.....:.....:.....:... ... .. ..... c 20 __ -. ...... --.- ... ._._. .. r. 0 15 .2 i-I 10 IL 5 0 e c_ L ry s w Ce _c c` LL M IppC N T�'1 41S r��d N ra1 yy�--�� 7 ppE 0 .i O 6 rS7Vf 30 �64.d Diratidn 30 25 L 20 5 0 1 2 5 10 25 50 100 200 500 1000 ack tR To Average recurrence interval Maps & aerials NOAA Atlas 14, Volume 2, Version 3 created tGMTI: Mon Sep 15 14:27:08 2014 Small scale terrain Washrr 'i1101"" Grvrrs•✓ l Charlottesville's Nafirt t f Fvresir% °� i ~`cIFyn hhurgU! V i r.g i n i a. Ric _61a kslwr �` Peter e 9i "Roanoke gip ortt — — - 0dnvill F-Johnson Ctierokee Navonal rvresf' >_ td 7 bonne tree sboro . �iFis❑ah<. ,.. 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E 7W 1953 � Sti t962 17dT Td76 S 4h� ,vr � 7pp Aen 1779 _ 87� H 2 km Map OpNoUilreboangie Back to Too US Department of Commerce National Oceanic and Atmospheric Administration National Weather Service Office of Hvdroloaic Develooment 1325 East West Highway Silver Spring, MD 20910 Questions?: HDSC.Questions(a)noaa.aov Disclaimer http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 REFRENCE 2 HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. R-15 Outlet-2 R02 Outlet-1 Routing Diagram for LT_1 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Inflow=280.99 cfs 17.492 afReach R-15: Outlet-2 Outflow=280.99 cfs 17.492 af Inflow=49.75 cfs 4.113 afReach R02: Outlet-1 Outflow=49.75 cfs 4.113 af Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-15: Outlet-2 Inflow Area = 39.459 ac, 0.00% Impervious, Inflow Depth > 5.32" for 100-Year event Inflow = 280.99 cfs @ 12.07 hrs, Volume= 17.492 af Outflow = 280.99 cfs @ 12.07 hrs, Volume= 17.492 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Reach R-15: Outlet-2 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 300 250 200 150 100 50 0 Inflow Area=39.459 ac 280.99 cfs280.99 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_1 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R02: Outlet-1 Inflow Area = 10.470 ac, 0.00% Impervious, Inflow Depth > 4.71" for 100-Year event Inflow = 49.75 cfs @ 12.11 hrs, Volume= 4.113 af Outflow = 49.75 cfs @ 12.11 hrs, Volume= 4.113 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Reach R02: Outlet-1 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 55 50 45 40 35 30 25 20 15 10 5 0 Inflow Area=10.470 ac 49.75 cfs49.75 cfs R-25 Outlet-3 R-42 Outlet-4 Routing Diagram for LT_2 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points x 2 Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Inflow=190.27 cfs 40.828 afReach R-25: Outlet-3 Outflow=190.27 cfs 40.828 af Inflow=81.99 cfs 6.571 afReach R-42: Outlet-4 Outflow=81.99 cfs 6.571 af Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-25: Outlet-3 Inflow Area = 95.370 ac, 0.00% Impervious, Inflow Depth > 5.14" for 100-Year event Inflow = 190.27 cfs @ 12.11 hrs, Volume= 40.828 af Outflow = 190.27 cfs @ 12.11 hrs, Volume= 40.828 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Reach R-25: Outlet-3 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=95.370 ac 190.27 cfs190.27 cfs Type II 24-hr 100-Year Rainfall=8.20"LT_2 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Reach R-42: Outlet-4 Inflow Area = 16.815 ac, 0.00% Impervious, Inflow Depth > 4.69" for 100-Year event Inflow = 81.99 cfs @ 12.11 hrs, Volume= 6.571 af Outflow = 81.99 cfs @ 12.11 hrs, Volume= 6.571 af, Atten= 0%, Lag= 0.0 min Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 2 Reach R-42: Outlet-4 Inflow Outflow Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 90 80 70 60 50 40 30 20 10 0 Inflow Area=16.815 ac 81.99 cfs81.99 cfs REFERENCE 3 North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. Appendices This section addresses the design of stable conveyance channels and diversions using flexible linings. A stable channel is defined as a channel which is nonsilting and nonscouring. To minimize silting in the channel, flow velocities should remain constant or increase slightly throughout the channel length. This is especially important in designing diversion channels and can be accomplished by adjusting channel grade. Procedures presented in this section address the problems of erosion and scour. More advanced procedures for permanent, unlined channels may be found elsewhere. (References: Garde and Ranga Raju, 1980) Diversions are channels usually with a supporting ridge on the lower side. They are generally located to divert flows across a slope and are designed following the same procedures as other channels. Design tables for vegetated diversions and waterways are included at the end of this section. Flexible channel linings are generally preferred to rigid linings from an erosion control standpoint because they conform to changes in channel shape without failure and are less susceptible to damage from frost heaving, soil swelling and shrinking, and excessive soil pore water pressure from lack of drainage. Flexible linings also are generally less expensive to construct, and when vegetated, are more natural in appearance. On the other hand, flexible linings generally have higher roughness and require a larger cross section for the same discharge. EROSION CONtROL CRItERIa The minimum design criteria for conveyance channels require that two primary conditions be satisfied: the channel system must have capacity for the peak flow expected from the 10-year storm and the channel lining must be resistant to erosion for the design velocity. In some cases, out-of-bank flow may be considered a functional part of the channel system. In these cases, flow capacities and design velocities should be considered separately for out- of-bank flows and channel flows. Both the capacity of the channel and the velocity of flow are functions of the channel lining, cross-sectional area and slope. The channel system must carry the design flow, fit site conditions, and be stable. Sta BLE CHaNNEL DESIGN mEtHODS Two accepted procedures for designing stable channels with flexible linings are: (1) the permissible velocity approach; and (2) the tractive force approach. Under the permissible velocity approach, the channel is considered stable if the design, mean velocity is lower than the maximum permissible velocity. Under the tractive force approach, erosive stress evaluated at the boundary between flowing water and lining materials must be less than the minimum unit tractive force that will cause serious erosion of material from a level channel bed. 8.05 DESIGN Of Sta BLE CHaNNELS aND DIVERSIONS 8.05.1 8 8.05.2 The permissible velocity procedure is recommended for the design of vegetative channels because of common usage and the availability of reliable design tables. The tractive force approach is recommended for design of channels with temporary synthetic liners or riprap liners. The tractive force procedure is described in full in the U.S. Department of Transportation, Federal Highway Administration Bulletin, Design of Roadside Channels with Flexible Linings. Permissible Velocity Procedure The permissible velocity procedure uses two equations to calculate flow: Manning’s equation, V = 1.49 R2/3 S1/2 n where: V = average velocity in the channel in ft/sec. n = Manning’s roughness coefficient, based upon the lining of the channel R = hydraulic radius, wetted cross-sectional area/wetted perimeter in ft S = slope of the channel in ft/ft and the continuity equation, Q = AV where: Q = flow in the channel in cfs A = cross-sectional area of flow within the channel in ft2 V = average velocity in the channel in ft/sec. Manning’s equation and the continuity equation are used together to determine channel capacity and flow velocity. A nomograph for solving Manning’s equation is given in Figure 8.05a. Selecting Permanent Channel Lining Channel lining materials include such flexible materials as grass, riprap and gabions, as well as rigid materials such as paving blocks, flag stone, gunite, asphalt, and concrete. The design of concrete and similar rigid linings is generally not restricted by flow velocities. However, flexible channel linings do have maximum permissible flow velocities beyond which they are susceptible to erosion. The designer should select the type of liner that best fits site conditions. Table 8.05a lists maximum permissible velocities for established grass linings and soil conditions. Before grass is established, permissible velocity is determined by the choice of temporary liner. Permissible velocities for riprap linings are higher than for grass and depend on the stone size selected. Appendices 8.05.3 8 8.05.4 Table 8.05a Maximum Allowable Design Velocities1 for Vegetated Channels Typical Channel Slope Application Soil Characteristics2 Grass Lining Permissible Velocity3 for Established Grass Lining (ft/sec) 0-5%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 5.0 4.5 4.5 4.5 3.5 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 6.0 5.5 5.5 5.5 4.5 5-10%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 4.5 4.0 4.0 4.0 3.0 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass Grass-legume mixture 5.5 5.0 5.0 5.0 3.5 >10%Easily Erodible Non-plastic (Sands & Silts) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass 3.5 2.5 2.5 2.5 Erosion Resistant Plastic (Clay mixes) Bermudagrass Tall fescue Bahiagrass Kentucky bluegrass 4.5 3.5 3.5 3.5 Source: USDA-SCS Modified NOTE:1Permissible Velocity based on 10-year storm peak runoff 2Soil erodibility based on resistance to soil movement from concentrated flowing water. 3Before grass is established, permissible velocity is determined by the type of temporary liner used. Selecting Channel Cross-Section Geometry To calculate the required size of an open channel, assume the design flow is uniform and does not vary with time. Since actual flow conditions change throughout the length of a channel, subdivide the channel into design reaches, and design each reach to carry the appropriate capacity. The three most commonly used channel cross-sections are “V”-shaped, parabolic, and trapezoidal. Figure 8.05b gives mathematical formulas for the area, hydraulic radius and top width of each of these shapes. Appendices 8.05.5 8 8.05.6 Rev. 12/93 Design Procedure- Permissible Velocity The following is a step-by-step procedure for designing a runoff conveyance channel using Manning’s equation and the continuity equation: Step 1. Determine the required flow capacity, Q, by estimating peak runoff rate for the design storm (Appendix 8.03). Step 2. Determine the slope and select channel geometry and lining. Step 3. Determine the permissible velocity for the lining selected, or the desired velocity, if paved. (see Table 8.05a, page 8.05.4) Step 4. Make an initial estimate of channel size—divide the required Q by the permissible velocity to reach a “first try” estimate of channel flow area. Then select a geometry, depth, and top width to fit site conditions. Step 5. Calculate the hydraulic radius, R, from channel geometry (Figure 8.05b, page 8.05.5). Step 6. Determine roughness coefficient n. Structural Linings—see Table 8.05b, page 8.05.6. Grass Lining: a. Determine retardance class for vegetation from Table 8.05c, page 8.05.8. To meet stability requirement, use retardance for newly mowed condition (generally C or D). To determine channel capacity, use at least one retardance class higher. b. Determine n from Figure 8.05c, page 8.05.7. Step 7. Calculate the actual channel velocity, V, using Manning’s equation (Figure 8.05a, pg. 8.05.3), and calculate channel capacity, Q, using the continuity equation. Step 8. Check results against permissible velocity and required design capacity to determine if design is acceptable. Step 9. If design is not acceptable, alter channel dimensions as appropriate. For trapezoidal channels, this adjustment is usually made by changing the bottom width. Table 8.05b Manning’s n for Structural Channel Linings Channel Lining Recommended n values Asphaltic concrete, machine placed Asphalt, exposed prefabricated Concrete Metal, corrugated Plastic Shotcrete Gabion Earth 0.014 0.015 0.015 0.024 0.013 0.017 0.030 0.020 Source: American Society of Civil Engineers (modified) Appendices Rev. 12/93 8.05.7 Step 10. For grass-lined channels once the appropriate channel dimensions have been selected for low retardance conditions, repeat steps 6 through 8 using a higher retardance class, corresponding to tall grass. Adjust capacity of the channel by varying depth where site conditions permit. NOTE 1: If design velocity is greater than 2.0 ft/sec., a temporary lining may be required to stabilize the channel until vegetation is established. The temporary liner may be designed for peak flow from the 2-year storm. If a channel requires a temporary lining, the designer should analyze shear stresses in the channel to select the liner that provides protection and promotes establishment of vegetation. For the design of temporary liners, use tractive force procedure. NOTE 2: Design Tables—Vegetated Channels and Diversions at the end of this section may be used to design grass-lined channels with parabolic cross-sections. Step 11. Check outlet for carrying capacity and stability. If discharge velocities exceed allowable velocities for the receiving stream, an outlet protection structure will be required (Table 8.05d, page 8.05.9). Sample Problem 8.05a illustrates the design of a grass-lined channel. 8 8.05.8 Table 8.05c Retardance Classification for Vegetal Covers Retardance Cover Condition A Reed canarygrass Weeping lovegrass Excellent stand, tall (average 36”) Excellent stand, tall (average 30”) B Tall fescue Bermudagrass Grass-legume mixture (tall fescue,red fescue, sericea lespedeza) Grass mixture (timothy, smooth bromegrass or orchardgrass) Sericea lespedeza Reed canarygrass Alfalfa Good stand, uncut, (average 18”) Good stand, tall (average 12”) Good stand, uncut Good stand, uncut (average 20”) Good stand, not woody, tall (average 19”) Good stand, cut, (average 12-15”) Good stand, uncut (average 11”) C Tall fescue Bermudagrass Bahiagrass Grass-legume mixture-- summer (orchardgrass, redtop and annual lespedeza) Centipedegrass Kentucky bluegrass Redtop Good stand (8-12”) Good stand, cut (average 6”) Good stand, uncut (6-8”) Good stand, uncut (6-8”) Very dense cover (average 6”) Good stand, headed (6-12”) Good stand, uncut (15-20”) D Tall fescue Bermudagrass Bahiagrass Grass-legume mixture-- fall-spring (orchardgrass, redtop, and annual lespedeza) Red fescue Centipedegrass Kentucky bluegrass Good stand, cut (3-4”) Good stand, cut (2.5”) Good stand, cut (3-4”) Good stand, uncut (4-5”) Good stand, uncut (12-18”) Good stand, cut (3-4”) Good stand, cut (3-4”) E Bermudagrass Bermudagrass Good stand, cut (1.5”) Burned stubble Modified from: USDA-SCS, 1969. Engineering Field Manual. Appendices 8.05.9 Table 8.05d Maximum Permissible Velocities for Unprotected Soils in Existing Channels. Materials Maximum Permissible Velocities (fps) Fine Sand (noncolloidal) Sand Loam (noncolloidal) Silt Loam (noncolloidal) Ordinary Firm Loam Fine Gravel Stiff Clay (very colloidal) Graded, Loam to Cobbles (noncolloidal) Graded, Silt to Cobbles (colloidal) Alluvial Silts (noncolloidal) Alluvial Silts (colloidal) Coarse Gravel (noncolloidal) Cobbles and Shingles 2.5 2.5 3.0 3.5 5.0 5.0 5.0 5.5 3.5 5.0 6.0 5.5 Sample Problem 8.05a Design of a Grass-lined Channel. Given: Design Q10 = 16.6 cfs Proposed channel grade = 2% Proposed vegetation: Tall fescue Soil: Creedmoor (easily erodible) Permissible velocity, Vp = 4.5 ft/s (Table 8.05a) Retardance class: “B” uncut, “D” cut (Table 8.05c). Trapezoidal channel dimensions: designing for low retardance condition (retardance class D) design to meet Vp. Find: Channel dimensions Solution: Make an initial estimate of channel size A = Q/V, 16.6 cfs/4.5 ft/sec = 3.69 ft2 Try bottom width = 3.0 ft w/side slopes of 3:1 Z = 3 A = bd + Zd2 P = b + 2d Z2 + 1 R = AP An iterative solution using Figure 8.05a to relate flow depth to Manning’s n proceeds as follows: Manning’s equation is used to check velocities. *From Fig. 8.05c, pg. 8.05.7, Retardance Class d (VR=4.5x0.54=2.43) d (ft) A (ft 2) R (ft) *n Vt (fps) Q (cfs) Comments 0.8 4.32 0.54 0.043 3.25 14.0 V<Vp OK, Q<Q10 (too small, try deeper channel) 0.9 5.13 0.59 0.042 3.53 18.10 V<Vp, OK, Q>Q10, OK Now design for high retardance (class B): For the ease of construction and maintenance assume and try d = 1.5 ft and trial velocity Vt = 3.0 ft/sec d (ft) A (ft 2) R (ft)Vt (fps)n V (fps) Q (cfs) Comments 1.5 11.25 0.90 3.0 2.0 1.6 **1.5 0.08 0.11 0.12 0.13 2.5 1.8 1.6 1.5 28 20 18 17 reduce Vtreduce Vt Q>Q10 OK ** These assumptions = actual V (fps.) (chart continued on next page) 8 8.05.10 Rev. 12/93 (continued) Sample Problem 8.05a Design of a Grass-lined Channel. Channel summary: Trapezoidal shape, Z = 3, b = 3 ft, d = 1.5 ft, grade = 2% Note: In Sample Problem 8.05a the “n-value” is first chosen based on a permissible velocity and not a design velocity criteria. Therefore, the use of Table 8.05c may not be as accurate as individual retardance class charts when a design velocity is the determining factor. Tractive Force Procedure The design of riprap-lined channels and temporary channel linings is based on analysis of tractive force. NOTE: This procedure is for uniform flow in channels and is not to be used for design of deenergizing devices and may not be valid for larger channels. To calculate the required size of an open channel, assume the design flow is uniform and does not vary with time. Since actual flow conditions change through the length of a channel, subdivide the channel into design reaches as appropriate. PERMISSIBLE SHEAR STRESS The permissible shear stress, Td, is the force required to initiate movement of the lining material. Permissible shear stress for the liner is not related to the erodibility of the underlying soil. However, if the lining is eroded or broken, the bed material will be exposed to the erosive force of the flow. COMPUTING NORMAL DEPTH The first step in selecting an appropriate lining is to compute the design flow depth (the normal depth) and determine the shear stress. Normal depths can be calculated by Manning’s equation as shown for trapezoidal channels in Figure 8.05d. Values of the Manning’s roughness coefficient for different ranges of depth are provided in Table 8.05e for temporary linings and Table 8.05f for riprap. The coefficient of roughness generally decreases with increasing flow depth. n value for Depth Ranges* Table 8.05e Manning’s Roughness Coefficients for Temporary Lining Materials 0-0.5 ft 0.5-2.0 ft >2.0 ft Lining Type Woven Paper Net Jute Net Fiberglass Roving Straw with Net Curled Wood Mat Synthetic Mat 0.016 0.028 0.028 0.065 0.066 0.036 0.015 0.022 0.021 0.033 0.035 0.025 0.015 0.019 0.019 0.025 0.028 0.021 * Adapted from: FHWA-HEC 15, Pg. 37 - April 1988 8 8.05.12 Rev. 12/93 Table 8.05f Manning’s Roughness Coefficient n - value n value for Depth Ranges Lining Category Lining Type 0-0.5 ft (0-15 cm) 0.5-2.0 ft (15-60 cm) 2.0 ft (>60 cm) Rigid Concrete Grouted Riprap Stone Masonry Soil Cement Asphalt 0.015 0.040 0.042 0.025 0.018 0.013 0.030 0.032 0.022 0.016 0.013 0.028 0.030 0.020 0.016 Unlined Bare Soil Rock Cut 0.023 0.045 0.020 0.035 0.020 0.025 Gravel Riprap 1-inch (2.5-cm) D502-inch (5-cm) D50 0.044 0.066 0.033 0.041 0.030 0.034 Rock Riprap 6-inch (15-cm) D5012-inch (30-cm) D50 0.104 -- 0.069 0.078 0.035 0.040 Note: Values listed are representative values for the respective depth ranges. Manning’s roughness coefficients, n, vary with the flow depth. DETERMINING SHEAR STRESS Shear stress, T, at normal depth is computed for the lining by the following equation: T = yds Td = Permissible shear stress where: T = shear stress in lb/ft2 y = unit weight of water, 62.4 lb/ft3 d = flow depth in ft s = channel gradient in ft/ft If the permissible shear stress, Td, given in Table 8.05g is greater than the computed shear stress, the riprap or temporary lining is considered acceptable. If a lining is unacceptable, select a lining with a higher permissible shear stress and repeat the calculations for normal depth and shear stress. In some cases it may be necessary to alter channel dimensions to reduce the shear stress. Computing tractive force around a channel bend requires special considerations because the change in flow direction imposes higher shear stress on the channel bottom and banks. The maximum shear stress in a bend, Tb, is given by the following equation: Tb = KbT where: Tb = bend shear stress in lb/ft2 kb = bend factor T = computed stress for straight channel in lb/ft2 The value of kb is related to the radius of curvature of the channel at its center line, Rc, and the bottom width of the channel, B, Figure 8.05e. The length of channel requiring protection downstream from a bend, Lp, is a function of the roughness of the lining material and the hydraulic radius as shown in Figure 8.05f. Appendices Rev. 12/93 8.05.13 Table 8.05g Permissible Shear Stresses for Riprap and Temporary Liners Permissible Unit Shear Stress, Td Lining Category Lining Type (lb/ft2) Temporary Woven Paper Net Jute Net Fiberglass Roving: Single Double Straw with Net Curled Wood mat Synthetic Mat 0.15 0.45 0.60 0.85 1.45 1.55 2.00 d50 Stone Size (inches) Gravel Riprap 1 2 0.33 0.67 Rock Riprap 6 9 12 15 18 21 24 2.00 3.00 4.00 5.00 6.00 7.80 8.00 Adapted From: FHWA, HEC-15, April 1983, pgs. 17 & 37. Design Procedure- Temporary Liners The following is a step-by-step procedure for designing a temporary liner for a channel. Because temporary liners have a short period of service, the design Q may be reduced. For liners that are needed for six months or less, the 2-year frequency storm is recommended. Step 1. Select a liner material suitable for site conditions and application. Determine roughness coefficient from manufacturer’s specifications or Table 8.05e, page 8.05.10. Step 2. Calculate the normal flow depth using Manning’s equation (Figure 8.05d). Check to see that depth is consistent with that assumed for selection of Manning’s n in Figure 8.05d, page 8.05.11. For smaller runoffs Figure 8.05d is not as clearly defined. Recommended solutions can be determined by using the Manning equation. Step 3. Calculate shear stress at normal depth. Step 4. Compare computed shear stress with the permissible shear stress for the liner. Step 5. If computed shear is greater than permissible shear, adjust channel dimensions to reduce shear, or select a more resistant lining and repeat steps 1 through 4. Design of a channel with temporary lining is illustrated in Sample Problem 8.05b, page 8.05.14. Temporary Sediment Basins Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 1 of 7 12/9/2016 (Initial Submittal) Calculation Title: Temporary Sediment Basins Calculation Summary: The temporary sediment basins were designed in accordance with the North Carolina Department of Environment and Natural Resources (NCDENR) “Erosion and Sediment Control Planning and Design Manual”. Notes: Revision Log: No. Description Originator Verifier Technical Reviewer 0 Initial Submittal – 12/9/2016 Chris Jordan Stephanie Stanwick Cedric H. Ruhl Temporary Sediment Basins Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 2 of 7 12/9/2016 (Initial Submittal) OBJECTIVE: The objective of this calculation is to design the temporary sediment basins for the interim closure conditions of the Primary and Secondary ash basins METHOD: The temporary sediment basins were designed in accordance with the North Carolina Department of Environment and Natural Resources (NCDENR) “Erosion and Sediment Control Planning and Design Manual” [Ref. 1]. The 100-year storm event was also evaluated. DEFINITION OF VARIABLES: A = area; CN = curve number; d = flow depth; i = rainfall depth; L = length; n = Manning’s n; Q = flow; S = longitudinal slope; Tc = time of concentration; and V = velocity CALCULATIONS: 1.0 Design of temporary sediment basin The sediment basins will be installed prior to the full removal of the southern dike. Basins will be used as containment until final construction and stabilization of stormwater conveyance devices has been completed. Sediment basin outlets will be located at the final discharge point for the final, stabilized conditions. Land use and time of concentration for short term, interim conditions has been calculated in the “Interim Conditions Stormwater Calculation”. 