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SW6210202_NCDEQ Hydrology Report - Rev. 1_20210512
Hydrology Study For Ft. Bragg Ft. Bragg, North Carolina Prepared for: North Carolina Department of Environmental Quality 225 Green Street, Suite 714 Fayetteville, NC 28301 Prepared by: Steve Waldron C)WE ENGINEER S October 30, 2020 Rev. 1 - May 12, 2021 Contents I. Executive Summary..............................................................................1 II. Hydrology.............................................................................................1 A. Objectives................................................................................................................... 1 B. Model Development................................................................................................... 1 III. Existing Conditions Hydrologic Analysis (Pre -Development) ................. 3 IV. Proposed Conditions Hydrologic Analysis (Post-Development).............4 V. Conclusion............................................................................................ 7 Tables Table 1: Rainfall Recurrence Intervals............................................................................2 Table 2: Study Point #1 Pre -Development Peak Flows....................................................3 Table 3: Study Point #2 Pre -Development Peak Flows....................................................4 Table 4: Overall Site Pre -Development Peak Flows........................................................4 Table 5: Study Point #1 Post -Development Peak Flows..................................................5 Table 6: Study Point #2 Post -Development Peak Flows..................................................5 Table 7: Overall Site Post -Development Peak Flows.......................................................6 Table 8: Study Point #1 Pre -Development and Post -Development Comparison ..............6 Table 9: Study Point #2 Pre -Development and Post -Development Comparison ..............6 Table 10: Overall Site Pre -Development and Post -Development Comparison.................7 Exhibits Exhibit1: Vicinity Map..................................................................................................9 Exhibit2: Soils Map.....................................................................................................10 Appendices Appendix 1: Pope Army NOAA Precipitation Data........................................................12 Appendix 2: Drainage Basin Maps...............................................................................13 Appendix 3: Calculations & Hydraflow / Storm Sewer Output......................................16 I. Executive Summary Lowe Engineers (henceforth to be referred to as "Lowe") has prepared this hydrological study on behalf of the United States Army Corps of Engineers for the proposed development of the SOF Operations Addition. The facility includes the construction of a 55,000 SF building, pavement, and approximately 277 parking spaces. The Ft. Bragg SOF Addition project proposes to develop ±5.78 acres of property located at an unnamed roadway near the intersection of Lamont Rd/McKellars Rd, Ft. Bragg, North Carolina in Cumberland County. The project location is depicted on the Vicinity Map, Exhibit 1. II. Hydrology A. Objectives This hydrology study evaluates the existing (pre -development) and proposed (post -development) hydrologic conditions of the site to determine the requirements for stormwater quality, detention, and extreme flood protection. This study was developed using the federal and state laws which govern the National Pollutant Discharge Elimination System (NPDES), as part of the CFR 40 Clean Water Act, and mandates local authorities to review, permit, and enforce all point discharges into waters of the United States, such as land disturbing activities in excess of 1-acre. B. Model Development The NRCS Discrete Method, Hydraflow version 2020, and Storm Sewers version 2020 (which are extensions of AutoCAD Civil 3D 2020) were used to model the existing and proposed drainage, bioretention cells, and pipe sizes. The following information is necessary to utilize the SCS method: 1. Determination of curve numbers in the drainage areas which is representative of the land uses and their hydrologic soil types. 2. Calculations of the times of concentration to their respective bioretention cells. 3. Type II rainfall distribution hydrographs, which are used to determine the total and excess rainfall amounts. The model uses a standard time series plot generated for an SCS Type II 24-hour rainfall distribution event for the 1-, 2-, 10-, 25-, 50-, and 100-year rainfall depths specific to that geographic location. Rainfall depths for this project were obtained from the NOAA Precipitation Frequency Data Server (PFDS). The design precipitation depths are listed below in Table 1. Additionally, Lowe designed proposed additions to the existing storm pipe network by entering Hydraflow bioretention cell outflow data into Storm Sewers. The graphical analysis and calculations can be reviewed in Appendix 3. Table 1: Rainfall Recurrence Intervals Rainfall Recurrence Depth Interval (Inches) Required Retention 1.00 1-year 3.06 2-year 3.70 10-year 5.46 25-year 6.52 50-year 7.38 100-year 8.26 To accurately determine total discharge volumes and rates, Lowe divided pre -developed and post -developed sites into sub -basins with varying curve numbers. Because each of the sub -basins are relatively small, times of concentration for each sub -basin are 5 minutes. Per the USGS Soils Map (Exhibit 2), Lowe entered curve numbers for Hydrologic Soils Groups (HSGs) "A". To show retention of the first 1" from impervious area, Lowe utilized NRCS Discrete Method calculations. See Appendix 3 for NRCS-modeled runoff calculations. Areas of relatively concentrated flows were