1.1 Sediment Basin Configuration The sediment basin stage-storage curves are presented in the following table: Temporary Sediment Basins Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 3 of 7 12/9/2016 (Initial Submittal) Sediment Basin ID Elevation (ft) Surface Area (ft2) Incremental Storage Volume (ft3) Total Storage Volume (ft3) Notes 499.5 23,638 0 0 Bottom of Basin 502 91,335 143,716 143,716 Riser Invert 504 157,004 248,339 392,055 506 217,187 374,191 766,246 508 261,101 478,288 1,244,534 Emergency Spillway Invert 510 303,774 564,875 1,809,409 Crest of Basin 499.5 27,133 0 0 Bottom of Basin 502 123,530 188,329 188,329 Riser Invert 504 235,949 359,479 547,808 506 332,784 568,733 1,116,541 508 414,029 746,813 1,863,354 Emergency Spillway Invert 510 499,518 913,547 2,776,901 Crest of Basin 499.5 37,965 0 0 Bottom of Basin 502 127,980 207,431 207,431 Riser Invert 504 232,275 360,255 567,686 506 311,809 544,084 1,111,770 508 389,284 701,093 1,812,863 Emergency Spillway Invert 510 475,061 864,345 2,677,208 Crest of Basin 498.0 16,092 0 0 Bottom of Basin 502 67,831 167,846 167,846 Riser Invert 504 128,509 196,340 364,186 506 191,174 319,683 683,869 508 261,872 453,046 1,136,915 Emergency Spillway Invert 510 317,714 579,586 1,716,501 Crest of Basin SB-1 SB-2 SB-3 SB-4 Table 1: Sediment Basin Stage-Storage Information Sediment Basins 1 through 3 will consist of a 36 inch diameter vertical corrugated metal pipe (CMP) riser pipe that discharges through a culvert to the Dan River. Sediment Basin 4 discharges through an existing NPDES permitted outfall to the Dan River. The emergency spillway for each basin will consist of a trapezoidal shaped spillway with an invert elevation of 508, height of 2 feet, bottom width of 10 feet and side slopes of 10H:1V. 1.2 Sediment Basin Hydraulic Performance The sediment basin hydraulic performance was evaluated for the 2-year, 10-year, 25-year, and 100-year, 24-hour storm events based on NOAA Atlas 14 rainfall data [Ref. 5]. The sediment basin hydraulic performance was evaluated using HydroCAD software, the results of which are presented in Reference 3 and summarized in the following table: Temporary Sediment Basins Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 4 of 7 12/9/2016 (Initial Submittal) Sediment Basin ID Elevation (ft)Notes 499.50 Bottom of Basin 501.38 Water Surface Elevation from 2-Year Storm Event 502.00 Riser Invert 502.07 Water Surface Elevation from 10-Year Storm Event 502.31 Water Surface Elevation from 25-Year Storm Event 502.58 Water Surface Elevation from 100-Year Storm Event 508.00 Emergency Spillway Invert 510.00 Crest of Basin 499.50 Bottom of Basin 502 Riser Invert 502.22 Water Surface Elevation from 2-Year Storm Event 502.8 Water Surface Elevation from 10-Year Storm Event 503.66 Water Surface Elevation from 25-Year Storm Event 504.05 Water Surface Elevation from 100-Year Storm Event 508 Emergency Spillway Invert 510 Crest of Basin 499.50 Bottom of Basin 502 Riser Invert 502.8 Water Surface Elevation from 2-Year Storm Event 503.79 Water Surface Elevation from 10-Year Storm Event 504.48 Water Surface Elevation from 25-Year Storm Event 505.63 Water Surface Elevation from 100-Year Storm Event 508 Emergency Spillway Invert 510 Crest of Basin 499.50 Bottom of Basin 502 Riser Invert 502.04 Water Surface Elevation from 2-Year Storm Event 502.22 Water Surface Elevation from 10-Year Storm Event 502.4 Water Surface Elevation from 25-Year Storm Event 502.73 Water Surface Elevation from 100-Year Storm Event 508 Emergency Spillway Invert 510 Crest of Basin Table 2: Sediment Basin Hydraulic Performance SB-1 SB-2 SB-3 SB-4 Each sediment basin has enough capacity to store the 100-year storm event without activating the emergency spillway. Sediment basin SB-1 can store a 2-year storm event without activating the riser pipe spillway. 1.3 Skimmer Design The skimmer will discharge at a constant rate depending on the orifice size as shown in the following table: Temporary Sediment Basins Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 5 of 7 12/9/2016 (Initial Submittal) Sediment Basin ID Volume to De-Water (ft3) Orifice Size (in) [Ref. 4] Discharge Rate (ft3/hr) Dewatering Time (hours) [Ref. 4] Dewatering Time (days) [Ref. 4] 1.5 72 1,996 83.2 2.0 137 1,051 43.8 2.5 260 553 23.1 3.0 407 353 14.7 4.0 838 172 7.1 5.0 1,368 105 4.4 6.0 2,160 67 2.8 8.0 4,082 35 1.5 1.5 72 2,616 109.0 2.0 137 1,377 57.4 2.5 260 725 30.2 3.0 407 462 19.3 4.0 838 225 9.4 5.0 1,368 138 5.7 6.0 2,160 87 3.6 8.0 4,082 46 1.9 1.5 72 2,881 120.0 2.0 137 1,516 63.2 2.5 260 799 33.3 3.0 407 509 21.2 4.0 838 248 10.3 5.0 1,368 152 6.3 6.0 2,160 96 4.0 8.0 4,082 51 2.1 1.5 72 2,331 97.1 2.0 137 1,227 51.1 2.5 260 646 26.9 3.0 407 412 17.2 4.0 838 200 8.3 5.0 1,368 123 5.1 6.0 2,160 78 3.2 8.0 4,082 41 1.7 SB-4 Table 3: Skimmer Design SB-1 143,716 SB-2 SB-3 188,329 207,431 167,846 All four sediment basins were selected to use a skimmer with a 6-inch orifice for dewatering times in excess of 48 hours. 1.4 Sediment Basin Design Summary The sediment basin was designed to meet the requirements of the NCDENR “Erosion and Sediment Control Planning and Design Manual” [Ref. 1] as summarized in the following table: Temporary Sediment Basins Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 6 of 7 12/9/2016 (Initial Submittal) Sediment Basin ID Minimum Design Requirement Actual Design Requirement Maximum drainage area = 100 acres 11.14 Maximum design life = 3 years Less than 3 Years Minimum Design Storm = 10-year 100-year Volume = 1,800 ft3/ac = 20,160 ft3 143,716 Surface Area = 435 ft2/cfs = 20,114 ft3 91,335 Minimum dewatering time = 48 hours 67.00 Maximum drainage area = 100 acres 39.46 Maximum design life = 3 years Less than 3 Years Minimum Design Storm = 10-year 100-year Volume = 1,800 ft3/ac = 36,012 ft4 188,329 Surface Area = 435 ft2/cfs =75,864 ft4 123,530 Minimum dewatering time = 48 hours 87.00 Maximum drainage area = 100 acres 98.61 Maximum design life = 3 years Less than 3 Years Minimum Design Storm = 10-year 100-year Volume = 1,800 ft3/ac = 33,120 ft5 207,431 Surface Area = 435 ft2/cfs = 64,262 ft5 127,980 Minimum dewatering time = 48 hours 96.00 Maximum drainage area = 100 acres 16.81 Maximum design life = 3 years Less than 3 Years Minimum Design Storm = 10-year 100-year Volume = 1,800 ft3/ac = 26,640 ft6 167,846 Surface Area = 435 ft2/cfs = 24,917 ft6 67,831 Minimum dewatering time = 48 hours 78.00 SB-2 SB-3 SB-4 Table 4: Sediment Basin Design Summary SB-1 The proposed sediment basins meet the design requirements. 1.5 Anti-Flotation Block Sediment basin risers will be anchored to the ground using antiflotation devices. Sediment Basin 4 will use a pre-existing concrete antiflotation device while Sediment Basins 1, 2 and 3 will use a 5 ft x 5 ft x 1.5 ft concrete block. The design of the antiflotation block is summarized in the following table: Sediment Basin ID Riser Diameter (ft) Riser Height (ft) Mass of Water Displaced by Riser (lbs) Block Length (ft) Block Width (ft) Block Height (ft) Buoyant Unit Weight of Block (pcf) Mass of Block (Rectangle) (lbs) Safety Factor Against Flotation (Rectangle) SB-1 3.0 2.5 1,103 5.0 5.0 1.5 87.6 3,285 2.98 SB-2 3.0 2.5 1,103 5.0 5.0 1.5 87.6 3,285 2.98 SB-3 3.0 2.5 1,103 5.0 5.0 1.5 87.6 3,285 2.98 Table 5: Rectangular Anti-Flotation Block Design Summary The safety factor against flotation is 2.98, which is greater than the minimum required safety factor of 1.1 [Ref. 1]. DISCUSSION: The temporary sediment basins were designed in accordance with the North Carolina Department of Environment and Natural Resources (NCDENR) “Erosion and Sediment Control Planning and Design Manual”. Temporary Sediment Basins Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 7 of 7 12/9/2016 (Initial Submittal) REFERENCES: 1. North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. 2. United States Department of Agriculture, “Urban Hydrology for Small Watersheds”, Technical Release 44, June 1986. 3. HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. 4. J.W. Faircloth & Son, Inc. “Determining the Skimmer Size and the Required Orifice for the Faircloth Skimmer Surface Drain” Revised November 2007. 5. Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. REFERENCE 1 North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. Appendices Rev. 6/06 8.03.17 table 8.03e Runoff curve numbers of urban areas1 ---------------------------------------Cover Description------------------------- Curve number for ---------hydrologic soil group-------- Cover type and hydrologic condition Average percent impervious area2 ABCD Fully developed urban areas (vegetation established) Open space (lawns, parks, golf courses, cemeteries, etc.) 3: Poor condition (grass cover < 50%) .............................68 79 86 89 Fair condition (grass cover 50% to 75%) .....................49 69 79 84 Good condition (grass cover > 75%) ............................39 61 74 80 Impervious areas: Paved parking lots, roofs, driveways, etc. (excluding right-of-way) ...............................................98 98 98 98 Streets and roads: Paved; curbs and storm sewers (excluding right-of-way) ..................................................................98 98 98 98 Paved; open ditches (including right-of-way) ................83 89 92 93 Gravel (including right-of-way) ......................................76 85 89 91 Dirt (including right-of-way) ...........................................72 82 87 89 Urban districts: Commercial and business ................................................. 85 89 92 94 95 Industrial ...........................................................................72 81 88 91 93 Residential districts by average lot size: 1/8 acre or less (town houses) ......................................... 65 77 85 90 92 1/4 acre ............................................................................ 38 61 75 83 87 1/3 acre .............................................................................30 57 72 81 86 1/2 acre .............................................................................25 54 70 80 85 1 acre ...............................................................................20 51 68 79 84 2 acres ..............................................................................12 46 65 77 82 Developing urban areas Newly graded areas (pervious areas only, no vegetation) 4 ..............................77 86 91 94 Idle lands (CN’s are determined using cover types similar to those in table 2-2c). 1. Average runoff condition, and Ia = 0.2S. 2. The average percent impervious area shown was used to develop the composite CN’s. Other assumptions are as follows: impervious areas are directly connected to the drainage system, impervious areas have a CN of 98, and pervious areas are considered equivalent to open space in good hydrologic condition. CN’s for other combinations of conditions may be computed using Figure 8.03c or 8.03d. 3. CN’s shown are equivalent to those of pasture. Composite CN’s may be computed for other combinations of open space cover type. 4. Composite CN’s to use for the design of temporary measures during grading and construction should be computed using Figure 8.03c or 8.03d based on the degree of development (impervious area percentage) and the CN’s for the newly graded pervious areas. Practice Standards and Specifications 6.61 Definition An earthen embankment suitably located to capture sediment with a primary spillway system consisting of a riser and barrel pipe. Purpose To retain sediment on the construction site, and prevent sedimentation in off-site streams, lakes, and drainageways. Conditions Where Special limitation – This practice applies only to the design and installation of Practice Applies sediment basins where failure of the structure would not result in the loss of life, damage to homes or buildings, or interrupt the use of public roads or utilities. All high hazard potential dams and structures taller than 25 feet, and that also have a maximum storage capacity of 50 acre-feet or more are subject to the N.C. Dam Safety . Law of 1967 Sediment basins are needed where drainage areas exceed design criteria of other measures. Specific criteria for installation of a sediment basin are as follows: • Keep the drainage area less than 100 acres; • Ensure that basin location provides a convenient concentration point for sediment-laden flows from the area served; • Ensure that basin location allows access for sediment removal and proper disposal under all weather conditions; and • Keep the basin life limited to 3 years, unless it is designed as a permanent structure; Do not locate sediment basins in intermittent or perennial streams. Planning Select key locations for sediment basins during initial site evaluation. Install Considerations basins before any land-disturbance takes place within the drainage area. Select basin sites to capture sediment from all areas that are not treated adequately by other sediment controls. Always consider access for cleanout and disposal of the trapped sediment. Locations where a pond can be formed by constructing a low dam across a natural swale are generally preferred to sites that require excavation. Where practical, divert sediment-free runoff away from the basin. Sediment trapping efficiency is primarily a function of sediment particle size and the ratio of basin surface area to inflow rate. Therefore, design the basin to have a large surface area for its volume. Figure 6.61a shows the relationship between the ratio of surface area to peak inflow rate and trap efficiency observed by Barfield and Clar (1986). Sediment basins with an expected life greater than 3 years should be designed as permanent structures. Often sediment basins are converted to stormwater ponds. In these cases, the structure should be designed by a qualified professional engineer experienced in the design of dams. Permanent ponds and artificial lakes are beyond the scope of this practice standard. USDA Soil Conservation Services Practice Standard Ponds Code No. 378 provides criteria for design of permanent ponds. SEDIMENT BASIN Rev. 5/13 6.61.1 Practice Standards and Specifications Figure 6.61a Relationship between the ratio of surface area to peak inflow rate and trap efficiency. Design Criteria Summary: Primary Spillway: Riser/Barrel Pipe Temporary Sediment Basin: Maximum Drainage Area: 100 acres Minimum Sediment Storage Volume: 1800 cubic feet per acre of disturbed area Minimum Surface Area: 435 square feet per cfs of Q 10 Minimum L/W Ratio: 2:1 peak inflow Maximum L/W Ratio: 6:1 Minimum Depth: 2 feet Dewatering Mechanism: Skimmer(s) attached at bottom of riser pipe or flashboard riser Minimum Dewatering Time: 48 hours Baffles Required: 3 baffles* (*Note: Basins less than 20 feet in length may use 2 baffles.) Drainage areas- Limit drainage areas to 100 acres. Design basin life- Ensure a design basin life of 3 years or less. Dam height- Limit dam height to 15 feet. Height of a dam is measured from the top of the dam to the lowest point at the downstream toe. Volume is measured from the top of the dam when determining if the dam impounds enough water to be regulated by the Dam Safety Law. Rev. 5/136.61.2 Practice Standards and Specifications Basin locations- Select areas that: • Provide capacity for sediment storage from as much of the planned disturbed area as practical; • Exclude runoff from undisturbed areas where practical; • Provide access for sediment removal throughout the life of the project and; • Interfere minimally with construction activities. Basin shape- Ensure that the flow length to basin width ratio is at least 2:1 to improve trapping efficiency. This basin shape may be attained by site selection or excavation. Length is measured at the elevation of the principal spillway. Storage volume- Ensure that the sediment storage volume of the basin, as measured to the elevation of the crest of the principal spillway, is at least 1,800 ft3/acre for the disturbed area draining into the basin (1,800 ft3 Remove sediment from the basin when approximately one-half of the storage volume has been filled. is equivalent to a ½ inch of sediment per acre of basin drainage area). Spillway capacity- The spillway system must carry the peak runoff from the 10- year storm with a minimum 1 foot freeboard in the emergency spillway. Base runoff computations on the disturbed soil cover conditions expected during the effective life of the structure. Principal spillway- Construct the principal spillway with a vertical riser connected to a horizontal barrel that extends through the embankment and outlets beyond the downstream toe of the dam, or an equivalent design. • Capacity- The primary spillway system must carry the peak runoff from the 2-year storm, with the water surface at the emergency spillway crest elevation. Sediment cleanout elevation- Show the distance from the top of the riser to the pool level when the basin is 50 percent full. This elevation should also be marked in the field with a permanent stake set at this ground elevation (not the top of the stake). Crest elevation- Keep the crest elevation of the riser a minimum of 1 foot below the crest elevation of the emergency spillway. Riser and Barrel- Keep the minimum barrel size at 15 inches for corrugated metal pipe or 12 inches for smooth wall pipe to facilitate installation and reduce potential for failure from blockage. Ensure that the pipe is capable of withstanding the maximum external loading without yielding, buckling or cracking. To improve the efficiency of the principal spillway system, make the cross-sectional area of the riser at least 1.5 times that of the barrel. The riser should be sized to minimize the range of stages when orifice flow will occur. Pipe Connections- Ensure that all conduit connections are watertight. Rod and lug type connector bands with gaskets are preferred for corrugated metal pipe to assure watertightness under maximum loading and internal pressure. Do not use dimple (universal) connectors under any circumstances. • Trash guard- It is important that a suitable trash guard be installed to prevent the riser and barrel pipes from becoming clogged. Install a trash guard on the top of the riser to prevent trash and other debris from Rev. 5/13 6.61.3 Practice Standards and Specifications clogging the conduit. A combination anti-vortex device and trash guard improves the efficiency of the principal spillway and protects against trash intake. • Protection against piping- Install at least one watertight anti-seep collar with a minimum projection of 1.5 feet around the barrel of principal spillway conduits, 8 inches or larger in diameter. Locate the anti-seep collar slightly downstream from the dam center line. A properly designed drainage diaphragm installed around the barrel may be used instead of an anti-seep collar when it is appropriate. • Protection against flotation- Secure the riser by an anchor with buoyant weight greater than 1.1 times the water displaced by the riser. • Outlet- Protect the outlet of barrel against erosion. Discharge velocities must be within allowable limits for the receiving stream (References: Outlet Protection). Basin dewatering- The basin should be provided with a mechanism to dewater the basin from the water surface. Previously sediment basins were dewatered with a perforated riser. These were designed to dewater relatively quickly and draw water from the entire water column. Dewatering from the surface provides greater trapping efficiency. Two common methods are a skimmer and flashboard riser. • Skimmer- A floating skimmer should be attached to the base of the riser. The orifice in the skimmer will control the rate of dewatering. The skimmer should be sized to dewater the basin in 2-5 days. A chart to determine the appropriate skimmer and orifice size is included on page 6.64.3. See Practice 6.64, Skimmer Basins for details on the installation of skimmers. Figure 6.61b Sediment basin with skimmer attached to riser for dewatering. Photo Credit: Town of Apex Rev. 5/136.61.4 Practice Standards and Specifications • Flashboard Riser- A different approach is to use a flashboard riser, which forces the basin to fill to a given level before the water tops the riser. In this way it is similar to a solid riser, but with the option of being able to lower the water level in the basin when accumulated sediment must be removed. Flashboard risers are usually fabricated as a box or as a riser pipe cut in half. The open face has slots on each side into which boards or “stop logs” are placed, forcing the water up and over them. This device should be sized the same way as a typical riser. Forcing the water to exit the sediment basin from the top of the water column has the same advantages in sediment capture as the skimmer. A flashboard riser basin will have an adjustable, permanent pool which also improves basin efficiency. This method is a disadvantage when the sediment needs to be removed because the operator may need to remove the boards down to the sediment level to drain the basin. Flashboard risers are a good option for stilling basins for pump discharges, or when sandy soil conditions will allow dewatering of the basin through infiltration. They should not be selected when the basin will have to be cleaned frequently, or when located in clay soils. Figure 6.61c Flashboard Riser installation example. Photo credit: NC State University Rev. 5/13 6.61.5 Practice Standards and Specifications Emergency spillway- Construct the entire flow area of the emergency spillway in undisturbed soil (not fill). Make the cross section trapezoidal with side slopes of 3:1 or flatter. Make the control section of the spillway straight and at least 20 feet long. The inlet portion of the spillway may be curved to improve alignment, but ensure that the outlet section is straight due to supercritical flow in this portion. • Capacity- The minimum design capacity of the emergency spillway must be the peak rate of runoff from the 10-year storm, less any reduction due to flow in the principal spillway. In no case should freeboard of the emergency spillway be less than 1 foot above the design depth of flow. • Velocity- Ensure that the velocity of flow discharged from the basin is non-erosive for the existing conditions. When velocities exceed that allowable for the receiving areas, provide outlet protection (References: Outlet Protection). Embankment- • Cut-off trench- Excavate a trench at the center line of the embankment. Ensure that the trench is in undisturbed soil and extends through the length of the embankment to the elevation of the riser crest at each end. A minimum of depth of 2 feet is recommended. • Top width- The minimum top width of the dam is shown in Table 6.61a. • Freeboard- Ensure that the minimum difference between the design water elevation in the emergency spillway and the top of the settled embankment is 1 foot. • Side slopes- Make the side slopes of the impoundment structure 2.5:1 or flatter (Figure 6.61d). • Allowance for settlement- Increase the constructed height of the fill at least 10 percent above the design height to allow for settlement. • Erosion protection- Stabilize all areas disturbed by construction (except the lower ½ of the sediment pool) by suitable means immediately after completing the basin (References: Surface Stabilization). Design information included in the Appendices may be used to develop final plans for sediment basins (References: Appendices). Trap efficiency- Improve sediment basin trapping efficiency by employing the following considerations in the basin design: • Surface area- In the design of the settling pond, allow the largest surface area possible. Studies of Barfield and Clar (1986) indicate that surface area (in acres) should be larger than 0.01 times the peak inflow rate in cfs, or 435 sq. ft. per cfs of peak flow. • Length- The length to width ratio should be between 2:1 to 6:1. Fill Height Minimum Top Width less than 10 ft 8.0 ft 10 ft to 15 ft 10.0 ft Table 6.61a Acceptable Dimensions for Basin Embankment Rev. 5/136.61.6 Practice Standards and Specifications • Baffles- Provides a minimum of three porous baffles to evenly distribute flow across the basin and reduces turbulence. Basins less than 20 feet in length may use 2 baffles . • Inlets- Locate the sediment inlets to the basin the greatest distance from the principal spillway. • Inflow rate- Reduce the inflow velocity and divert all sediment-free runoff. Construction 1. Site preparations- Clear, grub, and strip topsoil from areas under the Specifications embankment to remove trees, vegetation, roots, and other objectionable material. Delay clearing the pool area until the dam is complete and then remove brush, trees, and other objectionable materials to facilitate sediment cleanout. Stockpile all topsoil or soil containing organic matter for use on the outer shell of the embankment to facilitate vegetative establishment. Place temporary sediment control measures below the basin as needed. 2. Cut-off trench- Excavate a cut-off trench along the center line of the earth fill embankment. Cut the trench to stable soil material, but in no case make it less than 2 feet deep. The cut-off trench must extend into both abutments to at least the elevation of the riser crest. Make the minimum bottom width wide enough to permit operation of excavation and compaction equipment, but in no case less than 2 feet. Make side slopes of the trench no steeper than 1:1. Compaction requirements are the same as those for the embankment. Keep the trench dry during backfilling and compaction operations. 3. Embankment- Take fill material from the approved areas shown on the plans. It should be clean mineral soil, free of roots, woody vegetation, rocks, and other objectionable material. Scarify areas on which fill is to be placed before placing fill. The fill material must contain sufficient moisture so it can be formed by hand into a ball without crumbling. If water can be squeezed out of the ball, it is too wet for proper compaction. Place fill material in 6 to 8 inch continuous layers over the entire length of the fill area and compact it. Compaction may be obtained by routing the construction hauling equipment over the fill so that the entire surface of each layer is traversed by at least one wheel or tread track of heavy equipment, or a compactor may be used. Construct the embankment to an elevation 10 percent higher than the design height to allow for settling. 4. Conduit spillways- Securely attach the riser to the barrel or barrel stub to make a watertight structural connection. Secure all connections between barrel sections by approved watertight assemblies. Place the barrel and riser on a firm, smooth foundation of impervious soil. Do not use pervious material such as sand, gravel, or crushed stone as backfill around the pipe or anti-seep collars. Place the fill material around the pipe spillway in 4-inch layers, and compact it under and around the pipe to at least the same density as the adjacent embankment. Care must be taken not to raise the pipe from firm contact with its foundation when compacting under the pipe haunches. • Dewatering- Allow the maximum reasonable detention period before the basin is completely dewatered-at least 48 hours. Rev. 5/13 6.61.7 Practice Standards and Specifications Place a minimum depth of 2 feet of compacted backfill over the pipe spillway before crossing it with construction equipment. Anchor the riser in place by concrete or other satisfactory means to prevent flotation. In no case should the pipe conduit be installed by cutting a trench through the dam after the embankment is complete. 5. Emergency spillway- Install the emergency spillway in undisturbed soil. The achievement of planned elevations, grade, design width, and entrance and exit channel slopes are critical to the successful operation of the emergency spillway. 6. Inlets- Discharge water into the basin in a manner to prevent erosion. Use diversions with outlet protection to divert sediment-laden water to the upper end of the pool area to improve basin trap efficiency (References: Runoff Control Measures and Outlet Protection). 7. Erosion control- Construct the structure so that the disturbed area is minimized. Divert surface water away from bare areas. Complete the embankment before the area is cleared. Stabilize the emergency spillway embankment and all other disturbed areas above the crest of the principal spillway immediately after construction (References: Surface Stabilization). 8. Install porous baffles as specified in Practice 6.65, Porous Baffles. 9. Safety- Sediment basins may attract children and can be dangerous. Avoid steep side slopes, and fence and mark basins with warning signs if trespassing is likely. Follow all state and local requirements. Maintenance Inspect temporary sediment basins at least weekly and after each significant (1/2 inch or greater) rainfall event and repair immediately. Remove sediment and restore the basin to its original dimensions when it accumulates to one-half the design depth. Place removed sediment in an area with sediment controls. Check the embankment, spillways, and outlet for erosion damage, and inspect the embankment for piping and settlement. Make all necessary repairs immediately. Remove all trash and other debris from the riser and pool area. Rev. 5/136.61.8 NO T T O S C A L E NO T E S 1. S E E D A N D P L A C E M A T T I N G F O R E R O S I O N C O N T R O L O N I N T E R I O R A N D E X T E R I O R S I D E S L O P E S . 2. I N S T A L L A M I N I M U M O F 3 C O I R F I B E R B A F F L E S I N A C C O R D A N C E W I T H P R A C T I C E S T A N D A R D 6 . 6 5 . 3. I N S T A L L S K I M M E R A N D C O U P L I N G T O R I S E R S T R U C T U R E O R D I R E C T L Y I N T O E M B A N K M E N T 1 F T . F R O M B O T T O M O F B A S I N . 4. T H E A R M P I P E S H A L L H A V E A M I N I M U M L E N G T H O F 6 F T . B E T W E E N T H E S K I M M E R A N D C O U P L I N G . SE C T I O N A L V I E W PL A N V I E W 4’ MA X . 4’ 4’ 1’ 1’ 6’ M I N . ST E E L P O S T S ( Q U A N T I T Y V A R . ) SK I M M E R ( S I Z E V A R . ) RI S E R S T R U C T U R E ST O N E E N E R G Y DI S S I P A T O R EM B A N K M E N T PL A S T I C S L O P E D R A I N P I P E (P R A C T I C E S T A N D A R D 6 . 3 2 ) OR GE O T E X T I L E L I N I N G TE M P O R A R Y O R PE R M A N E N T D I T C H CO I R F I B E R B A F F L E S (P R A C T I C E S T A N D A R D 6 . 6 5 ) ST O N E P A D (b e l o w s k i m m e r ) WO O D S T A K E OR M E T A L P O S T RO P E BA R R E L PI P E 2.5 : 1 S L O P E M A X 2 . 5 : 1 S L O P E M A X TO P O F E M B A N K M E N T RI S E R S T R U C T U R E TR A S H R A C K SK I M M E R CL A S S B S T O N E P A D (4 ’ X 4 ’ X 1 ’ M I N . ) EM E R G E N C Y S P I L L W A Y AN T I F L O T A T I O N B L O C K FR E E B O A R D - 1’ M I N . EM E R G E N C Y S P I L L W A Y ST A B I L I Z E D OU T L E T AN T I - S E E P CO L L A R CU T - O F F TR E N C H 2’ D E E P 1. 1 1 ’ M I N . Rev. 5/13 6.61.9 Practice Standards and Specifications Fi g u r e 6 . 6 1 d Se d i m e n t B a s i n ( w i t h R i s e r B a r r e l P i p e ) Practice Standards and Specifications References Surface Stabilization 6.10, Temporary Seeding 6.11, Permanent Seeding 6.12, Sodding 6.13, Trees, Shrubs, Vines, and Ground Covers Runoff Control Measures 6.20, Temporary Diversions 6.21, Permanent Diversions 6.22, Perimeter Dike Outlet Protection 6.40, Level Spreader 6.41, Outlet Stabilization Structure Sediment Traps and Barriers 6.64, Skimmer Sediment Basin 6.65, Porous Baffles Appendices 8.01, Soil Information 8.02, Vegetation Tables 8.03, Estimating Runoff 8.04, Estimating Roughness Coefficients 8.05, Design of Stable Channels and Diversions 8.06, Design of Riprap Outlet Protection 8.07, Sediment Basin Design 8.08, The Sediment Control Law Barfield, B.J. and M.L. Clar. Erosion and Sediment Control Practices. Report to the Sediment and Stormwater Division – Maryland Water Resources Administration, 1986. Rev. 5/136.61.10 REFERENCE 2 United States Department of Agriculture, “Urban Hydrology for Small Watersheds”, Technical Release 44, June 1986. Technical Release 55 Urban Hydrology for Small Watersheds Time of Concentration and Travel TimeChapter 3 3–4 (210-VI-TR-55, Second Ed., June 1986) Manning’s equation is: V rs n =149 2 3 1 2.[eq. 3-4] where: V = average velocity (ft/s) r = hydraulic radius (ft) and is equal to a/pw a = cross sectional flow area (ft 2) pw = wetted perimeter (ft) s = slope of the hydraulic grade line (channel slope, ft/ft) n = Manning’s roughness coefficient for open channel flow. Manning’s n values for open channel flow can be obtained from standard textbooks such as Chow (1959) or Linsley et al. (1982). After average velocity is computed using equation 3-4, Tt for the channel seg- ment can be estimated using equation 3-1. Reservoirs or lakes Sometimes it is necessary to estimate the velocity of flow through a reservoir or lake at the outlet of a watershed. This travel time is normally very small and can be assumed as zero. Limitations •Manning’s kinematic solution should not be used for sheet flow longer than 300 feet. Equation 3-3 was developed for use with the four standard rainfall intensity-duration relationships. •In watersheds with storm sewers, carefully identify the appropriate hydraulic flow path to estimate Tc. Storm sewers generally handle only a small portion of a large event. The rest of the peak flow travels by streets, lawns, and so on, to the outlet. Consult a standard hydraulics textbook to determine average velocity in pipes for either pressure or nonpressure flow. •The minimum Tc used in TR-55 is 0.1 hour. •A culvert or bridge can act as a reservoir outlet if there is significant storage behind it. The proce- dures in TR-55 can be used to determine the peak flow upstream of the culvert. Detailed storage routing procedures should be used to determine the outflow through the culvert. Example 3-1 The sketch below shows a watershed in Dyer County, northwestern Tennessee. The problem is to compute Tc at the outlet of the watershed (point D). The 2-year 24-hour rainfall depth is 3.6 inches. All three types of flow occur from the hydraulically most distant point (A) to the point of interest (D). To compute Tc, first determine Tt for each segment from the following information: Segment AB: Sheet flow; dense grass; slope (s) = 0.01 ft/ft; and length (L) = 100 ft. Segment BC: Shallow concentrated flow; unpaved; s = 0.01 ft/ft; and L = 1,400 ft. Segment CD: Channel flow; Manning’s n = .05; flow area (a) = 27 ft2; wetted perimeter (pw) = 28.2 ft; s = 0.005 ft/ft; and L = 7,300 ft. See figure 3-2 for the computations made on worksheet 3. A B C D 7,300 ft1,400 ft100 ft (Not to scale) REFERENCE 3 HydroCAD 10.00 (build 9), HydroCAD Software Solutions LLC, 2013. 6P Sediment Basin (SB-2) 49P Sediment Basin 1 Routing Diagram for ST 1 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=502.22' Storage=4.967 af Inflow=105.30 cfs 6.269 afPond 6P: Sediment Basin (SB-2) Primary=3.09 cfs 1.451 af Secondary=0.00 cfs 0.000 af Outflow=3.09 cfs 1.451 af Peak Elev=501.38' Storage=2.115 af Inflow=38.41 cfs 2.116 afPond 49P: Sediment Basin 1 Primary=0.00 cfs 0.000 af Secondary=0.00 cfs 0.000 af Outflow=0.00 cfs 0.000 af Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 6P: Sediment Basin (SB-2) Inflow Area = 39.459 ac, 0.00% Impervious, Inflow Depth > 1.91" for 2-Year event Inflow = 105.30 cfs @ 11.98 hrs, Volume= 6.269 af Outflow = 3.09 cfs @ 15.68 hrs, Volume= 1.451 af, Atten= 97%, Lag= 222.2 min Primary = 3.09 cfs @ 15.68 hrs, Volume= 1.451 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 502.22' @ 15.68 hrs Surf.Area= 3.118 ac Storage= 4.967 af Plug-Flow detention time= 327.3 min calculated for 1.451 af (23% of inflow) Center-of-Mass det. time= 219.6 min ( 997.4 - 777.8 ) Volume Invert Avail.Storage Storage Description #1 499.50' 63.755 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.620 0.000 0.000 502.00 2.840 4.325 4.325 504.00 5.420 8.260 12.585 506.00 7.640 13.060 25.645 508.00 9.500 17.140 42.785 510.00 11.470 20.970 63.755 Device Routing Invert Outlet Devices #1 Primary 499.50'24.0" Round Culvert L= 103.0' CMP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 498.00' S= 0.0146 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 3.14 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=3.09 cfs @ 15.68 hrs HW=502.22' (Free Discharge) 1=Culvert (Passes 3.09 cfs of 19.81 cfs potential flow) 2=Orifice/Grate (Weir Controls 3.09 cfs @ 1.52 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 6P: Sediment Basin (SB-2) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 110 100 90 80 70 60 50 40 30 20 10 0 Inflow Area=39.459 ac Peak Elev=502.22' Storage=4.967 af 105.30 cfs 3.09 cfs3.09 cfs0.00 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 5HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 49P: Sediment Basin 1 Inflow Area = 11.140 ac, 0.00% Impervious, Inflow Depth > 2.28" for 2-Year event Inflow = 38.41 cfs @ 11.97 hrs, Volume= 2.116 af Outflow = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af, Atten= 100%, Lag= 0.0 min Primary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Peak Elev= 501.38' @ 20.00 hrs Surf.Area= 1.712 ac Storage= 2.115 af Plug-Flow detention time= (not calculated: initial storage exceeds outflow) Center-of-Mass det. time= (not calculated: no outflow) Volume Invert Avail.Storage Storage Description #1 499.50' 41.530 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.540 0.000 0.000 502.00 2.100 3.300 3.300 504.00 3.600 5.700 9.000 506.00 4.990 8.590 17.590 508.00 5.990 10.980 28.570 510.00 6.970 12.960 41.530 Device Routing Invert Outlet Devices #1 Primary 499.50'12.0" Round Culvert L= 116.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 497.00' S= 0.0216 '/' Cc= 0.900 n= 0.025, Flow Area= 0.79 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 1=Culvert ( Controls 0.00 cfs) 2=Orifice/Grate ( Controls 0.00 cfs) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 1 Printed 10/19/2015Prepared by AMEC Page 6HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 49P: Sediment Basin 1 Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 40 35 30 25 20 15 10 5 0 Inflow Area=11.140 ac Peak Elev=501.38' Storage=2.115 af 38.41 cfs 0.00 cfs0.00 cfs0.00 cfs Type II 24-hr 10-Year Rainfall=5.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 7HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=502.80' Storage=7.012 af Inflow=186.29 cfs 11.362 afPond 6P: Sediment Basin (SB-2) Primary=22.07 cfs 6.330 af Secondary=0.00 cfs 0.000 af Outflow=22.07 cfs 6.330 af Peak Elev=502.08' Storage=3.480 af Inflow=65.41 cfs 3.634 afPond 49P: Sediment Basin 1 Primary=0.76 cfs 0.154 af Secondary=0.00 cfs 0.000 af Outflow=0.76 cfs 0.154 af Type II 24-hr 10-Year Rainfall=5.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 8HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 6P: Sediment Basin (SB-2) Inflow Area = 39.459 ac, 0.00% Impervious, Inflow Depth > 3.46" for 10-Year event Inflow = 186.29 cfs @ 11.98 hrs, Volume= 11.362 af Outflow = 22.07 cfs @ 12.56 hrs, Volume= 6.330 af, Atten= 88%, Lag= 34.9 min Primary = 22.07 cfs @ 12.56 hrs, Volume= 6.330 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 502.80' @ 12.56 hrs Surf.Area= 3.873 ac Storage= 7.012 af Plug-Flow detention time= 198.2 min calculated for 6.330 af (56% of inflow) Center-of-Mass det. time= 121.5 min ( 886.2 - 764.7 ) Volume Invert Avail.Storage Storage Description #1 499.50' 63.755 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.620 0.000 0.000 502.00 2.840 4.325 4.325 504.00 5.420 8.260 12.585 506.00 7.640 13.060 25.645 508.00 9.500 17.140 42.785 510.00 11.470 20.970 63.755 Device Routing Invert Outlet Devices #1 Primary 499.50'24.0" Round Culvert L= 103.0' CMP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 498.00' S= 0.0146 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 3.14 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=22.07 cfs @ 12.56 hrs HW=502.80' (Free Discharge) 1=Culvert (Passes 22.07 cfs of 22.94 cfs potential flow) 2=Orifice/Grate (Weir Controls 22.07 cfs @ 2.93 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 10-Year Rainfall=5.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 9HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 6P: Sediment Basin (SB-2) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=39.459 ac Peak Elev=502.80' Storage=7.012 af 186.29 cfs 22.07 cfs22.07 cfs 0.00 cfs Type II 24-hr 10-Year Rainfall=5.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 10HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 49P: Sediment Basin 1 Inflow Area = 11.140 ac, 0.00% Impervious, Inflow Depth > 3.91" for 10-Year event Inflow = 65.41 cfs @ 11.97 hrs, Volume= 3.634 af Outflow = 0.76 cfs @ 20.00 hrs, Volume= 0.154 af, Atten= 99%, Lag= 481.6 min Primary = 0.76 cfs @ 20.00 hrs, Volume= 0.154 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Peak Elev= 502.08' @ 20.00 hrs Surf.Area= 2.163 ac Storage= 3.480 af Plug-Flow detention time= 684.9 min calculated for 0.154 af (4% of inflow) Center-of-Mass det. time= 364.2 min ( 1,117.4 - 753.2 ) Volume Invert Avail.Storage Storage Description #1 499.50' 41.530 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.540 0.000 0.000 502.00 2.100 3.300 3.300 504.00 3.600 5.700 9.000 506.00 4.990 8.590 17.590 508.00 5.990 10.980 28.570 510.00 6.970 12.960 41.530 Device Routing Invert Outlet Devices #1 Primary 499.50'12.0" Round Culvert L= 116.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 497.00' S= 0.0216 '/' Cc= 0.900 n= 0.025, Flow Area= 0.79 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=0.76 cfs @ 20.00 hrs HW=502.08' (Free Discharge) 1=Culvert (Passes 0.76 cfs of 3.29 cfs potential flow) 2=Orifice/Grate (Weir Controls 0.76 cfs @ 0.95 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 10-Year Rainfall=5.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 11HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 49P: Sediment Basin 1 Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 70 60 50 40 30 20 10 0 Inflow Area=11.140 ac Peak Elev=502.08' Storage=3.480 af 65.41 cfs 0.76 cfs0.76 cfs0.00 cfs Type II 24-hr 25-Year Rainfall=5.70"ST 1 Printed 10/19/2015Prepared by AMEC Page 12HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=503.01' Storage=7.861 af Inflow=209.05 cfs 12.823 afPond 6P: Sediment Basin (SB-2) Primary=23.98 cfs 7.739 af Secondary=0.00 cfs 0.000 af Outflow=23.98 cfs 7.739 af Peak Elev=502.12' Storage=3.559 af Inflow=72.94 cfs 4.062 afPond 49P: Sediment Basin 1 Primary=1.30 cfs 0.536 af Secondary=0.00 cfs 0.000 af Outflow=1.30 cfs 0.536 af Type II 24-hr 25-Year Rainfall=5.70"ST 1 Printed 10/19/2015Prepared by AMEC Page 13HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 6P: Sediment Basin (SB-2) Inflow Area = 39.459 ac, 0.00% Impervious, Inflow Depth > 3.90" for 25-Year event Inflow = 209.05 cfs @ 11.98 hrs, Volume= 12.823 af Outflow = 23.98 cfs @ 12.57 hrs, Volume= 7.739 af, Atten= 89%, Lag= 35.6 min Primary = 23.98 cfs @ 12.57 hrs, Volume= 7.739 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 503.01' @ 12.57 hrs Surf.Area= 4.146 ac Storage= 7.861 af Plug-Flow detention time= 192.5 min calculated for 7.739 af (60% of inflow) Center-of-Mass det. time= 119.1 min ( 881.1 - 762.0 ) Volume Invert Avail.Storage Storage Description #1 499.50' 63.755 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.620 0.000 0.000 502.00 2.840 4.325 4.325 504.00 5.420 8.260 12.585 506.00 7.640 13.060 25.645 508.00 9.500 17.140 42.785 510.00 11.470 20.970 63.755 Device Routing Invert Outlet Devices #1 Primary 499.50'24.0" Round Culvert L= 103.0' CMP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 498.00' S= 0.0146 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 3.14 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=23.98 cfs @ 12.57 hrs HW=503.01' (Free Discharge) 1=Culvert (Inlet Controls 23.98 cfs @ 7.63 fps) 2=Orifice/Grate (Passes 23.98 cfs of 31.40 cfs potential flow) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 25-Year Rainfall=5.70"ST 1 Printed 10/19/2015Prepared by AMEC Page 14HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 6P: Sediment Basin (SB-2) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 220 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=39.459 ac Peak Elev=503.01' Storage=7.861 af 209.05 cfs 23.98 cfs23.98 cfs 0.00 cfs Type II 24-hr 25-Year Rainfall=5.70"ST 1 Printed 10/19/2015Prepared by AMEC Page 15HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 49P: Sediment Basin 1 Inflow Area = 11.140 ac, 0.00% Impervious, Inflow Depth > 4.38" for 25-Year event Inflow = 72.94 cfs @ 11.97 hrs, Volume= 4.062 af Outflow = 1.30 cfs @ 17.09 hrs, Volume= 0.536 af, Atten= 98%, Lag= 306.9 min Primary = 1.30 cfs @ 17.09 hrs, Volume= 0.536 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Peak Elev= 502.12' @ 17.09 hrs Surf.Area= 2.191 ac Storage= 3.559 af Plug-Flow detention time= 491.7 min calculated for 0.536 af (13% of inflow) Center-of-Mass det. time= 286.8 min ( 1,037.2 - 750.4 ) Volume Invert Avail.Storage Storage Description #1 499.50' 41.530 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.540 0.000 0.000 502.00 2.100 3.300 3.300 504.00 3.600 5.700 9.000 506.00 4.990 8.590 17.590 508.00 5.990 10.980 28.570 510.00 6.970 12.960 41.530 Device Routing Invert Outlet Devices #1 Primary 499.50'12.0" Round Culvert L= 116.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 497.00' S= 0.0216 '/' Cc= 0.900 n= 0.025, Flow Area= 0.79 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=1.30 cfs @ 17.09 hrs HW=502.12' (Free Discharge) 1=Culvert (Passes 1.30 cfs of 3.31 cfs potential flow) 2=Orifice/Grate (Weir Controls 1.30 cfs @ 1.14 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 25-Year Rainfall=5.70"ST 1 Printed 10/19/2015Prepared by AMEC Page 16HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 49P: Sediment Basin 1 Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 80 70 60 50 40 30 20 10 0 Inflow Area=11.140 ac Peak Elev=502.12' Storage=3.559 af 72.94 cfs 1.30 cfs1.30 cfs0.00 cfs Type II 24-hr 100-Year Rainfall=8.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 17HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=504.06' Storage=12.886 af Inflow=323.07 cfs 20.282 afPond 6P: Sediment Basin (SB-2) Primary=28.52 cfs 14.779 af Secondary=0.00 cfs 0.000 af Outflow=28.52 cfs 14.779 af Peak Elev=502.58' Storage=4.647 af Inflow=110.59 cfs 6.224 afPond 49P: Sediment Basin 1 Primary=3.49 cfs 2.260 af Secondary=0.00 cfs 0.000 af Outflow=3.49 cfs 2.260 af Type II 24-hr 100-Year Rainfall=8.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 18HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 6P: Sediment Basin (SB-2) Inflow Area = 39.459 ac, 0.00% Impervious, Inflow Depth > 6.17" for 100-Year event Inflow = 323.07 cfs @ 11.98 hrs, Volume= 20.282 af Outflow = 28.52 cfs @ 12.70 hrs, Volume= 14.779 af, Atten= 91%, Lag= 43.7 min Primary = 28.52 cfs @ 12.70 hrs, Volume= 14.779 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 504.06' @ 12.70 hrs Surf.Area= 5.481 ac Storage= 12.886 af Plug-Flow detention time= 227.8 min calculated for 14.772 af (73% of inflow) Center-of-Mass det. time= 164.7 min ( 916.2 - 751.5 ) Volume Invert Avail.Storage Storage Description #1 499.50' 63.755 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.620 0.000 0.000 502.00 2.840 4.325 4.325 504.00 5.420 8.260 12.585 506.00 7.640 13.060 25.645 508.00 9.500 17.140 42.785 510.00 11.470 20.970 63.755 Device Routing Invert Outlet Devices #1 Primary 499.50'24.0" Round Culvert L= 103.0' CMP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 498.00' S= 0.0146 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 3.14 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=28.52 cfs @ 12.70 hrs HW=504.06' (Free Discharge) 1=Culvert (Inlet Controls 28.52 cfs @ 9.08 fps) 2=Orifice/Grate (Passes 28.52 cfs of 48.79 cfs potential flow) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 100-Year Rainfall=8.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 19HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 6P: Sediment Basin (SB-2) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 350 300 250 200 150 100 50 0 Inflow Area=39.459 ac Peak Elev=504.06' Storage=12.886 af 323.07 cfs 28.52 cfs28.52 cfs 0.00 cfs Type II 24-hr 100-Year Rainfall=8.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 20HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 49P: Sediment Basin 1 Inflow Area = 11.140 ac, 0.00% Impervious, Inflow Depth > 6.70" for 100-Year event Inflow = 110.59 cfs @ 11.97 hrs, Volume= 6.224 af Outflow = 3.49 cfs @ 14.12 hrs, Volume= 2.260 af, Atten= 97%, Lag= 128.8 min Primary = 3.49 cfs @ 14.12 hrs, Volume= 2.260 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs Peak Elev= 502.58' @ 14.12 hrs Surf.Area= 2.536 ac Storage= 4.647 af Plug-Flow detention time= 335.4 min calculated for 2.259 af (36% of inflow) Center-of-Mass det. time= 221.6 min ( 961.6 - 740.1 ) Volume Invert Avail.Storage Storage Description #1 499.50' 41.530 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.540 0.000 0.000 502.00 2.100 3.300 3.300 504.00 3.600 5.700 9.000 506.00 4.990 8.590 17.590 508.00 5.990 10.980 28.570 510.00 6.970 12.960 41.530 Device Routing Invert Outlet Devices #1 Primary 499.50'12.0" Round Culvert L= 116.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 497.00' S= 0.0216 '/' Cc= 0.900 n= 0.025, Flow Area= 0.79 sf #2 Device 1 502.00'36.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=3.49 cfs @ 14.12 hrs HW=502.58' (Free Discharge) 1=Culvert (Barrel Controls 3.49 cfs @ 4.44 fps) 2=Orifice/Grate (Passes 3.49 cfs of 13.65 cfs potential flow) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 100-Year Rainfall=8.20"ST 1 Printed 10/19/2015Prepared by AMEC Page 21HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 49P: Sediment Basin 1 Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 120 110 100 90 80 70 60 50 40 30 20 10 0 Inflow Area=11.140 ac Peak Elev=502.58' Storage=4.647 af 110.59 cfs 3.49 cfs3.49 cfs0.00 cfs 8P Sediment Basin (SB-3) 37P Sediment Basin (SB-4) Routing Diagram for ST 2 Prepared by AMEC, Printed 10/19/2015 HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Subcat Reach Pond Link Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 2HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points x 3 Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=502.72' Storage=7.175 af Inflow=103.10 cfs 11.974 afPond 8P: Sediment Basin (SB-3) Primary=21.79 cfs 6.427 af Secondary=0.00 cfs 0.000 af Outflow=21.79 cfs 6.427 af Peak Elev=502.03' Storage=2.466 af Inflow=39.32 cfs 2.568 afPond 37P: Sediment Basin (SB-4) Primary=0.72 cfs 0.102 af Secondary=0.00 cfs 0.000 af Outflow=0.72 cfs 0.102 af Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 3HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 8P: Sediment Basin (SB-3) Inflow Area = 98.610 ac, 0.00% Impervious, Inflow Depth > 1.46" for 2-Year event Inflow = 103.10 cfs @ 11.99 hrs, Volume= 11.974 af Outflow = 21.79 cfs @ 13.14 hrs, Volume= 6.427 af, Atten= 79%, Lag= 69.2 min Primary = 21.79 cfs @ 13.14 hrs, Volume= 6.427 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 502.72' @ 13.14 hrs Surf.Area= 3.796 ac Storage= 7.175 af Plug-Flow detention time= 196.6 min calculated for 6.424 af (54% of inflow) Center-of-Mass det. time= 115.7 min ( 918.0 - 802.3 ) Volume Invert Avail.Storage Storage Description #1 499.50' 61.472 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.870 0.000 0.000 502.00 2.940 4.762 4.762 504.00 5.330 8.270 13.032 506.00 7.160 12.490 25.522 508.00 8.940 16.100 41.622 510.00 10.910 19.850 61.472 Device Routing Invert Outlet Devices #1 Primary 499.50'30.0" Round Culvert L= 91.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 496.00' S= 0.0385 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 4.91 sf #2 Device 1 502.00'42.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=21.79 cfs @ 13.14 hrs HW=502.72' (Free Discharge) 1=Culvert (Passes 21.79 cfs of 33.14 cfs potential flow) 2=Orifice/Grate (Weir Controls 21.79 cfs @ 2.77 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 4HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 8P: Sediment Basin (SB-3) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 110 100 90 80 70 60 50 40 30 20 10 0 Inflow Area=98.610 ac Peak Elev=502.72' Storage=7.175 af 103.10 cfs 21.79 cfs21.79 cfs 0.00 cfs Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 5HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 37P: Sediment Basin (SB-4) Inflow Area = 16.815 ac, 0.00% Impervious, Inflow Depth > 1.83" for 2-Year event Inflow = 39.32 cfs @ 11.99 hrs, Volume= 2.568 af Outflow = 0.72 cfs @ 19.56 hrs, Volume= 0.102 af, Atten= 98%, Lag= 454.2 min Primary = 0.72 cfs @ 19.56 hrs, Volume= 0.102 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 502.03' @ 19.56 hrs Surf.Area= 1.584 ac Storage= 2.466 af Plug-Flow detention time= 621.4 min calculated for 0.102 af (4% of inflow) Center-of-Mass det. time= 367.0 min ( 1,145.9 - 778.9 ) Volume Invert Avail.Storage Storage Description #1 499.50' 37.962 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.370 0.000 0.000 502.00 1.560 2.413 2.413 504.00 2.950 4.510 6.923 506.00 4.390 7.340 14.262 508.00 6.010 10.400 24.662 510.00 7.290 13.300 37.962 Device Routing Invert Outlet Devices #1 Primary 498.00'36.0" Round Culvert L= 150.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 498.00' / 495.00' S= 0.0200 '/' Cc= 0.900 n= 0.012 Concrete pipe, finished, Flow Area= 7.07 sf #2 Device 1 502.00'104.0" x 104.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=0.72 cfs @ 19.56 hrs HW=502.03' (Free Discharge) 1=Culvert (Passes 0.72 cfs of 54.18 cfs potential flow) 2=Orifice/Grate (Weir Controls 0.72 cfs @ 0.61 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 2-Year Rainfall=3.40"ST 2 Printed 10/19/2015Prepared by AMEC Page 6HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 37P: Sediment Basin (SB-4) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 40 35 30 25 20 15 10 5 0 Inflow Area=16.815 ac Peak Elev=502.03' Storage=2.466 af 39.32 cfs 0.72 cfs0.72 cfs0.00 cfs Type II 24-hr 10-Year Rainfall=5.10"ST 2 Printed 10/19/2015Prepared by AMEC Page 7HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points x 3 Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=503.79' Storage=11.927 af Inflow=182.08 cfs 22.836 afPond 8P: Sediment Basin (SB-3) Primary=41.19 cfs 16.919 af Secondary=0.00 cfs 0.000 af Outflow=41.19 cfs 16.919 af Peak Elev=502.22' Storage=2.766 af Inflow=69.27 cfs 4.543 afPond 37P: Sediment Basin (SB-4) Primary=11.39 cfs 2.055 af Secondary=0.00 cfs 0.000 af Outflow=11.39 cfs 2.055 af Type II 24-hr 10-Year Rainfall=5.10"ST 2 Printed 10/19/2015Prepared by AMEC Page 8HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 8P: Sediment Basin (SB-3) Inflow Area = 98.610 ac, 0.00% Impervious, Inflow Depth > 2.78" for 10-Year event Inflow = 182.08 cfs @ 11.98 hrs, Volume= 22.836 af Outflow = 41.19 cfs @ 13.98 hrs, Volume= 16.919 af, Atten= 77%, Lag= 120.1 min Primary = 41.19 cfs @ 13.98 hrs, Volume= 16.919 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 503.79' @ 13.98 hrs Surf.Area= 5.076 ac Storage= 11.927 af Plug-Flow detention time= 164.7 min calculated for 16.919 af (74% of inflow) Center-of-Mass det. time= 106.3 min ( 906.2 - 799.9 ) Volume Invert Avail.Storage Storage Description #1 499.50' 61.472 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.870 0.000 0.000 502.00 2.940 4.762 4.762 504.00 5.330 8.270 13.032 506.00 7.160 12.490 25.522 508.00 8.940 16.100 41.622 510.00 10.910 19.850 61.472 Device Routing Invert Outlet Devices #1 Primary 499.50'30.0" Round Culvert L= 91.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 496.00' S= 0.0385 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 4.91 sf #2 Device 1 502.00'42.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=41.19 cfs @ 13.98 hrs HW=503.79' (Free Discharge) 1=Culvert (Inlet Controls 41.19 cfs @ 8.39 fps) 2=Orifice/Grate (Passes 41.19 cfs of 61.94 cfs potential flow) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 10-Year Rainfall=5.10"ST 2 Printed 10/19/2015Prepared by AMEC Page 9HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 8P: Sediment Basin (SB-3) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=98.610 ac Peak Elev=503.79' Storage=11.927 af 182.08 cfs 41.19 cfs41.19 cfs 0.00 cfs Type II 24-hr 10-Year Rainfall=5.10"ST 2 Printed 10/19/2015Prepared by AMEC Page 10HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 37P: Sediment Basin (SB-4) Inflow Area = 16.815 ac, 0.00% Impervious, Inflow Depth > 3.24" for 10-Year event Inflow = 69.27 cfs @ 11.99 hrs, Volume= 4.543 af Outflow = 11.39 cfs @ 12.55 hrs, Volume= 2.055 af, Atten= 84%, Lag= 33.9 min Primary = 11.39 cfs @ 12.55 hrs, Volume= 2.055 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 502.22' @ 12.55 hrs Surf.Area= 1.710 ac Storage= 2.766 af Plug-Flow detention time= 200.8 min calculated for 2.055 af (45% of inflow) Center-of-Mass det. time= 111.9 min ( 879.0 - 767.1 ) Volume Invert Avail.Storage Storage Description #1 499.50' 37.962 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.370 0.000 0.000 502.00 1.560 2.413 2.413 504.00 2.950 4.510 6.923 506.00 4.390 7.340 14.262 508.00 6.010 10.400 24.662 510.00 7.290 13.300 37.962 Device Routing Invert Outlet Devices #1 Primary 498.00'36.0" Round Culvert L= 150.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 498.00' / 495.00' S= 0.0200 '/' Cc= 0.900 n= 0.012 Concrete pipe, finished, Flow Area= 7.07 sf #2 Device 1 502.00'104.0" x 104.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=11.39 cfs @ 12.55 hrs HW=502.22' (Free Discharge) 1=Culvert (Passes 11.39 cfs of 56.09 cfs potential flow) 2=Orifice/Grate (Weir Controls 11.39 cfs @ 1.52 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 10-Year Rainfall=5.10"ST 2 Printed 10/19/2015Prepared by AMEC Page 11HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 37P: Sediment Basin (SB-4) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 70 60 50 40 30 20 10 0 Inflow Area=16.815 ac Peak Elev=502.22' Storage=2.766 af 69.27 cfs 11.39 cfs11.39 cfs 0.00 cfs Type II 24-hr 25-Year Rainfall=6.22"ST 2 Printed 10/19/2015Prepared by AMEC Page 12HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points x 3 Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=504.48' Storage=15.691 af Inflow=220.19 cfs 30.504 afPond 8P: Sediment Basin (SB-3) Primary=45.64 cfs 24.118 af Secondary=0.00 cfs 0.000 af Outflow=45.64 cfs 24.118 af Peak Elev=502.40' Storage=3.095 af Inflow=89.78 cfs 5.905 afPond 37P: Sediment Basin (SB-4) Primary=28.82 cfs 3.405 af Secondary=0.00 cfs 0.000 af Outflow=28.82 cfs 3.405 af Type II 24-hr 25-Year Rainfall=6.22"ST 2 Printed 10/19/2015Prepared by AMEC Page 13HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 8P: Sediment Basin (SB-3) Inflow Area = 98.610 ac, 0.00% Impervious, Inflow Depth > 3.71" for 25-Year event Inflow = 220.19 cfs @ 11.97 hrs, Volume= 30.504 af Outflow = 45.64 cfs @ 14.68 hrs, Volume= 24.118 af, Atten= 79%, Lag= 162.3 min Primary = 45.64 cfs @ 14.68 hrs, Volume= 24.118 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 504.48' @ 14.68 hrs Surf.Area= 5.768 ac Storage= 15.691 af Plug-Flow detention time= 181.1 min calculated for 24.106 af (79% of inflow) Center-of-Mass det. time= 130.6 min ( 932.5 - 801.9 ) Volume Invert Avail.Storage Storage Description #1 499.50' 61.472 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.870 0.000 0.000 502.00 2.940 4.762 4.762 504.00 5.330 8.270 13.032 506.00 7.160 12.490 25.522 508.00 8.940 16.100 41.622 510.00 10.910 19.850 61.472 Device Routing Invert Outlet Devices #1 Primary 499.50'30.0" Round Culvert L= 91.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 496.00' S= 0.0385 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 4.91 sf #2 Device 1 502.00'42.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=45.64 cfs @ 14.68 hrs HW=504.48' (Free Discharge) 1=Culvert (Inlet Controls 45.64 cfs @ 9.30 fps) 2=Orifice/Grate (Passes 45.64 cfs of 72.94 cfs potential flow) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 25-Year Rainfall=6.22"ST 2 Printed 10/19/2015Prepared by AMEC Page 14HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 8P: Sediment Basin (SB-3) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 240 220 200 180 160 140 120 100 80 60 40 20 0 Inflow Area=98.610 ac Peak Elev=504.48' Storage=15.691 af 220.19 cfs 45.64 cfs45.64 cfs 0.00 cfs Type II 24-hr 25-Year Rainfall=6.22"ST 2 Printed 10/19/2015Prepared by AMEC Page 15HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 37P: Sediment Basin (SB-4) Inflow Area = 16.815 ac, 0.00% Impervious, Inflow Depth > 4.21" for 25-Year event Inflow = 89.78 cfs @ 11.99 hrs, Volume= 5.905 af Outflow = 28.82 cfs @ 12.29 hrs, Volume= 3.405 af, Atten= 68%, Lag= 18.2 min Primary = 28.82 cfs @ 12.29 hrs, Volume= 3.405 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 502.40' @ 12.29 hrs Surf.Area= 1.839 ac Storage= 3.095 af Plug-Flow detention time= 160.9 min calculated for 3.404 af (58% of inflow) Center-of-Mass det. time= 83.1 min ( 844.7 - 761.6 ) Volume Invert Avail.Storage Storage Description #1 499.50' 37.962 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.370 0.000 0.000 502.00 1.560 2.413 2.413 504.00 2.950 4.510 6.923 506.00 4.390 7.340 14.262 508.00 6.010 10.400 24.662 510.00 7.290 13.300 37.962 Device Routing Invert Outlet Devices #1 Primary 498.00'36.0" Round Culvert L= 150.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 498.00' / 495.00' S= 0.0200 '/' Cc= 0.900 n= 0.012 Concrete pipe, finished, Flow Area= 7.07 sf #2 Device 1 502.00'104.0" x 104.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=28.82 cfs @ 12.29 hrs HW=502.40' (Free Discharge) 1=Culvert (Passes 28.82 cfs of 57.97 cfs potential flow) 2=Orifice/Grate (Weir Controls 28.82 cfs @ 2.07 fps) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 25-Year Rainfall=6.22"ST 2 Printed 10/19/2015Prepared by AMEC Page 16HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 37P: Sediment Basin (SB-4) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 100 90 80 70 60 50 40 30 20 10 0 Inflow Area=16.815 ac Peak Elev=502.40' Storage=3.095 af 89.78 cfs 28.82 cfs28.82 cfs 0.00 cfs Type II 24-hr 100-Year Rainfall=8.20"ST 2 Printed 10/19/2015Prepared by AMEC Page 17HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Time span=0.00-20.00 hrs, dt=0.01 hrs, 2001 points x 3 Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Peak Elev=505.63' Storage=22.942 af Inflow=283.94 cfs 44.603 afPond 8P: Sediment Basin (SB-3) Primary=52.22 cfs 32.389 af Secondary=0.00 cfs 0.000 af Outflow=52.22 cfs 32.389 af Peak Elev=502.73' Storage=3.734 af Inflow=126.84 cfs 8.377 afPond 37P: Sediment Basin (SB-4) Primary=61.16 cfs 5.859 af Secondary=0.00 cfs 0.000 af Outflow=61.16 cfs 5.859 af Type II 24-hr 100-Year Rainfall=8.20"ST 2 Printed 10/19/2015Prepared by AMEC Page 18HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 8P: Sediment Basin (SB-3) Inflow Area = 98.610 ac, 0.00% Impervious, Inflow Depth > 5.43" for 100-Year event Inflow = 283.94 cfs @ 11.97 hrs, Volume= 44.603 af Outflow = 52.22 cfs @ 15.93 hrs, Volume= 32.389 af, Atten= 82%, Lag= 237.4 min Primary = 52.22 cfs @ 15.93 hrs, Volume= 32.389 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Starting Elev= 497.00' Surf.Area= 0.000 ac Storage= 0.000 af Peak Elev= 505.63' @ 15.93 hrs Surf.Area= 6.822 ac Storage= 22.942 af Plug-Flow detention time= 208.8 min calculated for 32.389 af (73% of inflow) Center-of-Mass det. time= 145.0 min ( 953.5 - 808.5 ) Volume Invert Avail.Storage Storage Description #1 499.50' 61.472 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.870 0.000 0.000 502.00 2.940 4.762 4.762 504.00 5.330 8.270 13.032 506.00 7.160 12.490 25.522 508.00 8.940 16.100 41.622 510.00 10.910 19.850 61.472 Device Routing Invert Outlet Devices #1 Primary 499.50'30.0" Round Culvert L= 91.0' CPP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 499.50' / 496.00' S= 0.0385 '/' Cc= 0.900 n= 0.013 Corrugated PE, smooth interior, Flow Area= 4.91 sf #2 Device 1 502.00'42.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=52.22 cfs @ 15.93 hrs HW=505.63' (Free Discharge) 1=Culvert (Inlet Controls 52.22 cfs @ 10.64 fps) 2=Orifice/Grate (Passes 52.22 cfs of 88.27 cfs potential flow) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 100-Year Rainfall=8.20"ST 2 Printed 10/19/2015Prepared by AMEC Page 19HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 8P: Sediment Basin (SB-3) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 300 250 200 150 100 50 0 Inflow Area=98.610 ac Peak Elev=505.63' Storage=22.942 af 283.94 cfs 52.22 cfs52.22 cfs 0.00 cfs Type II 24-hr 100-Year Rainfall=8.20"ST 2 Printed 10/19/2015Prepared by AMEC Page 20HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Summary for Pond 37P: Sediment Basin (SB-4) Inflow Area = 16.815 ac, 0.00% Impervious, Inflow Depth > 5.98" for 100-Year event Inflow = 126.84 cfs @ 11.99 hrs, Volume= 8.377 af Outflow = 61.16 cfs @ 12.17 hrs, Volume= 5.859 af, Atten= 52%, Lag= 10.9 min Primary = 61.16 cfs @ 12.17 hrs, Volume= 5.859 af Secondary = 0.00 cfs @ 0.00 hrs, Volume= 0.000 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-20.00 hrs, dt= 0.01 hrs / 3 Peak Elev= 502.73' @ 12.17 hrs Surf.Area= 2.066 ac Storage= 3.734 af Plug-Flow detention time= 132.7 min calculated for 5.859 af (70% of inflow) Center-of-Mass det. time= 65.6 min ( 819.7 - 754.2 ) Volume Invert Avail.Storage Storage Description #1 499.50' 37.962 af Custom Stage Data (Prismatic) Listed below (Recalc) Elevation Surf.Area Inc.Store Cum.Store (feet) (acres) (acre-feet) (acre-feet) 499.50 0.370 0.000 0.000 502.00 1.560 2.413 2.413 504.00 2.950 4.510 6.923 506.00 4.390 7.340 14.262 508.00 6.010 10.400 24.662 510.00 7.290 13.300 37.962 Device Routing Invert Outlet Devices #1 Primary 498.00'36.0" Round Culvert L= 150.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 498.00' / 495.00' S= 0.0200 '/' Cc= 0.900 n= 0.012 Concrete pipe, finished, Flow Area= 7.07 sf #2 Device 1 502.00'104.0" x 104.0" Horiz. Orifice/Grate C= 0.600 Limited to weir flow at low heads #3 Secondary 508.00'Custom Weir/Orifice, Cv= 2.62 (C= 3.28) Head (feet) 0.00 2.00 Width (feet) 10.00 50.00 Primary OutFlow Max=61.16 cfs @ 12.17 hrs HW=502.73' (Free Discharge) 1=Culvert (Inlet Controls 61.16 cfs @ 8.65 fps) 2=Orifice/Grate (Passes 61.16 cfs of 70.50 cfs potential flow) Secondary OutFlow Max=0.00 cfs @ 0.00 hrs HW=499.50' (Free Discharge) 3=Custom Weir/Orifice ( Controls 0.00 cfs) Type II 24-hr 100-Year Rainfall=8.20"ST 2 Printed 10/19/2015Prepared by AMEC Page 21HydroCAD® 10.00 s/n 08086 © 2013 HydroCAD Software Solutions LLC Pond 37P: Sediment Basin (SB-4) Inflow Outflow Primary Secondary Hydrograph Time (hours) 20191817161514131211109876543210 Fl o w ( c f s ) 140 120 100 80 60 40 20 0 Inflow Area=16.815 ac Peak Elev=502.73' Storage=3.734 af 126.84 cfs 61.16 cfs61.16 cfs 0.00 cfs REFERENCE 4 J.W. Faircloth & Son, Inc. “Determining the Skimmer Size and the Required Orifice for the Faircloth Skimmer Surface Drain” Revised November 2007. November 6, 2007 1 Determining the Skimmer Size and the Required Orifice for the Faircloth Skimmer® Surface Drain November 2007 Important note: The orifice sizing chart in the Pennsylvania Erosion Control Manual and reproduced in the North Carolina Design Manual DOES NOT APPLY to our skimmers. It will give the wrong size orifice and not specify which size skimmer is required. Please use the information below to choose the size skimmer required for the basin volume provided and determine the orifice size required for the drawdown time, typically 4-7 days in Pennsylvania and 3 days in North Carolina. The size of a Faircloth Skimmer®, for example a 4” skimmer, refers to the maximum diameter of the skimmer inlet. The inlet on each of the 8 sizes offered can be reduced to adjust the flow rate by cutting a hole or orifice in a plug using an adjustable cutter (both supplied). Determining the skimmer size needed and the orifice for that skimmer required to drain the sediment basin’s volume in the required time involves two steps: First, determining the size skimmer required based on the volume to be drained and the number of days to drain it; and Second, calculate the orifice size to adjust the flow rate and “customize” the skimmer for the basin’s volume. The second step is not always necessary if the flow rate for the skimmer with the inlet wide open equals or is close to the flow rate required for the basin volume and the drawdown time. Both the skimmer size and the required orifice radius for the skimmer should be shown for each basin on the erosion and sediment control plan. Make it clear that the dimension is either the radius or the diameter. It is also helpful to give the basin volume in case there are questions. During the skimmer installation the required orifice can be cut in the plastic plug using the supplied adjustable cutter and installed in the skimmer using the instructions provided. The plan review and enforcement authority may require the calculations showing that the skimmer used can drain the basin in the required time. Determining the Skimmer Size Step 1. Below are approximate skimmer maximum flow capacities based on typical draw down requirements, which can vary between States and jurisdictions and watersheds. If one 6” skimmer does not provide enough capacity, multiple skimmers can be used to drain the basin. For drawdown times not shown, multiply the 24-hour figure by the number of days required. Example: A basin’s volume is 29,600 cubic feet and it must be drained in 3 days. A 3” skimmer with the inlet wide open will work perfectly. (Actually, the chart below gives 29,322 cubic feet but this is well within the accuracy of the calculations and the basin’s constructed volume.) Example: A basin’s volume is 39,000 cubic feet and it must be drained in 3 days. The 3” skimmer is too small; a 4” skimmer has enough capacity but it is too large, so the inlet will need to be reduced using step 2 to adjust the flow rate for the basin’s volume. (It needs a 3.2” diameter orifice.) 1½” skimmer: 1,728 cubic feet in 24 hours 6,912 cubic feet in 4 days with a 1½” head 3,456 cubic feet in 2 days 12,096 cubic feet in 7 days 5,184 cubic feet in 3 days 2” skimmer: 3,283 cubic feet in 24 hours 13,132 cubic feet in 4 days with a 2” head 6,566 cubic feet in 2 days 22,982 cubic feet in 7 days 9,849 cubic feet in 3 days 2½” skimmer: 6,234 cubic feet in 24 hours 24,936 cubic feet in 4 days with a 2.5” head 12,468 cubic feet in 2 days 43,638 cubic feet in 7 days Revised 11-6-07 18,702 cubic feet in 3 days 3” skimmer: 9,774 cubic feet in 24 hours 39,096 cubic feet in 4 days with a 3” head 19,547 cubic feet in 2 days 68,415 cubic feet in 7 days 29,322 cubic feet in 3 days 4” skimmer: 20,109 cubic feet in 24 hours 80,436 cubic feet in 4 days with a 4” head 40,218 cubic feet in 2 days 140,763 cubic feet in 7 days Revised 11-6-07 60,327 cubic feet in 3 days 5” skimmer: 32,832 cubic feet in 24 hours 131,328 cubic feet in 4 days with a 4” head 65,664 cubic feet in 2 days 229,824 cubic feet in 7 days 98,496 cubic feet in 3 days 6” skimmer: 51,840 cubic feet in 24 hours 207,360 cubic feet in 4 days with a 5” head 103,680 cubic feet in 2 days 362,880 cubic feet in 7 days 155,520 cubic feet in 3 days 8” skimmer: 97,978 cubic feet in 24 hours 391,912 cubic feet in 4 days with a 6” head 195,956 cubic feet in 2 days 685,846 cubic feet in 7 days CUSTOM 293,934 cubic feet in 3 days MADE BY ORDER CALL! Determining the Orifice Step 2. To determine the orifice required to reduce the flow rate for the basin’s volume and the number of days to drain the basin, simply use the formula volume ÷ factor (from the chart below) for the same size skimmer chosen in the first step and the same number of days. This calculation will give the area of the required orifice. Then calculate the orifice radius using Area = π r2 and solving for r, )14.3/(Arear=.The supplied cutter can be adjusted to this radius to cut the orifice in the plug. The instructions with the plug and cutter has a ruler divided into tenths of inches. Again, this step is not always necessary as explained above. An alternative method is to use the orifice equation with the head for a particular skimmer shown on the previous page and determine the orifice needed to give the required flow for the volume and draw down time. C = 0.59 is used in this chart. Example: A 4” skimmer is the smallest skimmer that will drain 39,000 cubic feet in 3 days but a 4” inlet will drain the basin too fast (in 1.9 days) To determine the orifice required use the factor of 4,803 from the chart below for a 4” skimmer and a drawdown time of 3 days. 39,000 cubic November 6, 2007 2 feet ÷ 4,803 = 8.12 square inches of orifice required. Calculate the orifice radius using Area = π r2 and solving for r, )14.3/12.8(=r and r = 1.61”. As a practical matter 1.6” is about as close as the cutter can be adjusted and the orifice cut.. Factors (in cubic feet of flow per square inch of opening through a round orifice with the head for that skimmer and for the drawdown times shown) for determining the orifice radius for a basin’s volume to be drained. This quick method works because the orifice is centered and has a constant head (given above in Step 1). 1½” skimmer: 960 to drain in 24 hours 3,840 to drain in 4 days 1,920 to drain in 2 days 6,720 to drain in 7 days 2,880 to drain in 3 days 2” skimmer: 1,123 to drain in 24 hours 4,492 to drain in 4 days 2,246 to drain in 2 days 7,861 to drain in 7 days 3,369 to drain in 3 days 2½” skimmer: 1,270 to drain in 24 hours 5,080 to drain in 4 days Revised 11-6-07 2,540 to drain in 2 days 8,890 to drain in 7 days 3,810 to drain in 3 days 3” skimmer: 1,382 to drain in 24 hours 5,528 to drain in 4 days 2,765 to drain in 2 days 9,677 to drain in 7 days 4,146 to drain in 3 days 4” skimmer: 1,601 to drain in 24 hours 6,404 to drain in 4 days Revised 11-6-07 3,202 to drain in 2 days 11,207 to drain in 7 days 4,803 to drain in 3 days 5” skimmer: 1,642 to drain in 24 hours 6,568 to drain in 4 days 3,283 to drain in 2 days 11,491 to drain in 7 days 4,926 to drain in 3 days 6” skimmer: 1,814 to drain in 24 hours 7,256 to drain in 4 days 3,628 to drain in 2 days 12,701 to drain in 7 days 5,442 to drain in 3 days 8” skimmer: 1,987 to drain in 24 hours 7,948 to drain in 4 days 3,974 to drain in 2 days 13,909 to drain in 7 days 5,961 to drain in 3 days J. W. Faircloth & Son, Inc. Post Office Box 757 412-A Buttonwood Drive Hillsborough, North Carolina 27278 Telephone (919) 732-1244 FAX (919) 732-1266 FairclothSkimmer.com jwfaircloth@embarqmail.com Orifice sizing Revised 2-2-01; 3-3-05; 2-1-07; 11-6-07 November 6, 2007 3 REFERENCE 5 Bonnin, G.M. et. al., “NOAA Atlas 14, Volume 2, Version 3, Point Precipitation Frequency Estimates”, NOAA National Weather Service, obtained September 15, 2014. Precipitation Frequency Data Server Page 1 of 3 NOAA Atlas 14, Volume 2, Version 3 Location name: Eden, North Carolina, US" Latitude: 36.4999°, Longitude:-79.7013° Elevation: 582 ft* * source: Google Maps "*�,�,,.t 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 I PF graphical I Maps & aerials PF tabular PDS-based point precipitation frequency estimates with 90% confidence intervals (in inches)' Average recurrence interval (years) Duration ��� 10 25 50 100 200 500 1000 0.363 0.433 0.512 0.567 0.633 0.676 0.717 0.754 0.796 0.826 5-min (0.331-0.397) (0.396-0.473) (0.467-0.560) (0.518-0.619) (0.575-0.688) (0.612-0.735) (0.646-0.781) (0.676-0.822) (0.708-0.869) (0.729-0.902) 0.579 0.692 0.820 0.908 1.01 1.08 1.14 1.20 1.26 1.30 10-min (0 .529-0.634) (0.633-0.757) (0.749-0.898) (0.829-0.991) (0.917-1.10) (0.974-1.17) 1 (1.03-1.24) 1 (1.07-1.30) 1 (1.12-1.38) 0.724 0.870 1.04 1.15 1.28 1.36 1.44 1.51 1.59 1.63 15-min (0.661-0.792) (0.796-0.951) (0.947-1.14) 1 (1.05-1.25) 1 (1.16-1.39) 1 (1.23-1.48) 1 (1.30-1.57) 1 (1.35-1.64) 1 (1.41-1.73) 1 (1.44-1.78) 0.993 1.20 1.47 1.66 1.89 2.05 2.21 2.35 2.52 2.64 30-min (0.906-1.09) 1 (1.10-1.31) 1 (1.35-1.61) 1 (1.52-1.82) 1 (1.72-2.06) (1.86-2.23) (1.99-2.40) (2.11-2.56) (2.24-2.75) (2.33-2.89) 1.24 1.51 1.89 2.17 2.52 2.78 3.04 3.29 3.62 3.86 60-min (1.13-1.35) (1.38-1.65) (1.73-2.07) (1.98-2.36) (2.29-2.74) (2.52-3.03) (2.74-3.31) (2.95-3.59) (3.22-3.95) (3.41-4.22) 1.47 1.79 2.25 2.61 3.08 3.45 3.83 4.20 4.71 5.10 2-hr (1.35-1.61) (1.63-1.96) (2.06-2.46) (2.38-2.85) (2.80-3.36) (3.12-3.75) (3.44-4.16) (3.75-4.57) (4.15-5.12) (4.45-5.56) 1.59 1.93 2.44 2.82 3.33 3.73 4.13 4.54 5.08 5.50 3-hr (1.46-1.73) (1.78-2.11) (2.24-2.66) (2.58-3.07) (3.03-3.62) (3.38-4.04) (3.72-4.48) (4.06-4.92) ( 4.49-5.52) ( 4.81-5.98) 1.96 2.37 2.99 3.48 4.15 4.70 5.28 5.87 6.71 7.38 6-hr (1.80-2.15) (2.18-2.61) (2.74-3.27) (3.17-3.80) (3.76-4.53) (4.22-5.12) (4.70-5.73) (5.18-6.37) (5.82-7.29) (6.31-8.02) 2.36 2.87 3.63 4.26 5.15 5.89 6.70 7.56 8.81 9.84 12-hr (2.17-2.59) (2.63-3.14) (3.32-3.96) (3.88-4.62) (4.65-5.57) (5.28-6.37) (5.94-7.21) (6.62-8.12) (7.57-9.48) (8.31-10.6 ) 2.81 3.40 4.33 5.10 6.22 7.17 8.20 9.32 11.0 12.4 24-hr (2.61-3.04) (3.16-3.68) (4.02-4.67) (4.72-5.48) (5.72-6.68) (6.55-7.69) (7.44-8.79) (8.39-10.0) (9.74-11.8) (10.9-13.3) 3.30 3.99 5.04 5.90 7.12 8.13 9.21 10.4 12.0 13.4 2-day (3.08-3.55) (3.72-4.30) (4.70-5.42) (5.48-6.33) (6.59-7.63) (7.48-8.71) (8.42-9.88) (9.40-11.1 ) ( 10.8-13.0 ) ( 11.9-14.5 ) 3.49 4.22 5.33 6.23 7.52 8.59 9.72 10.9 12.7 14.2 3-day (3.26-3.76) (3.93-4.55) (4.96-5.73) (5.79-6.69) (6.95-8.07) (7.89-9.21) (8.88-10.4) (9.92-11.8) (11.4-13.7) ( 12.6-15.3) 3.68 4.45 5.61 6.56 7.92 9.04 10.2 11.5 13.4 14.9 4-day (3.43-3.97) (4.15-4.80) (5.23-6.05) (6.10-7.06) (7.32-8.51) (8.31-9.71) (9.35-11.0) (10.4-12.4) (12.0-14.4) (13.2-16.1) 4.22 5.07 6.29 7.29 8.71 9.88 11.1 12.4 14.3 15.9 7-day (3.96-4.51) (4.75-5.42) (5.89-6.72) (6.81-7.78) (8.11-9.28) (9.14-10.5) (10.2-11.9) ( 11.4-13.3) ( 12.9-15.3) ( 14.2-17.0) 4.77 5.71 7.01 8.0 6 10.7 12.0 13.3 15.1 16.6 10-day ��69.53 (4.48-5.10 ) (5.37-6.10) (6.58-7.48 ) (7.55-8.60) (8.89-10.2 ) (9.96-11.4) (11.1-12.8) (12.2-14.2) (13.8-16.2) (15.0-17.8) 6.43 7.65 9.20 10.4 12.1 13.4 14.7 16.1 17.9 19.3 20-day (6.05-6.85) (7.21-8.16) (8.66-9.81) (9.79-11.1) (11.3-12.9) (12.5-14.3) (13.7-15.7) (14.9-172) (16.4-19.2) (17.6-20.8) 30-day 7.95 9.40 11.1 12.3 14.0 15.3 16.5 17.7 19.3 20.5 (7.53-8.41) (8.91-9.94) (10.5-11.7) (11.7-13.0) (13.2-14.8) (14.4-16.2) (15.5-17.5) (16.6-18.8) (18.0-20.5) (19.0-21.9) 45-day 10.0 11.8 13.7 15.2 17.1 18.5 19.8 21.1 22.8 24.0 (9.48-10.6) (11.2-12.5) (13.0-14.5) (14.4-16.0) (16.1-18.0) (17.4-19.5) (18.6-21.0) (19.8-22.4) (21.3-24.2) (22.3-25.6) 12.0 14.0 16.1 17.7 19.7 21.2 22.6 23.9 25.6 26.8 60-day ( 114-12.6) 1 (13.4-14.8) 1 U-15-3-1-7.0) I (16.8-18.6) 1 U-18-7-2-o.7) 1 (20.0-22.3) 1 U-21-3-2-3.8) 1 (22.5-25.2) J (24.0-27.1) 11 (25.1-28.4) 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. Back to Top PF graphical http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 Precipitation Frequency Data Server Page 2 of 3 25 ....:....:.....:.....:.....:... ... .. ..... c 20 __ -. ...... --.- ... ._._. .. r. 0 15 .2 i-I 10 IL 5 0 e c_ L ry s w Ce _c c` LL M IppC N T�'1 41S r��d N ra1 yy�--�� 7 ppE 0 .i O 6 rS7Vf 30 �64.d Diratidn 30 25 L 20 5 0 1 2 5 10 25 50 100 200 500 1000 ack tR To Average recurrence interval Maps & aerials NOAA Atlas 14, Volume 2, Version 3 created tGMTI: Mon Sep 15 14:27:08 2014 Small scale terrain Washrr 'i1101"" Grvrrs•✓ l Charlottesville's Nafirt t f Fvresir% °� i ~`cIFyn hhurgU! V i r.g i n i a. Ric _61a kslwr �` Peter e 9i "Roanoke gip ortt — — - 0dnvill F-Johnson Ctierokee Navonal rvresf' >_ td 7 bonne tree sboro . �iFis❑ah<. ,.. 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E 7W 1953 � Sti t962 17dT Td76 S 4h� ,vr � 7pp Aen 1779 _ 87� H 2 km Map OpNoUilreboangie Back to Too US Department of Commerce National Oceanic and Atmospheric Administration National Weather Service Office of Hvdroloaic Develooment 1325 East West Highway Silver Spring, MD 20910 Questions?: HDSC.Questions(a)noaa.aov Disclaimer http://hdsc.nws.noaa.gov/hdse/pfds/pfds printpage.html?lat=3 6.4999&lon=-79.7013 &data... 9/15/2014 Energy Dissipater and Stone Gabion Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 1 of 4 12/9/2016 (Initial submittal) Calculation Title: Energy Dissipater and Stone Gabion Calculation Summary: The energy dissipaters and stone gabion mattresses were designed for stability and capacity for a Type II 100-year, 24-hour design storm event of 8.20 inches while maintaining channel lining stability. Notes: Revision Log: No. Description Originator Verifier Technical Reviewer 0 Initial submittal – 12/9/2016 Chris Jordan Stephanie Stanwick Cedric H. Ruhl Energy Dissipater and Stone Gabion Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 2 of 4 12/9/2016 (Initial submittal) OBJECTIVE: The objective of this calculation is to design riprap energy dissipaters and stone gabions that will be constructed during decommissioning of the Primary and Secondary Ash Basin dams at Duke Energy’s Dan River Steam Station. METHOD: The riprap energy dissipaters and stone gabions were designed for a 100-year storm event in accordance with the North Carolina Department of Environment and Natural Resources (NCDENR) “Erosion and Sediment Control Planning and Design Manual”. DEFINITION OF VARIABLES: A = drainage area; AC = cross-section area of flow through channel; b = bottom width of flow through channel; d = depth of flow through channel; D0 = bottom width or diameter; d50 = minimum riprap size; dmax = maximum riprap size; CN = curve number; D = channel depth; i = rainfall depth; La = minimum apron length; W = downstream apron width; n = Manning’s roughness co-efficient for flow through channel; P = wetted perimeter of flow through channel; Q = discharge flow; R = hydraulic radius of flow through channel; S = longitudinal slope of the channel flow; T = top width of flow through channel; V = velocity of flow through channel; and Z = channel side slope. CALCULATIONS: 1.0 Design riprap energy dissipaters Riprap energy dissipaters will be located at the outlet of slope drains and culverts that convey stormwater flow from upstream tributary areas to the footprint of the decommissioned impoundment. The 48-inch diameter culvert, 54-inch diameter culvert, and 36-inch diameter slope drain all discharge directly to a longitudinal ditch with riprap lining and are designed in the “Final Conditions Stormwater Calculation”. Peak flows to each dissipater were calculated for a 100-year, 24 hour design storm event. Riprap energy dissipaters for minimum tailwater conditions were calculated as follows: Energy Dissipater and Stone Gabion Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 3 of 4 12/9/2016 (Initial submittal) 𝑃𝑚𝑟𝑟𝑟𝑍𝑍𝑚 𝐴𝑚𝑟𝑚𝑚 𝑃�ℎ𝑍𝑟�=3𝐷0 𝑃=𝐷0 +𝐿𝑎 Riprap energy dissipaters for maximum tailwater conditions were calculated as follows: 𝑃𝑚𝑟𝑟𝑟𝑍𝑍𝑚 𝐴𝑚𝑟𝑚𝑚 𝑃�ℎ𝑍𝑟�=3𝐷0 𝑃=𝐷0 +0.4𝐿𝑎 Apron Thickness is calculated as follows: 𝐴𝑚𝑟𝑚𝑚 𝑃𝑖ℎ𝑍𝑘𝑚𝑍𝑟𝑟=1.5𝑍𝑚𝑎𝑥 The riprap energy dissipaters will have the dimensions shown in the following table: Outlet ID Dissipater ID Tailwater Condition Discharge (cfs) Diameter {D0} (in) Minimum Riprap Size {d50} (in) [Ref. 1] Selected Riprap Class [Ref. 2] Maximum Riprap Size {dmax} (in) [Ref. 2] Apron Thickness (in) Minimum Apron Length {La} (ft) [Ref. 1] Upstream Apron Width (ft) [Ref. 1] Downstream Apron Width {W} (ft) [Ref. 1] SD-4 RD-1 minimum 12.2 18 7.2 B 10.8 16.2 16 4.5 17.5 SD-5 RD-2 minimum 16.6 36 7.2 B 10.8 16.2 20 9 12 SD-6 RD-2 minimum 9.6 18 4.8 B 7.2 10.8 12 4.5 13.5 SD-7 RD-3 minimum 4.2 18 4.8 B 7.2 10.8 12 4.5 13.5 Table 1: Riprap Energy Dissipater Dimensions 2.0 Design gabion outlet protection Four gabions will be constructed to convey stormwater flow from the footprint of the decommissioned impoundment to the Dan River. The gabion mattresses were analyzed for capacity as a rectangular channel using Manning’s equation and the discharge from the “Outlet Channel Calculation” package as the peak runoff. 2.1 Gabion Capacity The gabion mattress capacity was assumed to be a rectangular channel with dimensions as presented in the following table: Gabion ID Bottom Width {b} (ft) MIN. Depth {D} (ft) Left Side Slope {Z1H:V} Right Side Slope {Z2H:V} Top Width {T} (ft) Upstream Invert (ft) Downstream Invert (ft) Length {L} (ft) Longitudinal Slope {S} (ft/ft) G-1 15 1.5 0 0 15 497.0 480 38 0.447 G-2 21 2 0 0 21 496.0 480 33 0.485 G-3 21 1.5 0 0 21 497.0 480 27 0.630 G-4 15 2 0 0 15 495.0 480 15 1.000 Table 2: Gabion Mattress Dimensions The capacity of each gabion was evaluated using Manning’s equation [Ref. 1] as presented in the following equation: Energy Dissipater and Stone Gabion Calculation Dam Decommissioning Plan Duke Energy – Dan River Steam Station Amec Foster Wheeler Project No. 7810-14-0065 4 of 4 12/9/2016 (Initial submittal) 𝑃=1.49 𝑚𝑃2/3 𝑃1/2 Where n is Manning’s coefficient, R is hydraulic radius and S is the longitudinal slope of the stormwater flow. The total discharge was given by: 𝑃=𝐴𝐶𝑃 The flow cross-section area “AC” and wetted perimeter “P” were calculated based on the geometry of a trapezoidal channel with a flow depth “d”, bottom width “b”, left side slope “Z1”, and right side slope “Z2”, using the following relationships: 𝐴𝐶=𝑍𝑍+0.5𝑍1 𝑍2 +0.5𝑍2 𝑍2 𝑃=𝑍+√[(𝑍1 𝑍)2 +𝑍2 ]+√[(𝑍2 𝑍)2 +𝑍2 ] Each gabion was assumed to have rip-rap lining and was evaluated in flow capacity for the 100- year, 24-hour design storm event. The trial flow depth and Manning’s n were iteratively modified until the channel capacity exceeded the predicted peak runoff for the conditions modeled. Gabion capacity estimated for the channel grade is shown in the following table: Gabion ID Channel Lining Manning's n {n} Trial Flow Depth {d} (ft) Flow Area {A} (ft2) Wetted Perimeter {P} (ft) Hydraulic Radius {R} (ft) Velocity {V} (ft/s) Channel Capacity {Q} (cfs) Peak Runoff {Q} (cfs) Channel Capacity > Peak Runoff? Freeboard (in) G-1 rip rap 0.03 0.26 3.9 15.5 0.3 13.2 51.45 49.75 yes 14.9 G-2 rip rap 0.03 0.58 12.2 22.2 0.5 23.1 281.88 280.99 yes 17.0 G-3 rip rap 0.03 0.43 9.0 21.9 0.4 21.8 196.86 190.27 yes 12.8 G-4 rip rap 0.03 0.28 4.2 15.6 0.3 20.7 86.89 81.99 yes 20.6 Table 3: Gabion Mattress - 100 years Long-Term Conditions The hydraulic analyses indicate that the gabion outlets have capacity to pass the 100-year, 24- hour design storm. DISCUSSION: The energy dissipaters and stone gabion mattresses for the Dan River dam decommissioning were designed for stability and capacity for a Type II 100-year, 24-hour design storm event of 8.20 inches while maintaining channel lining stability. REFERENCES: 1. North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. 2. North Carolina Department of Transportation. Standard Specification for Roads and Structures. Raleigh, 2012. REFERENCE 1 North Carolina Department of Environment and Natural Resources, “Erosion and Sediment Control Planning and Design Manual”, Revised May 2013. Appendices 8.05.5 8 8.05.6 Rev. 12/93 Design Procedure- Permissible Velocity The following is a step-by-step procedure for designing a runoff conveyance channel using Manning’s equation and the continuity equation: Step 1. Determine the required flow capacity, Q, by estimating peak runoff rate for the design storm (Appendix 8.03). Step 2. Determine the slope and select channel geometry and lining. Step 3. Determine the permissible velocity for the lining selected, or the desired velocity, if paved. (see Table 8.05a, page 8.05.4) Step 4. Make an initial estimate of channel size—divide the required Q by the permissible velocity to reach a “first try” estimate of channel flow area. Then select a geometry, depth, and top width to fit site conditions. Step 5. Calculate the hydraulic radius, R, from channel geometry (Figure 8.05b, page 8.05.5). Step 6. Determine roughness coefficient n. Structural Linings—see Table 8.05b, page 8.05.6. Grass Lining: a. Determine retardance class for vegetation from Table 8.05c, page 8.05.8. To meet stability requirement, use retardance for newly mowed condition (generally C or D). To determine channel capacity, use at least one retardance class higher. b. Determine n from Figure 8.05c, page 8.05.7. Step 7. Calculate the actual channel velocity, V, using Manning’s equation (Figure 8.05a, pg. 8.05.3), and calculate channel capacity, Q, using the continuity equation. Step 8. Check results against permissible velocity and required design capacity to determine if design is acceptable. Step 9. If design is not acceptable, alter channel dimensions as appropriate. For trapezoidal channels, this adjustment is usually made by changing the bottom width. Table 8.05b Manning’s n for Structural Channel Linings Channel Lining Recommended n values Asphaltic concrete, machine placed Asphalt, exposed prefabricated Concrete Metal, corrugated Plastic Shotcrete Gabion Earth 0.014 0.015 0.015 0.024 0.013 0.017 0.030 0.020 Source: American Society of Civil Engineers (modified) Appendices Rev. 12/93 8.06.3 8 8.06.4 Rev. 12/93 REFERENCE 2 North Carolina Department of Transportation. Standard Specification for Roads and Structures. Raleigh, 2012. Section 1043 10-62 All stone shall meet the approval of the Engineer. While no specific gradation is required, 1 there shall be equal distribution of the various sizes of the stone within the required size 2 range. The size of an individual stone particle will be determined by measuring its long 3 dimension. 4 Stone or broken concrete for rip rap shall meet Table 1042-1 for the class and size 5 distribution. 6 TABLE 1042-1 ACCEPTANCE CRITERIA FOR RIP RAP AND STONE FOR EROSION CONTROL Required Stone Sizes, inches Class Minimum Midrange Maximum A 2 4 6 B 5 8 12 1 5 10 17 2 9 14 23 No more than 5.0% of the material furnished can be less than the minimum size specified nor 7 no more than 10.0% of the material can exceed the maximum size specified. 8 SECTION 1043 9 AGGREGATE FROM CRUSHED CONCRETE 10 1043-1 GENERAL 11 Aggregate from crushed concrete is a recycled product made by crushing concrete obtained 12 from concrete truck clean out, demolition of existing concrete structures or pavement, or 13 similar sources and transported from a crushing facility. It does not include concrete 14 pavements that are rubblelized, broken or otherwise crushed in place on the roadway. 15 The crushed material must meet all sources approval requirements described in Sections 1005 16 and 1006 with the exception of the sodium sulfate test requirement. Deleterious materials 17 shall not be more than 3%. 18 Sampling and acceptance for the determination of gradaction, LL and PI will be performed as 19 described in the Aggregate QC/QA Program Manual and the Aggregate Sampling Manual. 20 1043-2 AGGREGATE BASE COURSE 21 The material shall meet the ABC gradation. The LL of the material shall be raised 5 points to 22 no more than 35. 23 1043-3 AGGREGATE SHOULDER BORROW 24 The material shall meet Section 1019. 25 1043-4 CLEAN COARSE AGGREGATE FOR ASPHALT 26 The material shall meet the gradation of a standard size in Table 1005-1. Use of the material 27 shall be approved by the Engineer, and the mix shall meet all requirements. 28 1043-5 CLEAN COARSE AGGREGATE FOR CONCRETE 29 The material shall meet the gradation of a standard size in Table 1005-1. Use of the material 30 is restricted to Class B concrete mixes only. Use of the material shall be approved by the 31 Engineer, and the concrete shall meet all requirements. 32 SECTION 1044 33 SUBSURFACE DRAINAGE MATERIALS 34 1044-1 SUBDRAIN FINE AGGREGATE 35 Subdrain fine aggregate shall meet No. 2S or 2MS in Table 1005-2. 36 NCDOT 2012 Standard Specifications err7[ for ter M ieeier AMEC Design Calculation or Analysis Cover Sheet Project Duke Energy Coal Combustion Residual Management Program CalciAnalysis No. AMEC Project No. Reconstitution Design of Ash Basins - Dan River Steam Station H-001 7810-14-0150 Title Primary (ROCK]-237-H) and Secondary (ROCKI-238-H) Ash Ponds - Hydrologic and Hydraulic (H&H) Analysis Computer Software and Version No. HydroCADTm Purpose and Objective Hydrologic and Hydraulic (H&H) Analysis to assess if the combined spillway capacity is sufficient to pass the inflow design flood (IDF) in a safe and non -erosive manner while maintaining required freeboard and without overtopping the embankment. The IDF hydrograph shall be calculated as the flow resulting from the design flood storm event falling on the watershed upstream of the impoundment and the impoundment itself and process flows. Summary of Conclusion Based on the results of this study and assumptions made, AMEC concludes that bath the Primary and Secondary Ash Ponds have sufficient hydraulic capacity to safety store/pass the 3/4 PMP design storm in a safe and non -erosive manner. Both the Primary and Secondary Ash Ponds pass the design storm without overtopping the embankment in accordance with the design criteria presented in the North Carolina Administrative Code and Duke's Programmatic Document. The Primary Ash Pond will have 0.66 feet of freeboard and the Secondary Ash Pond will have 5.56 feet of freeboard based on the hydraulic capacity analyses. The majority of the Primary Ash Pond dike is at elevation 540 and the maximum water surface is more than 8 feet below this elevation which means that the water surface is shielded from wind -generated wave setup and run-up by the surrounding dike. The Secondary Ash Pond is shielded from direct wind action by adjacent landforms (the ash stack and the Primary Ash Pond) and the maximum water surface is over 6 feet below the lowest point on the dike, therefore wind -generated wave run-up and setup is not applicable. The existing spillways for the Primary and Secondary Ash Ponds will discharge 80% of the inflow from the design storm within 15 days of the peak. Revision Log Rev. Revision Description: No. 0 Initial Issue C err �! +�rF l�jrf�t 4���R�11�15 Rev. Originator (Print) ` �' '., .�+' Independent Technical Reviewer (Print) No. Richard L Hiner w Joshua M. Bell, ?F,,CFM Sign I Date -1$5 = r Sign f Date,;29 rrrrr�us++ TABLE OF CONTENTS Section Page 1. EXECUTIVE SUMMARY ...................................................................................................................... 3 2. SCOPE OF INVESTIGATION ................................................................................................................ 4 3. ASSUMPTIONS .................................................................................................................................. 5 4. COMPUTER PROGRAM IDENTIFICATION .......................................................................................... 5 5. DESCRIPTION OF FACILITIES AND POTENTIALLY IMPACTED AREA ................................................... 6 6. CALCULATION APPROACH AND INPUT ........................................................................................... 10 7. SUMMARY OF METHODS AND APPROACH ..................................................................................... 14 8. CONCLUSIONS AND DISCUSSIONS .................................................................................................. 16 9. REFERENCES .................................................................................................................................... 18 10. ABBREVIATIONS .............................................................................................................................. 19 Tables Table 1 – Administrative Information - Primary (ROCKI-237-H) Ash Basin & Dam Table 2 – Administrative Information - Secondary (ROCKI-238-H) Ash Basin & Dam Table 3 – Stage-Storage Data for Dry Fly Ash Basin Table 4 – Stage-Storage Data for Primary (ROCKI-237-H) Ash Basin Table 5 – Stage-Storage Data for Secondary (ROCKI-238-H) Ash Basin Table 9 – HydroCAD™ Model Inputs for Dry Fly Ash Basin Table 10 –HydroCAD™ Model Inputs for Primary (ROCKI-237-H) Ash Basin Table 11 –HydroCAD™ Model Inputs for Secondary (ROCKI-238-H) Ash Basin Table 12 –HydroCAD™ Output Summary for the Dry Fly Ash, Primary (ROCKI-237-H) Ash, and Secondary (ROCKI-238-H) Ash Basins Figures Figures 1a & 1b – Scaled Topographic Map of the Contributing Watersheds Figure 2 – Basin Contours - Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basins Figures 3a & 3b – Soil Map - Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basins Appendix 15A NCAC 2K .0205 – Spillway Design Time of Concentration Calculations SCS Type II 6-hour Rainfall Distribution Curve Number Calculations Stage-Storage Calculations Stage-Discharge Calculations Rainfall Reference for PMP (Figure 18 from HMR51) HydroCAD™ Output for ¾ PMP Analysis PREPARED BY DATE CHECKED BY DATE JOB NUMBER 7810-14-0150 Source: USDA-NRCS Digital Raster Graph Mosaic, dated 2007. ST770 ST87 £¤311 Rockingham County NN OO RR TT HH CC AA RR OO LL II NN AA VV II RR GG II NN II AA Eden Sources: Esri, HERE, DeLorme, Intermap, increment P Corp., GEBCO, USGS, FAO, NPS, NRCAN, GeoBase, IGN, Kadaster NL, Ordnance Survey, Esri Japan, METI, Esri China (Hong Kong), swisstopo, MapmyIndia, © OpenStreetMap contributors, and the GIS User Community DAN RIVER ASH PLANT - DUKE ENERGYEDEN, NORTH CAROLINA ± JMS 8/31/2016 RLH 8/31/2016 EXHIBIT 1PROJECT LOCATION ^_ NORTH CAROLINA Copyright:© 2013 National Geographic Society, i-cubed Project Location 0 10,000 20,0005,000 Feet ASH BASIN Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 3 of 20 RCN: BFHR-0084.0 1. EXECUTIVE SUMMARY The Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basins at the Duke Energy Dan River Steam Station are considered to be large high-hazard structures (based on the existing NCDENR hazard-rating criteria). The Primary (ROCKI-237-H) Ash Basin Dam was originally constructed in 1951 and was modified in 1968. It is a 40-foot high earthen dam and the reservoir has a normal surface area of approximately 7.40 acres (at elevation 532) and a maximum hydraulic storage capacity of approximately 37 acre-feet (at elevation 532). The Secondary (ROCKI-238-H) Ash Basin Dam was constructed in 1976. It is a 30-foot high earthen dam and the reservoir has a normal surface area of approximately 4.83 acres (at elevation 515) and a maximum hydraulic storage capacity of approximately 130.16 acre-feet (at elevation 528.52). The purpose of this report is to demonstrate compliance with Section 15A of the North Carolina Administrative Code, Subchapter 2K, section .0205 (15A NCAC 2K .0205) with regards to spillway capacity (Part .0205 is excerpted in the Appendix). This report summarizes the methodology and results of the ¾ PMP spillway analysis completed for the Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basin Dams. Data for the hydrologic and hydraulic analyses were obtained from a combination of publicly available information, information provided by Duke Energy, and field data collection. Design documentation indicates that the constructed top-widths of both the Primary (ROCKI-237- H) and Secondary (ROCKI-238-H) Ash Basin Dams are 15 feet. The original design crest elevations were approximately 540 feet (Primary – ROCKI-237-H) and 530 feet (Secondary – ROCKI-238-H). According to recent survey data, in the lowest point on the current crest of the Secondary Ash Pond Dam is at elevation 528.52 and the dike breech area for the Primary Ash Pond Dike is at elevation 532 (the remainder of the Primary Ash Pond Dam is at approximately elevation 540). The design side slopes are 2 foot horizontal to 1 foot vertical (2H:1V) on the interior and 2H:1V on the exterior for both structures. The maximum height of the Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basin Dams are 40 feet and 30 feet, respectively, measured from the crest to the downstream toe. The hydrologic design criterion for both structures is three-quarters of the Probable Maximum Precipitation (¾ PMP) for the spillway design flood. The hydrologic analysis of the ¾ PMP storm was completed using HydroCAD™ 10.0, Build 18. Basin areas, land use classifications, soil hydrologic groups, flow lines, and topographical information were obtained for the Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basin dam watersheds. The Full PMP event for the 6-hour duration at this location was interpolated as 29.2 inches according to Hydro-Meteorological Report No. 51 (HMR-51) issued by the National Weather Service in June, 1978. A 6-hour, ¾ PMP storm of 21.9 inches (29.2*0.75) was used in this analysis. Based on the project location and using Figure B-2 from Appendix B of the TR-55 manual, an SCS Type II rainfall distribution was used for this analysis. This rainfall distribution concentrates the bulk of the rainfall in the ½ hour surrounding the center of the storm duration (between 2:45 and 3:15). This distribution was developed by the Natural Resource Conservation Service (NRCS, formerly SCS) in 1986 and is a synthetic distribution based on observed precipitation events. Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 4 of 20 The following analysis demonstrates that the existing spillway system meets the requirements of 15A NCAC 2K .0205. The Primary (ROCKI-237-H) Ash Basin Dam is not overtopped during the ¾ PMP storm event. No emergency spillway is required for the Primary (ROCKI-237-H) Ash Basin Dam. Therefore, the frequency of use requirements in 15A NCAC .0205 (b) are not applicable to this facility. The analysis also demonstrates that the Secondary (ROCKI-238-H) Ash Basin Dam is not overtopped during the ¾ PMP storm event. Both the Primary (ROCKI-237-H) Ash Basin and the Dry Fly Ash Basin discharge directly into the Secondary (ROCKI-238-H) Ash Basin and the existing principal spillway meets the requirements of 15A NCAC 02K .0205. The dam is not overtopped in the ¾ PMP design storm event and no emergency spillway is required for the Secondary (ROCKI-238-H) Ash Basin Dam. Therefore, the frequency of use requirements in 15A NCAC .0205 (b) are not applicable to this facility. 2. SCOPE OF INVESTIGATION AMEC performed the analysis of the Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basins to determine whether the existing spillway systems can safely pass the ¾ PMP event in compliance with 15A NCAC 2K .0205. Topographic information showing the current configuration of the interior of the ash basins was available from Duke Energy. The remaining contour data for the ash basin watersheds was developed for this analysis using a combination of LiDAR (Light Detection And Ranging) data and data from WSP Sells. The analysis of the Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basins for the ¾ PMP event was performed using HydroCAD™ and included the Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basins, the associated spillway/outfall structures, and the Dry Fly Ash Basin. No analysis of downstream structures or inundation was performed was performed for the Dan River as part of this analysis. The rainfall depth for the design event was obtained by determining the PMP event from the HMR 51 and multiplying it by 0.75. Lesser storms (500-yr, 100-yr, etc.) were not analyzed as part of this task. The contributing drainage areas for the Primary (ROCKI-237-H) and Secondary (ROCKI-238-H) Ash Basins were determined using a combination of topographic information developed for Duke, recent bathymetric data for the Secondary Ash Basin, recent topo of the stack area within the Primary Ash Basin, and LiDAR data as necessary to fill in any missing areas. A detailed survey was not performed for the remainder of the contributing watershed as part of this contract. The stage-storage information for the basins was determined from the topographic data provided by Duke Energy as part of this contract. The stage-discharge relationship was calculated dynamically within the HydroCAD program based on the structure data from the original design drawings. The following deliverables were prepared and are included in this report: Scaled topographic map of the contributing watershed; Time-of-concentration calculations; Curve number calculations; Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 5 of 20 Rainfall reference information for PMP (HMR 51); and Stage-storage and stage-discharge calculations. 3. ASSUMPTIONS For the analysis of the secondary ash pond, a number of assumptions have been established and are listed below. The normal pool level of the secondary pond has been lowered to elevation 514 to improve the stability of the dam structure and to provide additional storage during the design event. The stage-storage information for the Secondary Ash Pond is based on previously provided aerial topographic data and new bathymetric survey information obtained as part of the plan to lower the operating water level (OWL) in the Secondary Pond. The discharge structure input data for the Secondary Ash Pond is based on original design drawings for the spillway as well as previously provided survey information and the stage-discharge relationship is computed dynamically within the HydroCAD program. For the analysis of the primary ash pond, a number of additional assumptions have been established and are listed below. The normal pool level of the primary pond can be lowered to provide additional storage during the design event. The elevation of the containment dike at the breach can be raised to contain the peak stage during the ¾ PMP event. The stage-storage information for the primary ash pond is based on topographic survey information obtained for and used in the previously approved report (3/4 PMP Spillway Capacity Analysis for Primary (ROCKI-237-H) Ash Pond Dam and Secondary (ROCKI- 238-H) Ash Pond Dam) in addition to topographic information obtained following the failure of the pipe under the primary ash pond. The discharge structure input data for the Primary Ash Pond is based on original design drawings for the spillway as well as previously provided survey information and the stage- discharge relationship is computed dynamically within the HydroCAD program. 4. COMPUTER PROGRAM IDENTIFICATION The table below indicates the computer hardware, operating system, and software used by AMEC for the data analysis and/or calculations presented herein. User (Computer Name) Computer Hardware (Service Tag No.) Operating System Computer Software Richard Hiner Dell Latitude M4800 (LG750870) Microsoft Windows 7 Professional Microsoft Office Word 2007, HydroCAD™ 10.0, Build 18 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 6 of 20 5. DESCRIPTION OF FACILITIES AND POTENTIALLY IMPACTED AREA 1.1 General Information – Primary Ash Pond Dam The Primary (ROCKI-237-H) Ash Pond at the Dan River Station is not currently used for ash discharge. Information describing the characteristics of the impoundment, maximum dam sections and spillway facilities are provided in Table 1. Table 1 - Administrative Information - Primary (ROCKI-237-H) Ash Basin & Dam Basic Dam Information Name Primary (ROCKI-237-H) Ash Basin Dam National ID Number NC05945 State Dam ID Number ROCKI–237 Current Hazard Classification Large, High Hazard Status Impounding Type Earthen Purpose Ash sluicing operations Year Constructed 1968 Baseflow ( cfs ) 0.00 Owner's contact information Owner's name and address DAN RIVER STEAM STATION ROCKINGHAM COUNTY 900 SOUTH EDGEWOOD DRIVE EDEN, NC, 27288 336-623-0415 Engineer's name and address AMEC E&I, Inc. 2801 Yorkmont Road Charlotte, NC 28208 704.357.8600 Geographic coordinates, location and specific dam features Latitude, Longitude (NAD83 decimal degrees) N36.48830, W79.71480 County/NCDENR Region Rockingham/WSRO USGS Quadrangle Name Southeast Eden Name of Impounded Stream Unnamed tributary of Dan River Name of Receiving Stream Dan River River Basin Roanoke Nearest City Eden Distance to Nearest City ( miles ) 2.8 Specific information about the dam, including its construction and drainage area. Structural Height3 ( feet ) 40 Normal Freeboard4 ( feet ) 12 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 7 of 20 Hydraulic Height5 ( feet ) 28 Crest Length ( nearest foot ) 1,944 Crest Width ( nearest foot ) 15 Upstream Slope, XH:1V 2H:1V Downstream Slope, XH:1V 2H:1V Normal Pool Elevation 528.0 Pond Surface Area (acres ) 7.40 (area of ash) Normal Pool Capacity (acre·feet ) 0.00 (no impoundment) Hydraulic Capacity (acre-feet) 36.48 Bottom Drain Yes Bottom Drain Operable Unknown Drainage Area ( acres )2 27.4 Principal (ROCKI-237-H) Spillway Details1 Type Riser/Barrel Size Outlet: 36 inch diameter RCP Material CIP Concrete Total Weir Length ( feet ) 8 (2-4 foot weirs) Weir details Removable 4’ Concrete Stop Logs Total Drop ( feet ) 9 Invert Elevations, Weir/Outlet Barrel 528.0 ( current/min ) /526.2 Emergency Spillway Type None Emergency Spillway Details Not Applicable Notes: 1. Based on data provided by Duke Energy Corporation, Feb. 2011 2. Based on map–based drainage area calculations by AMEC, Apr. 2011 3. Estimated vertical distance from lowest point on crest to point at which breech would fail at toe. 4. Difference between structural height and hydraulic height. 5. Distance from normal pool to lowest point on downstream toe. Elevations in feet, NAVD 1988 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 8 of 20 1.2 General Information – Secondary Ash Pond Dam The Secondary (ROCKI-238-H) Ash Pond at the Dan River Station is currently used for final clarification of the ash discharge. Information describing the characteristics of the impoundment, maximum dam sections and spillway facilities are provided in Table 2. Table 2 - Administrative Information - Secondary (ROCKI-238-H) Ash Basin & Dam Basic Dam Information Name Secondary (ROCKI-238-H) Ash Basin Dam National ID Number NC05946 State Dam ID Number ROCKI–238 Current Hazard Classification Large, High Hazard Status Impounding Type Earth Purpose Ash sluicing operations Year Constructed 1976 Baseflow ( cfs ) 0.00 Owner's contact information Owner's name and address DAN RIVER STEAM STATION ROCKINGHAM COUNTY 900 SOUTH EDGEWOOD DRIVE EDEN, NC, 27288 336-623-0415 Engineer's name and address AMEC E&I, Inc. 2801 Yorkmont Road Charlotte, NC 28208 704.357.8600 Geographic coordinates, location and specific dam features Latitude, Longitude (NAD83 decimal degrees) N36.49190, W79.71140 County/NCDENR Region Rockingham/WSRO USGS Quadrangle Name Southeast Eden Name of Impounded Stream Unnamed tributary of Dan River Name of Receiving Stream Dan River River Basin Roanoke Nearest City Eden Distance to Nearest City ( miles ) 2.8 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 9 of 20 Specific information about the dam, including its construction and drainage area. Structural Height3 ( feet ) 30 Normal Freeboard4 ( feet ) 16 Hydraulic Height5 ( feet ) 14.0 Crest Length ( nearest foot ) 1364 Crest Width ( nearest foot ) 15 Upstream Slope, XH:1V 2H:1V Downstream Slope, XH:1V 2H:1V Normal Pool Elevation 515.0 Pond Surface Area ( acres ) 7.07 Normal Pool Capacity ( acre·feet ) 29.56 Hydraulic Capacity (acre-feet) 130.16 Bottom Drain Yes Bottom Drain Operable Yes Drainage Area ( acres )2 29.4 (119.616*) Principal (ROCKI-237-H) Spillway Details1 Type Riser/Barrel Size ( Outlet ) 33 inches (36” RCP with 1.5” lining) Material ( Riser ) CIP Concrete Total Weir Length ( feet ) 16 Weir details Removable 4’ Concrete Stop Logs Total Drop ( feet ) 16 Invert Elevations, Weir/Outlet Barrel 515 ( current ), 502.2 ( min )/498.0 Emergency Spillway Type None Emergency Spillway Details Not Applicable Notes: 1. Based on data provided by Duke Energy Corporation, Feb. 2011 2. Based on map–based drainage area calculations by AMEC, Apr. 2011 – *The area of 29.4 acres is the area which contributes by direct runoff. Since the Dry Fly Ash Basin and the Primary Ash Basin both discharge into the Secondary Ash Basin and are part of the watershed, the total area of the watershed 119.7 acres. 3. Estimated vertical distance from lowest point on crest to point at which breech would fail at toe. 4. Difference between structural height and hydraulic height. 5. Distance from normal pool to lowest point on downstream toe. Elevations in feet, NAVD 1988 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 10 of 20 6. CALCULATION APPROACH AND INPUT 6.1 Drainage Area Delineation The contributing watersheds for the Dry Fly Ash Basin, are based on a delineation prepared for this analysis using a combination of WSP-Sells contour data provided by Duke Energy and USGS data for areas not covered by the WSP-Sells data. This USGS data came from the 2001-2003 1/9-Arc Second National Elevation Dataset for the State of North Carolina and was published in 2008. The watershed drainage areas measured from this delineation are approximately 62.9 acres (0.0983 mi2) for the Dry Fly Ash Basin, 27.4 acres (0.0428 mi2) for the Primary (ROCKI- 237-H) Ash Basin and 29.4 acres (0.0459 mi2) for the Secondary (ROCKI-238-H) Ash Basin. The outflows from both the Dry Fly Ash Basin and the Primary (ROCKI-237-H) Ash Basin discharge directly into the Secondary (ROCKI-238-H) Ash Basin. Please refer to Figure 1 in this report for the drainage area delineation. 6.2 Time-of-Concentration/Lag-Time Calculations The time-of-concentration for the watershed was computed using the methodology in the NRCS (formerly SCS) publication Urban Hydrology for Small Watersheds (Technical Release 55). This methodology, like many others, requires the delineation of the longest flow path. This path is then broken down into three typical flow regimes; Sheet flow or overland flow, shallow concentrated flow, and channel/pipe flow. Once the flow path and flow regimes are identified, travel time for each segment is computed and then added together to determine the total time-of-concentration. Once this is determined, the lag-time is computed as 60% of the total time-of-concentration. While it has been common practice when modeling small ponds to assume a near instantaneous Tc of 0.01 hours, the large size of the pond renders this assumption inappropriately conservative. In addition to the overland flow, it is reasonable to assume that it will take some time for the inflow to propagate across the pond. For our analyses, the single wave solution of the Kortweg-de Vries equation (cp=SQRT(g(h+H), where g=32.2 ft/sec2, h is the average depth, and H is the wave height) was used to determine the wave propagation speed. Assuming an average water depth of 5 feet and a wave height of 0.5 feet, yields a computed wave propagation speed of approximately 13.3 ft/sec. This value will be used to determine the travel time across the pond for both ash basins. For the Dry Fly Ash Basin, the flow path is approximately 1670 feet in length and has an upper elevation of 628 feet and a lower elevation of 530 feet for an average slope of 5.87%. Since the shallow swales along the flow path are unpaved, the shallow concentrated flow calculations assume an unpaved condition. The time-of-concentration computed for this watershed is 9.0 minutes. Since the contributing watershed for the Primary (ROCKI-237-H) Ash Basin is limited to the basin itself, the 1,694 foot flow path consists of a short distance of sheet flow followed by the shallow Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 11 of 20 concentrated flow across the ash. The time-of-concentration computed for this watershed is 43.2 minutes. For the Secondary (ROCKI-238-H) Ash Basin, the flow path is approximately 2502 feet in length and has an upper elevation of 591 feet and a lower elevation of 530 feet for an average slope of 2.44%. Since the shallow swales along the flow path are unpaved, the shallow concentrated flow calculations assume an unpaved condition. The time-of-concentration computed for this watershed is 22.1 minutes. The full calculations for the time-of-concentration are included in the HydroCAD™ output. Please refer to Figures 1a and 1b in this report for a depiction of the flow path. 6.3 Rainfall Reference Information The Dan River Steam Station is located approximately 45 miles northeast of Winston-Salem, North Carolina and approximately 4 miles south of the Virginia state line. The rainfall depth information for this analysis was obtained from HMR-51 using the 6-hour, 10 mi2, All-Season PMP Isopluvial Map (Figure 18). Interpolation from this figure yields a full PMP event for the 6- hour duration of approximately 29.2 inches. Therefore, the 6-hour, ¾ PMP storm would be 21.9 inches and this value was used in the analysis and was distributed using a 6-hour duration SCS Type II distribution. Figure 18 from HMR-51 is included for reference in the appendix of this report. 6.4 Curve Number Information For the curve number computations, TR-55 methodology was used and several general assumptions were necessary to ensure consistency in the results. The first was the assumption that the normal pool area in each of the basins was impervious. The second was that the land use was considered as “open space with fair grass cover”. Curve numbers were then selected based on the distribution of soil types within the watershed. For Type B soils, a curve number of 69 was selected and for Type C soils, a curve number of 79 was selected. Impervious areas (ponded water) were modeled with a curve number of 98. The selected curve numbers are conservative given that much of the watersheds are used for ash stacking operations and coal ash deposits are highly pervious and would actually have an effective curve number much lowe r than the native soil in these areas. It is appropriate, however, for this type of analysis, to take a somewhat more conservative position since curve numbers for coal ash deposits have not been firmly established. The drainage area for the Dry Fly Ash Basin includes both the original dry fly ash stacking area and the former dredge pond. Both of these areas have been filled with coal ash deposits and no longer have any hydraulic storage capacity, but do drain to the remaining basin area between them. For the Dry Fly Ash Basin watershed, the weighted curve number was computed as 75 and the watershed was divided fairly evenly between Type B and Type C soils. The basin itself does not have a normal pool elevation as it is not intended to store water on a normal basis, so this watershed had no impervious percentage associated with it. Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 12 of 20 The drainage area for the Primary (ROCKI-237-H) Ash Basin consists of the ash basin itself and the basin has no permanent pool. The area of the basin is primarily Type C soil with a very small amount of Type B. A weighted curve number of 79 was computed for this basin. The contributing watershed for the Secondary (ROCKI-238-H) Ash Basin consists of about 49% Type B soils, 34% Type C soils, and 16% Ponded Water which results in a weighted curve number of 77. The normal pool area in the basin was modeled with a curve number of 98. Please refer to Figures 3a and 3b in this report as well as the calculations in the appendix for further information about the soil distribution in the watershed. 6.5 Stage-Storage Calculations LDSI performed an aerial survey of the Primary (ROCKI-237-H) Ash Basin in February 2014 and a bathymetric survey of the Secondary (ROCKI-238-H) Ash Basin for Duke Energy in September 2014. A CAD drawing of these surveys was provided by Duke Energy for this analysis. The contours in this drawing were used to create a triangulated irregular network (TIN – a vector based representation of the physical land surface) from which stage-storage data could be developed. Table 3: Stage-Storage Data for Dry Fly Ash Basin Elevation (ft) Surface Area (acres) Volume (acre-feet) 530 0 0 535 0.29 0.13 540 2.34 8.39 545 3.67 23.77 550 4.98 45.32 555 6.50 73.97 558.2 7.66 96.36 Table 4: Stage-Storage Data for Primary (ROCKI-237-H) Ash Basin Elevation (ft) Surface Area (acres) Volume (acre-feet) 528 7.40 0 529 8.22 7.81 530 9.13 16.48 531 9.82 25.96 532 11.22 36.48 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 13 of 20 Table 5: Stage-Storage Data for Secondary (ROCKI-238-H) Ash Basin Elevation (ft) Surface Area (acres) Volume (acre-feet) 515 7.07 0 516 7.47 7.27 517 7.87 14.94 518 8.14 22.95 519 8.34 31.19 520 8.52 39.62 521 8.68 48.22 522 8.85 56.99 523 9.15 65.99 524 9.81 75.46 525 11.60 86.17 526 12.24 98.09 527 12.50 110.45 528 13.04 123.22 528.52 13.38 130.09 529 13.69 136.58 6.6 Stage-Discharge Calculations The stage-discharge calculations are based on the physical characteristics of the principal spillway system. The spillway for the Dry Fly Ash basin consists of a riser tower with provisions for stop logs which is connected to a 24-inch diameter outfall pipe. Since this is not maintained as a wet basin, there are no stop logs in place and the spillway is free draining through the culvert. The spillway for the Primary (ROCKI-237-H) Ash Basin consists of a concrete riser tower with stop logs on two sides. The stop logs for the Primary principal spillway are placed at elevation 535 to maintain the normal pool. These stop logs can be removed down to the invert elevation of the outfall pipe if it is necessary to drain the pond. The spillway for the Secondary (ROCKI-238- H) Ash Basin consists of a concrete riser tower with stop logs on four sides. The stop logs for the Secondary principal spillway are placed at elevation 515 to maintain the normal pool. These stop logs can be removed down to the invert elevation of the outfall pipe if it is necessary to drain the pond. At very low flows (less than about 2 ft of head), the weir flow over the riser will control the discharge. Once the depth exceeds about 2 feet, orifice flow through the outfall pipe will control the discharge. HydroCAD™ computes the discharge dynamically at each elevation based on the physical characteristics of the riser structure and outfall pipe which are entered as input data. The stage-discharge characteristics can be viewed as part of the HydroCAD™ output data. Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 14 of 20 7. SUMMARY OF METHODS AND APPROACH 7.1 Hydrologic and Hydraulic Analysis Both the hydrologic and hydraulic analyses completed for this study were based on application of HydroCAD™ 10.0, build 18. HydroCAD™ is a general application, hydrologic and hydraulic model that can perform unsteady flow routing through storage areas and dams (an unsteady flow analysis deals with flow conditions that vary both temporally and spatially) in addition to performing hydraulic calculations for the outlet structures and discharge pipes. In accordance with 15A NCAC 2K .0205, the hydrologic analyses completed for this study were based on the guidelines presented in the National Weather Service (NWS) Hydro-Meteorological Report No. 51 (HMR-51, 1978). These guidelines were used to develop a Probable Maximum Precipitation (PMP) event for the project watershed. SCS methods were used for the rainfall-runoff analyses. The input parameters for the SCS hydrologic method for each basin were determined by analyses of the hydrologic soil group data provided by the NRCS. The full PMP event for the 6-hour duration at this location was interpolated as 29.2 inches according to HMR-51. Therefore, a 6-hour, ¾ PMP rainfall depth of 21.9 inches was used in this analysis and was distributed using a 6-hour duration SCS Type II distribution. The resulting hydrologic model simulates the runoff produced by the ¾ PMP event for the Primary (ROCKI- 237-H) and Secondary (ROCKI-238-H) Ash Pond watershed and the resulting discharge hydrographs were routed through the basin to determine the peak stage during the ¾ PMP event. The HEC-1 models developed for this analysis are included in the appendix and the basic input data is summarized in the following tables. Table 9. HydroCAD™ Model Inputs for the Dry Fly Ash Basin Input Value Basin Area (acres) 62.9 Time-of-Concentration(minutes) 9.0 SCS Curve Number 75 Unit Hydrograph SCS Rainfall Distribution SCS Type II Rainfall Duration 6 hours Precipitation (inches) for ¾ PMP 21.9 Computation time increment (minutes) 3 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 15 of 20 Table 10. HydroCAD™ Model Inputs for the Primary (ROCKI-237-H) Ash Basin Input Value Basin Area (acres) 27.39 Time-of-Concentration (minutes) 43.2 SCS Curve Number 79 Unit Hydrograph SCS Rainfall Distribution SCS Type II Rainfall Duration 6 hours Precipitation (inches) for ¾ PMP 21.9 Computation time increment (minutes) 3 Table 11. HydroCAD™ Model Inputs for the Secondary (ROCKI-238-H) Ash Basin Input Value Basin Area (acres) 29.42 Time-of-Concentration (minutes) 22.1 SCS Curve Number 77 Unit Hydrograph SCS Rainfall Distribution SCS Type II Rainfall Duration 6 hours Precipitation (inches) for ¾ PMP 21.9 Computation time increment (minutes) 3 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 16 of 20 8. CONCLUSIONS AND DISCUSSIONS 8.1 HydroCAD™ Modeling Results The results of the HydroCAD™ analysis are summarized in the following table (the full HydroCAD™ output is included in the appendix). Table 12. HydroCAD™ Output Summary for the Dry Fly Ash, Primary (ROCKI-237-H), and Secondary (ROCKI-238-H) Ash Basins Dry Fly Ash Basin Primary (ROCKI-237- H) Ash Basin Secondary (ROCKI-238-H) Ash Basin 6-hour, ¾ PMP (inches) 21.9 21.9 21.9 Total Loss 3.55 2.9 3.33 Total Excess 18.35 19.0 18.57 Peak Inflow to Basin (cfs) 2,363.41 469.95 891.47 Time of Peak Inflow (hours) 3.00 3.39 3.15 Total Storm Volume (ac-ft) 96.197 43.377 185.289 Peak Stage Elevation (ft) 553.28 531.34 522.96 Overtopping Elev. (ft) 558.2 532 528.52 Maximum Storage (ac-ft) 96.4 36.48 136.58 Remaining Freeboard 4.92 0.66 5.56 Peak Storage Volume (ac-ft) 64.142 29.582 65.634 Peak Discharge (cfs) 112.32 65.24 138.89 Time of Peak Outflow (hours) 4.24 4.63 9.63 Time to Drain Basin (hours) ~14 ~17 ~36 The results of the HEC-1 analysis for the Primary Ash Pond spillway indicate that with the operating water level at elevation 528 and the primary dike breach at elevation 532, sufficient storage capacity exists to safely pass the ¾ PMP storm event with approximately 0.66 feet of freeboard and in compliance with the requirements of 15A NCAC 2K .0205. The details from the HEC-1 model are captured in the following table: The results of the HEC-1 analysis of the Secondary Ash Pond spillway indicate that with an operating level of 514 in the Secondary Ash Pond, sufficient storage capacity exists to safely pass Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 17 of 20 the ¾ PMP storm event with approximately 5.56 feet of freeboard and in compliance with the requirements of 15A NCAC 2K .0205. 8.2 Adequacy of Existing Spillway System As demonstrated through the above analysis, the existing spillway systems meet the requirements of 15A NCAC 2K .0205. The Primary (ROCKI-237-H) Ash Basin Dam is not overtopped during the ¾ PMP storm event. No emergency spillway is required for the Primary (ROCKI-237-H) Ash Basin Dam. Therefore, the frequency of use requirements in 15A NCAC .0205 (b) are not applicable to this facility. The existing spillway system will also drain 80% of the stored water in less than 1 days. The Secondary (ROCKI-238-H) Ash Basin Dam is not overtopped during the ¾ PMP storm event and the existing spillway system meets the requirements of 15A NCAC 02K .0205. No emergency spillway is required for the Secondary (ROCKI-238-H) Ash Basin Dam. Therefore, the frequency of use requirements in 15A NCAC .0205 (b) are not applicable to this facility. The existing spillway system will also drain 80% of the stored water in less than 2 days. The majority of the Primary Ash Pond dike is at elevation 540 and the maximum water surface is 531.34 which means that the water surface is shielded from wind-generated wave setup and run- up by the surrounding dike. The majority of the Secondary Ash Pond dike is at elevation 530 and the maximum water surface is 522.96 which means that the water surface is shielded from wind- generated wave setup and run-up by the surrounding dike. Wind-generated wave run-up and setup should not be an issue at this site. Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 18 of 20 9. REFERENCES National Weather Service, June 1978. Hydrometeorological Report No. 51, Probable Maximum Precipitation Estimates, United States East of the 105th Meridian. USDA NRCS June 1986. Technical Release 55 - Urban Hydrology for Small Watersheds WSP-Sells AutoCAD drawing (x_topo-final.dwg) provided by Duke Energy on 03/22/2011 LDSI AutoCAD drawing (3074Bathymetric.dwg) provided by LDSI, Inc. on 10/23/2014 Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 19 of 20 10. ABBREVIATIONS AF acre-feet cfs cubic feet per second ft feet GIS geographic information system NCDENR North Carolina Department of Environment and Natural Resources NGVD National Geodetic Vertical Datum of 1929 NRCS Natural Resource Conservation Service (formerly SCS) PMP Probable Maximum Precipitation SCS Soil Conservation Service LIDAR LIght Detection And Ranging Design Calculation or Analysis Title: Dan River Primary and Secondary Ash Pond H&H Analyses AMEC Project No: Calculation No: Rev No: Page: 7810-14-0150 H - 001 0 20 of 20 APPENDIX D an R i v e r 62.9 AC 29.4 AC 27.4 AC PRIMARYASHPOND SECONDARYASHPOND DRY FLY ASHBASIN FLOWPATHL=1,669.6 FT FLOWPATHL=2,502.0 FT 630620610600 580 570 560 550 640 590 560 55 0 54 0 530 520 610600590 620610 600 61 0 600 560 550 53 05 2 0 540530 530 5 2 0 5 2 0 5 1 0 500 490 5 9 0 58 0 590 580 5 1 0 620 550 54 0 540 52 0 610 600 580 570 580 5 7 0 560 550 530 530 530 530 520 510 560 530 530 530 0 200 400 600100 Feet 27.4 AC $ DAN RIVER ASH PLANTDUKE ENERGYEDEN, NORTH CAROLINA FIGURE 1ADRAINAGE AREA ANDFLOWPATH Prepared By: Date: Checked By: Date: Job #: 7810-14-0150 JMS 8/31/2016 RLH 8/31/2016 LEGEND MAJOR CONTOUR (10FT) MINOR CONTOUR (2FT) FLOWPATH POST-DEVELOPMENT DRAINAGE AREA Data Source: Topographic Data from LDSI. D a n R i v e r 29.4 AC 27.4 AC PRIMARYASHPOND SECONDARYASHPOND 57 0 5 4 0 520 51 0 580 5 5 0 560 53 0 500 490 530 5 3 0 560 510 5 3 0 520 540 540 530 5 4 0 56 0 530 530 530 510 520 530 500 530 51 0 500 530 520 520 520 530 540 530 5 4 0 510 540 520 520 520 530 510 51 0 550 510 530 520 55 0 5 1 0 520 530 53 0 0 200 400 600100 Feet $ DAN RIVER ASH PLANTDUKE ENERGYEDEN, NORTH CAROLINA FIGURE 1BDRAINAGE AREA ANDFLOWPATH Prepared By: Date: Checked By: Date: Job #: 7810-14-0150 LEGEND POST-DEVELOPMENT DRAINAGE AREA FLOWPATH MAJOR CONTOUR (10FT) MINOR CONTOUR (2FT) Data Source: Topographic Data from LDSI. FLOWPATHL=1,693.9 FT JMS 9/1/2016 RLH 9/1/2016 D a n R i v er500 520 530 5 2 0 5 8 0 510 510 610 520 530 61 0 51 0 530 500 530 580 530 520 520 5 3 0 510 51 0 5 1 0 56 0 510 54 0 530 530 510 540 55 0 5 1 0 5 7 0 5 1 0 550 590 530 5 8 0 53 0 540 6 0 0 530 5 3 0 5 3 0 590 520 5 3 0 5 3 0 530 510 560 500 520 6 1 0 5 4 0 62 0 5 3 0 60 0 600 59 0 5 2 0 6 4 0 520 550 630 530 530 540 500 540 560 62 0 5 2 0 490 5 8 0 540 61 0 510 580 6 0 0 590 55 0 5 2 0 520 510 56 0 550 540 57 0 53 0 NC OneMap, NC Center for Geographic Information and Analysis, NC 911 Board 0 200 400 600100 Feet $ DAN RIVER ASH PLANTDUKE ENERGYEDEN, NORTH CAROLINA FIGURE 2BASIN CONTOURS Prepared By: Date: Checked By: Date: AMEC Foster Wheeler Job #: 7810-14-0150 LEGEND BASIN OUTLINE MAJOR CONTOUR (10FT) MINOR CONTOUR (2FT) Data Source: Aerial Topographic Survey obtained from LDSI; NAIP Aerial Photography, dated 2010. Bottom of Basin 509' Bottom of Basin 505' Top of Dam 528.52' Top of Dam 540'Primary Dike Breach at 532' SECONDARYASHPONDNORMAL POOL ELEV. = 514 PRIMARYASH POND Bottom of Basin 530' DRY FLYASHBASIN OVERTOPPINGELEV. 558.2' JMS 8/31/2016 RLH 8/31/2016 D an R i v e r 62.9 AC 29.4 AC 27.4 AC PRIMARYASHPOND SECONDARYASHPOND DRY FLY ASHBASIN 59 0 560 54 0 640 630 60 0 620 530 610 5 5 0 57 0 510 520 580 500 490 510 550 600 570 580 5 3 0 5 1 0 52 0 590 530 61 0 59 0 5 1 0 56 0 54 0 58 0 520 620 570 56 0 600 53 0 58 0 600 54 0 590 55 0 520 530 620 590 550 610 610 520 530 560 530 55 0 610 520 530 550 530 510 600 52 0 58 0Ud CmB AyF W CmD AyC DaA SvD SvB NC OneMap, NC Center for Geographic Information and Analysis, NC 911 Board 0 200 400 600100 Feet $ DAN RIVER ASH PLANTDUKE ENERGYEDEN, NORTH CAROLINA FIGURE 3ANRCS SOILS Prepared By: Date: Checked By: Date: Job #: 7810-14-0150 LEGEND POST-DEVELOPMENT DRAINAGE AREA SOIL BOUNDARY MAJOR CONTOUR (10FT) MINOR CONTOUR (2FT) FLOW PATH SOIL TYPES WITHIN DRAINAGE AREAS DRY FLY ASH BASIN B (26.94 AC) C (35.96 AC) SECONDARY ASH POND B (14.45 AC) C (10.14 AC) N/A (4.83 AC) Data Source: USDA NRCS Soil Survey Geographic (SSURGO) database for Rockingham County, North Carolina, dated 2009; NAIP Aerial Photography for Rockingham County, dated 2010. Soil Symbol Description Type AyF Ayersville gravelly loam, 15 to 45 percent slopes B CmB Clover sandy loam, 2 to 8 percent slopes B CmD Clover sandy loam, 8 to 15 percent slopes B DaA Dan River loam, 0 to 2 percent slopes, frequently flooded B Ud Udorthents, loamy C W Water NA JMS 9/1/2016 RLH 9/1/2016 D a n R i v e r 29.4 AC 27.4 AC PRIMARYASHPOND SECONDARYASHPOND 57 0 5 4 0 520 51 0 580 5 5 0 560 53 0 500 490 530 5 3 0 560 510 5 3 0 520 540 540 530 5 4 0 56 0 530 530 530 510 520 530 500 530 51 0 500 530 520 520 520 530 540 530 5 4 0 510 540 520 520 520 530 510 51 0 550 510 530 520 55 0 5 1 0 520 530 53 0 Ud DaA W AyC CsA CmD HbA CmB AyF NC OneMap, NC Center for Geographic Information and Analysis, NC 911 Board 0 200 400 600100 Feet $ DAN RIVER ASH PLANTDUKE ENERGYEDEN, NORTH CAROLINA FIGURE 3BNRCS SOILS Prepared By: Date: Checked By: Date: Job #: 7810-14-0150 LEGEND POST-DEVELOPMENT DRAINAGE AREA SOIL BOUNDARY MAJOR CONTOUR (10FT) MINOR CONTOUR (2FT) FLOW PATHSOIL TYPES WITH DRAINAGE AREA PRIMARY ASH POND B (O.45 AC) C (26.94 AC) Data Source: USDA NRCS Soil Survey Geographic (SSURGO) database for Rockingham County, North Carolina, dated 2009; NAIP Aerial Photography for Rockingham County, dated 2010. Soil Symbol Description Type AyF Ayersville gravelly loam, 15 to 45 percent slopes B CmB Clover sandy loam, 2 to 8 percent slopes B CmD Clover sandy loam, 8 to 15 percent slopes B DaA Dan River loam, 0 to 2 percent slopes, frequently flooded B Ud Udorthents, loamy C W Water NA JMS 9/1/2016 RLH 9/1/2016 15A NCAC 02K .0205 SPILLWAY DESIGN (a) All dams shall have a spillway system with capacity to pass a flow resulting from a design storm indicated in (e) of this Rule for a hazard classification appropriate for the dam, unless the applicant provides calculations, designs, and plans to show that the design flow can be stored, passed through, or passed over the dam without failure occurring. (b) A vegetated earth or unlined emergency spillway will be approved when computations indicate that it will pass the design storm without jeopardizing the safety of the structure. The risk of recurring storms, excessive erosion, and inadequate vegetative cover will be considered acceptable in such a spillway when its average frequency of use is predicted to be no more frequent than once in 25 years for existing class B and for class A dams except for small class A dams designed in accordance with all design criteria established by the U.S.D.A, Soil Conservation Service, and as contained in Engineering Standard 378 of the U.S.D.A., Soil Conservation Service; once in 50 years for new class B, small and medium new class C, and existing class C dams; and once in 100 years for large and very large new class C dams. The dam sizes referred to in this Subsection are defined in (e) of this Rule. (c) Lined Spillways and Channels. The design report shall include design data criteria for open channel, drop, ogee, and chute spillways and other spillway types that include crest structures, walls, channel lining, and miscellaneous details. All masonry or concrete structures shall have joints that are relatively water-tight and shall be placed on foundations capable of sustaining applied loads without undue deformation. Provisions must be made for handling leakage from the channel or underseepage from the foundation which might cause saturation of underlying materials or uplift against the undersurfaces. (d) Within 15 days following passage of the design storm peak, the spillway system shall be capable of removing from the reservoir at least 80 percent of the water temporarily detained in the reservoir above the elevation of the primary spillway. (e) It is recognized that the relationships between valley slope and width, total reservoir storage, drainage area, other hydrologic factors, and specific cultural features have a critical bearing on determining the safe spillway design flood. Rational selection of a safe spillway design flood for specific site conditions based on quantitative analysis is acceptable. The spillway should be sized so that the increased downstream damage resulting from overtopping failure of the dam would not be significant as compared with the damage caused by the flood in the absence of dam overtopping failure. A design storm more frequent than once in 100 years will not be acceptable for any class C dam. In lieu of quantitative analysis, the following tables shall be used as criteria for spillway design storms and permissible velocities for vegetated earth spillways: CRITERIA FOR SPILLWAY DESIGN STORM SIZE CLASSIFICATION Size Total Storage (Ac-Ft)1 Height (ft)1 Small less than 750 less than 35 Medium equal to or greater than 750 and less than 7,500 equal to or greater than 35 and less than 50 Large equal to or greater than 7,500 and less than 50,000 equal to or greater than 50 and less than 100 Very Large equal to or greater than 50,000 equal to or greater than 100 1 The factor determining the largest size shall govern MINIMUM SPILLWAY DESIGN STORMS Hazard Size Spillway Design Flood (SDF) Low (Class A) Small Medium Large Very Large Medium 50 year 100 year 1/3 PMP 1/2 PMP 1/3 PMP Intermediate (Class B) Small Large Very Large 100 year 1/2 PMP 3/4 PMP High (Class C) Small Medium Large Very Large 1/3 PMP 1/2 PMP 3/4 PMP PMP PERMISSIBLE VELOCITIES FOR VEGETATED EARTH SPILLWAYS Permissible velocity1 feet per second Erosion resistant soils Easily erodible soils Slope of exit channel Slope of exit channel Percent Percent Vegetation 0 to 5 5 thru 10 0 to 5 5 thru 10 Bermuda Grass Bahia grass 8 7 6 5 Tall fescue Kentucky bluegrass Reed canary 7 6 5 4 Sod forming grass mixture 5 4 4 3 Lespedeza sericea Weeping lovegrass Alfalfa Crabgrass 3.5 Do not use 2.5 Do not use 2 Increase values 10 percent when the anticipated average use of the spillway is not more frequent than once in 50 years or 25 percent when the anticipated average use is not more frequent than once in 100 years. History Note: Authority G.S. 143-215.26; 143-215.27; 143-215.31; Eff. June 15, 1980. 15A NCAC 02K .0206 CONDUITS (a) A conduit shall be provided to drain each reservoir. The conduit design shall include the computation of the minimum time required to drain the reservoir. (b) All pipe conduits shall convey water at the design velocity without damage to the interior surface. (c) Protection shall be provided to prohibit unsafe seepage along conduits through the dam, abutments, and foundation. The specific design for seepage protection along conduits shall be shown in the drawings and specifications. (d) Adequate allowances shall be incorporated in the design to compensate for differential settlement and possible elongation of the pipe conduit. (e) Trash racks shall be installed at the intake of conduits to prevent clogging the conduit. (f) Pipe Conduit Spillway Materials (1) Pipe conduits shall be designed to support the total external loads in addition to the total internal hydraulic pressure without leakage. (2) Reinforced or Prestressed Concrete Pipe Conduits (A) All conduits are to be designed and constructed to remain watertight under maximum anticipated hydraulic pressure and maximum probable joint opening, including the effects of joint rotation and extensibility. (B) Provisions for safe movement of the barrel are to be provided at each joint in the barrel and at the junction of the barrel and riser or inlet. Cradles are to be articulated if constructed on a yielding foundation. (C) The engineer shall submit the final design details of the proposed pipe to be used for all class A dams where the height of the dam exceeds 35 feet and all class B and C dams. (3) Corrugated Metal Pipe Conduits (A) Corrugated metal pipe shall not be used in class A dams over 35 feet high or in class B and C dams, except for special cases when the design engineer can adequately demonstrate satisfactory performance. (B) Corrugated metal pipe may be used in class A dams which are less than 35 feet high. (C) Corrugated metal conduits shall have watertight connecting bands designed and installed to remain watertight under maximum anticipated hydrostatic head and joint rotation. (D) Flange type couplings shall not be used for corrugated metal pipe or corrugated steel pipe where the diameter exceeds 12 inches unless the applicant produces computations to verify that the flanges and the pipe conduit are of such design to safely support the total external loads in addition to the total internal hydraulic pressure without leakage. (g) Dissipating Devices. All gates, valves, conduits and concrete channel outlets shall be provided with a dissipator designed and constructed to control erosion and prevent damage to the embankment or the downstream outlet or channel. Dan River Ash Basin Watersheds Prepared by: F. Hammers Dated: 05. Apr, 2011 Checked by: R. Hiner Dated: April 8, 2011 TC_ TR55-Method Basin ID:Dry Fly Ash (Condition: Developed) SHEET FLOW SEG #1 SEG #2 Roughness coefficents for sheet flow 2- Year, 24- HR. Rainfall (in)3.80 3.80 Smooth Surface 0.01 Manning's "n"0.13 Range (Natural)0.13 Flow Length (ft)100 Prairie grass 0.15 Elevation Up (ft)628.0 Dense grass (Lawns)0.24 Elevation Down (ft)610.0 Bermuda grass 0.41 Land Slope (ft/ft)0.1800 0.0000 Woods - Light 0.40 Time Of Concentration (mins)3.3 0.0 3.3 Woods - Medium 0.60 Woods - Dense 0.80 SHALLOW CONCENTRATED FLOW SEG #1 SEG #2 Surface Description (P OR U)U U U Flow Length (ft)593 P Elevation Up (ft)610.0 Elevation Down (ft)556.0 Watercourse Slope (ft/ft)0.0911 0.0000 Average Velocity (ft/sec)4.869 0.000 Time Of Concentration (mins)2.0 0.0 2.0 CHANNEL FLOW SEG #1 SEG #2 SEG #3 SEG #4 Bottom Width (ft)2.0 Depth (ft)2.0 Side Slopes (?H:1V) (ft)6.0 Flow Length (ft)977 Elevation Up (ft)556.0 Elevation Down (ft)530.0 Manning's "n"0.055 Area (sq. ft)28.000 0.000 0.000 0.000 Wetted Perimeter (ft)26.331 0.000 0.000 0.000 Hydraulic Radius (ft)1.063 0.000 0.000 0.000 Channel Slope (ft/ft)0.0266 0.0000 0.0000 0.0000 Average Velocity (ft/sec)4.606 0.000 0.000 0.000 Time Of Concentration (mins)3.5 0.0 0.0 0.0 3.5 CIRCULAR PIPE FLOW (Gravity)SEG #1 SEG #2 SEG #3 SEG #4 Pipe Diameter (in) Flow Length (ft) Elevation Up (ft) Elevation Down (ft) Manning's "n" Area (sq. ft)0.000 0.000 0.000 0.000 Wetted Perimeter (ft)0.000 0.000 0.000 0.000 Hydraulic Radius (ft)0.000 0.000 0.000 0.000 Channel Slope (ft/ft)0.0000 0.0000 0.0000 0.0000 Average Velocity (ft/sec)0.000 0.000 0.000 0.000 Time Of Concentration (mins)0.00 0.00 0.00 0.00 0.0 Total Length of Flow Path (feet)1669.60 Total Time Of Concentration (Minutes)8.89 Total Time Of Concentration (Hours)0.1482 Lagtime (Hours)0.0889 Dan River Ash Basin Watersheds Prepared by: F. Hammers Dated: 05. Apr, 2011 Checked by: R. Hiner Dated: April 8, 2011 TC_ TR55-Method Basin ID:Primary Ash Basin (Condition: Developed) SHEET FLOW SEG #1 SEG #2 Roughness coefficents for sheet flow 2- Year, 24- HR. Rainfall (in)3.80 Smooth Surface 0.01 Manning's "n"0.13 Range (Natural)0.13 Flow Length (ft)50 Prairie grass 0.15 Elevation Up (ft)542.0 Dense grass (Lawns)0.24 Elevation Down (ft)538.0 Bermuda grass 0.41 Land Slope (ft/ft)0.0800 0.0000 Woods - Light 0.40 Time Of Concentration (mins)2.6 0.0 2.6 Woods - Medium 0.60 Woods - Dense 0.80 SHALLOW CONCENTRATED FLOW SEG #1 SEG #2 Surface Description (P OR U)U U U Flow Length (ft)50 P Elevation Up (ft)539.0 Elevation Down (ft)536.0 Watercourse Slope (ft/ft)0.0600 0.0000 Average Velocity (ft/sec)3.952 0.000 Time Of Concentration (mins)0.2 0.0 0.2 CHANNEL FLOW SEG #1 SEG #2 SEG #3 SEG #4 Bottom Width (ft)200.0 Depth (ft)1.0 Side Slopes (?H:1V) (ft)20.0 Flow Length (ft)1594 Elevation Up (ft)536.0 Elevation Down (ft)535.0 Manning's "n"0.003 Area (sq. ft)220.000 0.000 0.000 0.000 Wetted Perimeter (ft)240.050 0.000 0.000 0.000 Hydraulic Radius (ft)0.916 0.000 0.000 0.000 Channel Slope (ft/ft)0.0006 0.0000 0.0000 0.0000 Average Velocity (ft/sec)12.139 0.000 0.000 0.000 Time Of Concentration (mins)2.2 0.0 0.0 0.0 2.2 CIRCULAR PIPE FLOW (Gravity)SEG #1 SEG #2 SEG #3 SEG #4 Pipe Diameter (in) Flow Length (ft) Elevation Up (ft) Elevation Down (ft) Manning's "n" Area (sq. ft)0.000 0.000 0.000 0.000 Wetted Perimeter (ft)0.000 0.000 0.000 0.000 Hydraulic Radius (ft)0.000 0.000 0.000 0.000 Channel Slope (ft/ft)0.0000 0.0000 0.0000 0.0000 Average Velocity (ft/sec)0.000 0.000 0.000 0.000 Time Of Concentration (mins)0.00 0.00 0.00 0.00 0.0 Total Length of Flow Path (feet)1693.90 Total Time Of Concentration (Minutes)5.04 Total Time Of Concentration (Hours)0.0841 Lagtime (Hours)0.0504 Dan River Ash Basin Watersheds Prepared by: F. Hammers Dated: 05. Apr, 2011 Checked by: R. Hiner Dated: April 8, 2011 TC_ TR55-Method Basin ID:Secondary Ash Basin (Condition: Developed) SHEET FLOW SEG #1 SEG #2 Roughness coefficents for sheet flow 2- Year, 24- HR. Rainfall (in)3.80 Smooth Surface 0.01 Manning's "n"0.13 Range (Natural)0.13 Flow Length (ft)100 Prairie grass 0.15 Elevation Up (ft)591.0 Dense grass (Lawns)0.24 Elevation Down (ft)590.0 Bermuda grass 0.41 Land Slope (ft/ft)0.0100 0.0000 Woods - Light 0.40 Time Of Concentration (mins)10.6 0.0 10.6 Woods - Medium 0.60 Woods - Dense 0.80 SHALLOW CONCENTRATED FLOW SEG #1 SEG #2 Surface Description (P OR U)U U U Flow Length (ft)1550 P Elevation Up (ft)590.0 Elevation Down (ft)532.0 Watercourse Slope (ft/ft)0.0374 0.0000 Average Velocity (ft/sec)3.121 0.000 Time Of Concentration (mins)8.3 0.0 8.3 CHANNEL FLOW SEG #1 SEG #2 SEG #3 SEG #4 Bottom Width (ft)200.0 Depth (ft)1.0 Side Slopes (?H:1V) (ft)20.0 Flow Length (ft)748 Elevation Up (ft)526.0 Elevation Down (ft)525.0 Manning's "n"0.010 Area (sq. ft)220.000 0.000 0.000 0.000 Wetted Perimeter (ft)240.050 0.000 0.000 0.000 Hydraulic Radius (ft)0.916 0.000 0.000 0.000 Channel Slope (ft/ft)0.0013 0.0000 0.0000 0.0000 Average Velocity (ft/sec)5.139 0.000 0.000 0.000 Time Of Concentration (mins)2.4 0.0 0.0 0.0 2.4 CIRCULAR PIPE FLOW (Gravity)SEG #1 SEG #2 SEG #3 SEG #4 Pipe Diameter (in)60 Flow Length (ft)104 Elevation Up (ft)532.0 Elevation Down (ft)530.0 Manning's "n"0.013 Area (sq. ft)19.625 0.000 0.000 0.000 Wetted Perimeter (ft)15.700 0.000 0.000 0.000 Hydraulic Radius (ft)1.250 0.000 0.000 0.000 Channel Slope (ft/ft)0.0192 0.0000 0.0000 0.0000 Average Velocity (ft/sec)18.457 0.000 0.000 0.000 Time Of Concentration (mins)0.09 0.00 0.00 0.00 0.1 Total Length of Flow Path (feet)2502.00 Total Time Of Concentration (Minutes)21.38 Total Time Of Concentration (Hours)0.3563 Lagtime (Hours)0.2138 SCS Type II 6 hour Rainfall Distribution Time (min)Time (hrs)Cum. % 1 0 0 0.0000 2 7.5 0.125 0.0053 3 15 0.25 0.0108 4 22.5 0.375 0.0164 5 30 0.5 0.0223 6 37.5 0.625 0.0284 7 45 0.75 0.0347 8 52.5 0.875 0.0414 9 60 1 0.0483 10 67.5 1.125 0.0555 11 75 1.25 0.0632 12 82.5 1.375 0.0712 13 90 1.5 0.0797 14 97.5 1.625 0.0887 15 105 1.75 0.0984 16 112.5 1.875 0.1089 17 120 2 0.1203 18 127.5 2.125 0.1328 19 135 2.25 0.1467 20 142.5 2.375 0.1625 21 150 2.5 0.1808 22 157.5 2.625 0.2042 23 165 2.75 0.2351 24 172.5 2.875 0.2833 25 180 3 0.6632 26 187.5 3.125 0.7351 27 195 3.25 0.7724 28 202.5 3.375 0.7989 29 210 3.5 0.8179 30 217.5 3.625 0.8380 31 225 3.75 0.8538 32 232.5 3.875 0.8676 33 240 4 0.8801 34 247.5 4.125 0.8914 35 255 4.25 0.9019 36 262.5 4.375 0.9115 37 270 4.5 0.9206 38 277.5 4.625 0.9291 39 285 4.75 0.9371 40 292.5 4.875 0.9446 41 300 5 0.9519 42 307.5 5.125 0.9588 43 315 5.25 0.9653 44 322.5 5.375 0.9719 45 330 5.5 0.9777 46 337.5 5.625 0.9836 47 345 5.75 0.9892 48 352.5 5.875 0.9947 49 360 6 1.0000 0.0000 0.2000 0.4000 0.6000 0.8000 1.0000 1.2000 0 1 2 3 4 5 6 7 SCS Type II -6-hour SCS Type II 4/18/2011 Dan River Ash Basins Page 1 of 1 SCS CURVE NUMBER CALCULATIONS Dry Fly Ash Basin Land Use Type Soil Type Area (acres)% of Perv.SCS CN Weighted CN Open Space (Fair)B 26.94 42.83%69 29.55 Open Space (Fair)C 35.96 57.17%79 45.16 Open Water (Impervious)N/A 0 100 100.00 Pervious Area 62.9 Weighted CN*74.72 Total Area 62.9 % Impervious 0.00% *Weighted Curve Number does not include impervious area Primary Ash Basin Land Use Type Soil Type Area (acres)% of Perv.SCS CN Weighted CN Open Space (Fair)B 5.21 92.05%69 63.51 Open Space (Fair)C 0.45 7.95%79 6.28 Open Water (Impervious)N/A 21.74 100 100.00 Pervious Area 5.66 Weighted CN*69.80 Total Area 27.4 % Impervious 79.34% *Weighted Curve Number does not include impervious area Secondary Ash Basin Land Use Type Soil Type Area (acres)% of Perv.SCS CN Weighted CN Open Space (Fair)B 14.45 71.39%69 49.26 Open Space (Fair)C 5.79 28.61%79 22.60 Open Water (Impervious)N/A 9.13 100 100.00 Pervious Area 20.24 Weighted CN*71.86 Total Area 29.37 % Impervious 31.09% *Weighted Curve Number does not include impervious area Chaptar 2 Estimating B cineff Tall le ME Runoillaurw narnl En foi uil anaram 1t Taahnilial Raliase 115 Url an lIldralog I fa i Small Watanil ads Q urva nuiul ars fc ii ----_�_•._ __. -. .-.-_ ._••_ Q c vE ii da i c riptic n------------ —--•-----liydre lol lie sc it grc lull_ -- Couch type and hildiolc gia aondillon FUlllyl daveJhpad i LrI an areas (vagatatian astahiltihi i .Miei age psrcan I impervia us ara 2 21 A 13 C D Open sipa co (lawns, parks, gc If aouises, aen et( ies, ate.): I c on condition (gaass aoue n < al %).......................................... 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(210.VI-TR4J, 8 aaaA Ed., Juna 1980) 2-11 Dan River Dry Fly Ash Basin Stage-Storage Elevation Area (SF)Area (acres)]Volume (CF)Volume (AF) 530.0 0.00 0.00 0.00 0.00 531.0 9.05 0.00 5.18 0.00 532.0 14.73 0.00 17.28 0.00 533.0 266.84 0.01 231.10 0.01 534.0 385.17 0.01 555.88 0.01 535.0 12477.58 0.29 5547.74 0.13 536.0 41896.87 0.96 31290.19 0.72 537.0 72821.75 1.67 99408.19 2.28 538.0 83705.98 1.92 177524.38 4.08 539.0 93968.59 2.16 267543.21 6.14 540.0 101822.07 2.34 365443.14 8.39 541.0 118702.41 2.73 479138.31 11.00 542.0 128290.50 2.95 602677.41 13.84 543.0 139051.80 3.19 736958.86 16.92 544.0 148490.61 3.41 880740.25 20.22 545.0 159753.12 3.67 1035211.15 23.77 546.0 170278.65 3.91 1200230.93 27.55 547.0 181759.79 4.17 1376702.33 31.60 548.0 192937.58 4.43 1563990.92 35.90 549.0 205045.32 4.71 1763408.20 40.48 550.0 216804.04 4.98 1974282.62 45.32 551.0 230283.96 5.29 2198687.93 50.47 552.0 242428.06 5.57 2435005.26 55.90 553.0 254995.56 5.85 2684110.41 61.62 554.0 267189.85 6.13 2945161.77 67.61 555.0 283274.13 6.50 3222135.36 73.97 556.0 295942.24 6.79 3511736.84 80.62 557.0 309962.55 7.12 3815344.20 87.59 558.0 322761.35 7.41 4131697.31 94.85 558.2 333600.47 7.66 4197344.84 96.36 Dan River Steam Station Stage-Storage Data Primary Ash Basin Elevation Area (sf)Area (ac)Inc. Vol. (cf)Cum. Vol. (cf)Cum. Vol. (af) 528 322,373.24 7.40 0 0 0.00 529 357,889.78 8.22 340131.51 340131.51 7.81 530 397,708.17 9.13 377798.975 717930.485 16.48 531 427,934.59 9.82 412821.38 1130751.865 25.96 532 488,917.54 11.22 458426.065 1589177.93 36.48 Secondary Ash Basin - 515 Elevation Area (sf)Area (ac)Inc. Vol. (cf)Cum. Vol. (cf)Cum. Vol. (af) 505 14,470.76 0.33 0 0 0.00 506 30,808.92 0.71 0 0 0.00 507 71,914.41 1.65 0 0 0.00 508 93,084.25 2.14 0 0 0.00 509 111,062.61 2.55 0 0 0.00 510 131,750.59 3.02 0 0 0.00 511 145,539.80 3.34 0 0 0.00 512 160,997.92 3.70 0 0 0.00 513 170,799.03 3.92 0 0 0.00 514 210,489.95 4.83 0 0 0.00 515 307,892.76 7.07 0 0 0.00 516 325,532.50 7.47 316712.63 316712.63 7.27 517 342,965.03 7.87 334248.765 650961.395 14.94 518 354,636.67 8.14 348800.85 999762.245 22.95 519 363,320.39 8.34 358978.53 1358740.775 31.19 520 371,083.28 8.52 367201.835 1725942.61 39.62 521 378,179.73 8.68 374631.505 2100574.115 48.22 522 385,521.98 8.85 381850.855 2482424.97 56.99 523 398,408.40 9.15 391965.19 2874390.16 65.99 524 427,168.80 9.81 412788.6 3287178.76 75.46 525 505,379.05 11.60 466273.925 3753452.685 86.17 526 533,029.28 12.24 519204.165 4272656.85 98.09 527 544,347.19 12.50 538688.235 4811345.085 110.45 528 567,885.15 13.04 556116.17 5367461.255 123.22 528.52 582,716.70 13.38 299156.481 5666617.736 130.09 529 596407.37 13.69 582146.26 5949607.515 136.58 Note: Stage-Storage Data based on new topo obtained by LDSI (2014) 1S Dry Fly Ash Basin DA 3S Primary Ash Basin DA 5S Secondary Ash Basin DA 2P Dry Fly Ash Pond 4P Primary Ash Basin Pond 6P Secondary Ash Basin Pond-515 Routing Diagram for Dan_River_Phase_2-515 Prepared by AMEC, Printed 10/12/2016 HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Subcat Reach Pond Link Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 2HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Area Listing (all nodes) Area (acres) CN Description (subcatchment-numbers) 41.390 69 Pasture/grassland/range, Fair, HSG B (1S, 5S) 46.100 79 Pasture/grassland/range, Fair, HSG C (1S, 5S) 0.450 69 Pasture/grassland/range, Poor, HSG B (3S) 26.940 79 Pasture/grassland/range, Poor, HSG C (3S) 4.830 98 Ponded Water (5S) 119.710 76 TOTAL AREA Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 3HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Soil Listing (all nodes) Area (acres) Soil Group Subcatchment Numbers 0.000 HSG A 41.840 HSG B 1S, 3S, 5S 73.040 HSG C 1S, 3S, 5S 0.000 HSG D 4.830 Other 5S 119.710 TOTAL AREA Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 4HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Ground Covers (all nodes) HSG-A (acres) HSG-B (acres) HSG-C (acres) HSG-D (acres) Other (acres) Total (acres) Ground Cover Subcatchment Numbers 0.000 41.390 46.100 0.000 0.000 87.490 Pasture/grassland/range, Fair 1S, 5S 0.000 0.450 26.940 0.000 0.000 27.390 Pasture/grassland/range, Poor 3S 0.000 0.000 0.000 0.000 4.830 4.830 Ponded Water 5S 0.000 41.840 73.040 0.000 4.830 119.710 TOTAL AREA Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 5HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Pipe Listing (all nodes) Line# Node Number In-Invert (feet) Out-Invert (feet) Length (feet) Slope (ft/ft) n Diam/Width (inches) Height (inches) Inside-Fill (inches) 1 5S 0.00 0.00 104.0 0.0192 0.013 60.0 0.0 0.0 2 2P 530.00 525.00 200.0 0.0250 0.024 36.0 0.0 0.0 3 4P 526.17 524.00 50.0 0.0434 0.013 36.0 0.0 0.0 4 6P 498.00 495.00 150.0 0.0200 0.013 33.0 0.0 0.0 Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 6HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Time span=0.00-72.00 hrs, dt=0.05 hrs, 1441 points Runoff by SCS TR-20 method, UH=SCS, Weighted-CN Reach routing by Dyn-Stor-Ind method - Pond routing by Dyn-Stor-Ind method Runoff Area=62.900 ac 0.00% Impervious Runoff Depth=18.35"Subcatchment 1S: Dry Fly Ash Basin DA Flow Length=1,670' Tc=9.0 min CN=75 Runoff=2,363.41 cfs 96.197 af Runoff Area=27.390 ac 0.00% Impervious Runoff Depth=19.00"Subcatchment 3S: Primary Ash Basin DA Flow Length=1,694' Tc=43.2 min CN=79 Runoff=469.95 cfs 43.377 af Runoff Area=29.420 ac 16.42% Impervious Runoff Depth=18.68"Subcatchment 5S: Secondary Ash Basin Flow Length=2,502' Tc=22.1 min CN=77 Runoff=762.01 cfs 45.804 af Peak Elev=553.28' Storage=64.142 af Inflow=2,363.41 cfs 96.197 afPond 2P: Dry Fly Ash Pond 36.0" Round Culvert n=0.024 L=200.0' S=0.0250 '/' Outflow=112.32 cfs 96.197 af Peak Elev=531.34' Storage=29.582 af Inflow=469.95 cfs 43.377 afPond 4P: Primary Ash Basin Pond Outflow=65.24 cfs 43.288 af Peak Elev=522.96' Storage=65.634 af Inflow=891.47 cfs 185.289 afPond 6P: Secondary Ash Basin Outflow=138.89 cfs 185.209 af Total Runoff Area = 119.710 ac Runoff Volume = 185.378 af Average Runoff Depth = 18.58" 95.97% Pervious = 114.880 ac 4.03% Impervious = 4.830 ac Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 7HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Summary for Subcatchment 1S: Dry Fly Ash Basin DA Runoff = 2,363.41 cfs @ 3.00 hrs, Volume= 96.197 af, Depth=18.35" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-72.00 hrs, dt= 0.05 hrs Type II 6-hr 3/4 PMP Rainfall=21.90" Area (ac) CN Description 26.940 69 Pasture/grassland/range, Fair, HSG B 35.960 79 Pasture/grassland/range, Fair, HSG C 62.900 75 Weighted Average 62.900 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 3.5 100 0.1800 0.47 Sheet Flow, Sheet Flow Range n= 0.130 P2= 3.40" 2.0 593 0.0911 4.86 Shallow Concentrated Flow, Shallow Concentrated Unpaved Kv= 16.1 fps 3.5 977 0.0266 4.59 128.64 Channel Flow, Channel Flow Area= 28.0 sf Perim= 26.3' r= 1.06' n= 0.055 9.0 1,670 Total Subcatchment 1S: Dry Fly Ash Basin DA Runoff Hydrograph Time (hours) 7065605550454035302520151050 Fl o w ( c f s ) 2,600 2,400 2,200 2,000 1,800 1,600 1,400 1,200 1,000 800 600 400 200 0 Runoff=2,363.41 cfs @ 3.00 hrs Type II 6-hr 3/4 PMP Rainfall=21.90" Runoff Area=62.900 ac Runoff Volume=96.197 af Runoff Depth=18.35" Flow Length=1,670' Tc=9.0 min CN=75 2,363.41 cfs @ 3.00 hrs Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 8HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Summary for Subcatchment 3S: Primary Ash Basin DA Runoff = 469.95 cfs @ 3.39 hrs, Volume= 43.377 af, Depth=19.00" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-72.00 hrs, dt= 0.05 hrs Type II 6-hr 3/4 PMP Rainfall=21.90" Area (ac) CN Description * 0.450 69 Pasture/grassland/range, Poor, HSG B * 26.940 79 Pasture/grassland/range, Poor, HSG C 27.390 79 Weighted Average 27.390 100.00% Pervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 11.2 100 0.0100 0.15 Sheet Flow, Sheet Flow Range n= 0.130 P2= 3.40" 32.0 1,594 0.0069 0.83 Shallow Concentrated Flow, Shallow Concentrated Nearly Bare & Untilled Kv= 10.0 fps 43.2 1,694 Total Subcatchment 3S: Primary Ash Basin DA Runoff Hydrograph Time (hours) 7065605550454035302520151050 Fl o w ( c f s ) 500 450 400 350 300 250 200 150 100 50 0 Runoff=469.95 cfs @ 3.39 hrs Type II 6-hr 3/4 PMP Rainfall=21.90" Runoff Area=27.390 ac Runoff Volume=43.377 af Runoff Depth=19.00" Flow Length=1,694' Tc=43.2 min CN=79 469.95 cfs @ 3.39 hrs Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 9HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Summary for Subcatchment 5S: Secondary Ash Basin DA Runoff = 762.01 cfs @ 3.14 hrs, Volume= 45.804 af, Depth=18.68" Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-72.00 hrs, dt= 0.05 hrs Type II 6-hr 3/4 PMP Rainfall=21.90" Area (ac) CN Description 14.450 69 Pasture/grassland/range, Fair, HSG B 10.140 79 Pasture/grassland/range, Fair, HSG C * 4.830 98 Ponded Water 29.420 77 Weighted Average 24.590 83.58% Pervious Area 4.830 16.42% Impervious Area Tc Length Slope Velocity Capacity Description (min) (feet) (ft/ft) (ft/sec) (cfs) 11.2 100 0.0100 0.15 Sheet Flow, Sheet Flow Range n= 0.130 P2= 3.40" 8.3 1,550 0.0374 3.11 Shallow Concentrated Flow, Shallow Concentrated Flow Unpaved Kv= 16.1 fps 2.5 748 0.0013 5.06 1,112.30 Channel Flow, Channel Flow Area= 220.0 sf Perim= 240.0' r= 0.92' n= 0.010 0.1 104 0.0192 18.38 360.88 Pipe Channel, RCP_Round 60" 60.0" Round Area= 19.6 sf Perim= 15.7' r= 1.25' n= 0.013 22.1 2,502 Total Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 10HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Subcatchment 5S: Secondary Ash Basin DA Runoff Hydrograph Time (hours) 7065605550454035302520151050 Fl o w ( c f s ) 800 700 600 500 400 300 200 100 0 Runoff=762.01 cfs @ 3.14 hrs Type II 6-hr 3/4 PMP Rainfall=21.90" Runoff Area=29.420 ac Runoff Volume=45.804 af Runoff Depth=18.68" Flow Length=2,502' Tc=22.1 min CN=77 762.01 cfs @ 3.14 hrs Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 11HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Summary for Pond 2P: Dry Fly Ash Pond Inflow Area = 62.900 ac, 0.00% Impervious, Inflow Depth = 18.35" for 3/4 PMP event Inflow = 2,363.41 cfs @ 3.00 hrs, Volume= 96.197 af Outflow = 112.32 cfs @ 4.24 hrs, Volume= 96.197 af, Atten= 95%, Lag= 74.2 min Primary = 112.32 cfs @ 4.24 hrs, Volume= 96.197 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-72.00 hrs, dt= 0.05 hrs Peak Elev= 553.28' @ 4.24 hrs Surf.Area= 0.000 ac Storage= 64.142 af Plug-Flow detention time= 254.4 min calculated for 96.130 af (100% of inflow) Center-of-Mass det. time= 254.5 min ( 449.8 - 195.3 ) Volume Invert Avail.Storage Storage Description #1 530.00' 96.400 af Custom Stage Data Listed below Elevation Cum.Store (feet) (acre-feet) 530.00 0.000 535.00 0.130 540.00 8.400 545.00 23.800 550.00 45.300 555.00 74.000 558.20 96.400 Device Routing Invert Outlet Devices #1 Primary 530.00'36.0" Round Culvert L= 200.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 530.00' / 525.00' S= 0.0250 '/' Cc= 0.900 n= 0.024, Flow Area= 7.07 sf Primary OutFlow Max=112.32 cfs @ 4.24 hrs HW=553.28' TW=520.83' (Dynamic Tailwater) 1=Culvert (Barrel Controls 112.32 cfs @ 15.89 fps) Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 12HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Pond 2P: Dry Fly Ash Pond Inflow Primary Hydrograph Time (hours) 7065605550454035302520151050 Fl o w ( c f s ) 2,500 2,000 1,500 1,000 500 0 Inflow Area=62.900 ac Inflow=2,363.41 cfs @ 3.00 hrs Primary=112.32 cfs @ 4.24 hrs Peak Elev=553.28' Storage=64.142 af 36.0" Round Culvert n=0.024 L=200.0' S=0.0250 '/' 2,363.41 cfs @ 3.00 hrs 112.32 cfs @ 4.24 hrs Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 13HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Summary for Pond 4P: Primary Ash Basin Pond Inflow Area = 27.390 ac, 0.00% Impervious, Inflow Depth = 19.00" for 3/4 PMP event Inflow = 469.95 cfs @ 3.39 hrs, Volume= 43.377 af Outflow = 65.24 cfs @ 4.63 hrs, Volume= 43.288 af, Atten= 86%, Lag= 74.2 min Primary = 65.24 cfs @ 4.63 hrs, Volume= 43.288 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-72.00 hrs, dt= 0.05 hrs Peak Elev= 531.34' @ 4.63 hrs Surf.Area= 0.000 ac Storage= 29.582 af Plug-Flow detention time= 286.7 min calculated for 43.258 af (100% of inflow) Center-of-Mass det. time= 288.6 min ( 513.9 - 225.4 ) Volume Invert Avail.Storage Storage Description #1 528.00' 36.480 af Custom Stage Data Listed below Elevation Cum.Store (feet) (acre-feet) 528.00 0.000 529.00 7.810 530.00 16.480 531.00 25.960 532.00 36.480 Device Routing Invert Outlet Devices #1 Primary 526.17'36.0" Round Culvert L= 50.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 526.17' / 524.00' S= 0.0434 '/' Cc= 0.900 n= 0.013, Flow Area= 7.07 sf #2 Device 1 528.00'4.0' long Sharp-Crested Rectangular Weir 2 End Contraction(s) #3 Device 1 528.00'4.0' long Sharp-Crested Rectangular Weir 2 End Contraction(s) Primary OutFlow Max=65.24 cfs @ 4.63 hrs HW=531.34' TW=521.20' (Dynamic Tailwater) 1=Culvert (Inlet Controls 65.24 cfs @ 9.23 fps) 2=Sharp-Crested Rectangular Weir (Passes < 66.62 cfs potential flow) 3=Sharp-Crested Rectangular Weir (Passes < 66.62 cfs potential flow) Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 14HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Pond 4P: Primary Ash Basin Pond Inflow Primary Hydrograph Time (hours) 7065605550454035302520151050 Fl o w ( c f s ) 500 450 400 350 300 250 200 150 100 50 0 Inflow Area=27.390 ac Inflow=469.95 cfs @ 3.39 hrs Primary=65.24 cfs @ 4.63 hrs Peak Elev=531.34' Storage=29.582 af 469.95 cfs @ 3.39 hrs 65.24 cfs @ 4.63 hrs Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 15HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Summary for Pond 6P: Secondary Ash Basin Pond-515 Inflow Area = 119.710 ac, 4.03% Impervious, Inflow Depth = 18.57" for 3/4 PMP event Inflow = 891.47 cfs @ 3.15 hrs, Volume= 185.289 af Outflow = 138.89 cfs @ 9.63 hrs, Volume= 185.209 af, Atten= 84%, Lag= 389.0 min Primary = 138.89 cfs @ 9.63 hrs, Volume= 185.209 af Routing by Dyn-Stor-Ind method, Time Span= 0.00-72.00 hrs, dt= 0.05 hrs Peak Elev= 522.96' @ 9.63 hrs Surf.Area= 0.000 ac Storage= 65.634 af Plug-Flow detention time= 263.9 min calculated for 185.209 af (100% of inflow) Center-of-Mass det. time= 262.5 min ( 667.2 - 404.7 ) Volume Invert Avail.Storage Storage Description #1 515.00' 136.580 af Custom Stage Data Listed below Elevation Cum.Store (feet) (acre-feet) 515.00 0.000 516.00 7.270 517.00 14.940 518.00 22.950 519.00 31.190 520.00 39.620 521.00 48.220 522.00 56.990 523.00 65.990 524.00 75.460 525.00 86.170 526.00 98.090 527.00 110.450 528.00 123.220 529.00 136.580 Device Routing Invert Outlet Devices #1 Primary 498.00'33.0" Round Culvert L= 150.0' RCP, square edge headwall, Ke= 0.500 Inlet / Outlet Invert= 498.00' / 495.00' S= 0.0200 '/' Cc= 0.900 n= 0.013, Flow Area= 5.94 sf #2 Device 1 515.00'4.0' long Sharp-Crested Rectangular Weir 2 End Contraction(s) #3 Device 1 515.00'4.0' long Sharp-Crested Rectangular Weir 2 End Contraction(s) #4 Device 1 515.00'4.0' long Sharp-Crested Rectangular Weir 2 End Contraction(s) #5 Device 1 515.00'4.0' long Sharp-Crested Rectangular Weir 2 End Contraction(s) Primary OutFlow Max=138.89 cfs @ 9.63 hrs HW=522.96' (Free Discharge) 1=Culvert (Inlet Controls 138.89 cfs @ 23.38 fps) 2=Sharp-Crested Rectangular Weir (Passes < 176.84 cfs potential flow) 3=Sharp-Crested Rectangular Weir (Passes < 176.84 cfs potential flow) 4=Sharp-Crested Rectangular Weir (Passes < 176.84 cfs potential flow) 5=Sharp-Crested Rectangular Weir (Passes < 176.84 cfs potential flow) Type II 6-hr 3/4 PMP Rainfall=21.90"Dan_River_Phase_2-515 Printed 10/12/2016Prepared by AMEC Page 16HydroCAD® 10.00-18 s/n 00996 © 2016 HydroCAD Software Solutions LLC Pond 6P: Secondary Ash Basin Pond-515 Inflow Primary Hydrograph Time (hours) 7065605550454035302520151050 Fl o w ( c f s ) 900 800 700 600 500 400 300 200 100 0 Inflow Area=119.710 ac Inflow=891.47 cfs @ 3.15 hrs Primary=138.89 cfs @ 9.63 hrs Peak Elev=522.96' Storage=65.634 af 891.47 cfs @ 3.15 hrs 138.89 cfs @ 9.63 hrs