assigned hydrological study point numbers, of which there are 2. The study points and descriptions of their discharge areas are listed below... • Study Point #1 includes... o Discharge area for "PRE -BASIN #1", which includes building O190U, its associated roadways/parking, adjacent embankments, and offsite runoff originating from the South. o Discharge area for "POST -BASIN #1", which includes the proposed building, surrounding roadways, and adjacent embankments. • Study Point #2 includes... o Discharge area for "PRE -BASIN #2", which is composed primarily of trees and vehicle -compacted soil. o Discharge area for "POST -BASIN #2", which includes additional facility parking. To review the sub -basin maps as well as all study point locations and pre -basin and post -basin routing, see drainage basin maps in Appendix 2. To ensure adequate bioretention cell volumes and properly designed outlet control structures, Lowe routed the hydrographs for various "POST - #X" hydrographs to their corresponding bioretention cells. To confirm 100-Yr conveyance, 25-Yr 2 hydraulic grade lines, and 10-Yr event outlet velocities adherence to NPDES standards, Lowe entered flow rates from pipe outlets into Storm Sewers. Results from the Storm Sewers analysis can be reviewed in Appendix 3. III. Existing Conditions Hydrologic Analysis (Pre -Development) The project site totals approx. 5.78 acres of pervious and impervious area. The impervious area consists of two buildings and roadways/parking that total approx. 2.5 acres. The remaining pervious area is comprised of woods and open space with soils primarily consisting of well - draining soils (HSG "A"). The topography slopes mildly to moderately across the site from East to West. The site is located within the Cape Fear River Basin and drains Northwestwardly to Cypress Creek which connects to Little River approximately 3 miles downstream. Per 2018 NCDEQ "2018 Final 303(d) List" no portion of Cypress Creek is classified as a 303(d) impaired waterbody. Most upstream runoff, including much of that denoted as "OFFSITE", appears to flow through the existing on -site stormwater network to the nearby existing detention area. Lowe calculated pre -development peak flowrates and hydraulic volumes. The results of those calculations are depicted in the tables below. Approximately 14 acres of upstream runoff appears to drain to the nearby detention area, but because the upstream runoff is routed through the existing network (which will be re-routed through a portion of the proposed network to be used exclusively for conveyance of existing upstream runoff), it was not included in the calculations for this report. Table 2 shows the flowrates and hydraulic volumes for "Study Pt. #1". Table 3 shows the flowrates and hydraulic volumes for "Study Pt. #2". Table 4 shows the overall site flowrates and hydraulic volumes for each pre -developed stormwater event. Note: Values for the following tables are the results of Hydraflow Analysis (Appendix 4). Table 2: Study Point #1 Pre -Development Peak Flows (Pre -Basin #1) Frequency (yr) Peak Discharge (cfs) Hydraulic Volume (ft3) 1 14.96 34,925 2 18.16 42,587 5 24.02 56,083 10 29.25 68,059 25 36.94 85,714 50 43.21 100,134 100 49.73 115,2 Table 3: Study Point #2 Pre -Development Peak Flows (Pre -Basin #2) Frequency (yr) Peak Discharge (cfs) Hydraulic Volume (ft3) 1 2.46 4,981 2 3.42 6,877 5 5.17 10,408 10 6.75 13,670 25 9.17 18,612 50 11.14 22,723 100 13.20 27,067 Table 4: Overall Site Pre -Development Peak Flows (Pre -Basin #1 & Pre -Basin #2) Frequency (yr) Peak Discharge (cfs) Hydraulic Volume (ft3) 1 17.33 39,907 2 21.50 49,464 5 29.15 66,491 10 36.00 81,729 25 46.11 104,326 50 54.35 122,856 100 62.94 142,275 IV. Proposed Conditions Hydrologic Analysis (Post -Development) The proposed site consists of a 55,000 SF -footprint building, pavement, and approximately 263 parking spaces. The addition of these materials will result in the percentage of post -developed impervious area being greater than that of the impervious area in pre -developed conditions. Impervious area percentages for individual sub -basins can be reviewed in Appendix 2. To meet NCDEQ and NPDES requirements, the post -developed site stormwater control measures were designed to ensure that the first 1" of post -developed runoff generated by impervious area is retained on -site (required and designed retention volumes for each drainage area can be reviewed in Appendix 3). Additionally, Lowe designed the retention measures to ensure that the annual post -developed hydraulic volume is less than a 10% increase over the pre -developed hydraulic volume. Differing site conditions between the pre -developed and post -developed site will result in increased impervious area. As a result of the increased impervious area, soil infiltration rates will be reduced. Because the re -developed site will be infiltrating at a lower rate, stormwater runoff will increase. Increased runoff generated by expanded parking areas and roadways will be routed to seven Bioretention Cells. The existing detention area inflows, where all "POST -BASIN #1" treated stormwater will be routed, is "Study Pt. #1". Table 5 shows the flowrates and hydraulic 4 volumes for "Study Pt. #1". Table 6 shows the flowrates and hydraulic volumes for "Study Pt. #2". Table 7 shows the overall site flowrates and hydraulic volumes for each post -developed stormwater event. The increased post -developed runoff will be controlled by routing the applicable post -developed area to bioretention cells for stormwater quality and quantity control. Five of the seven bioretention cell OCSs control and direct flow to "Study Pt. #1" (existing detention area). Due to topographical constraints, portions of the post -developed site runoff will not be collected. However, uncollected runoff generated from said proposed impervious area is approximately equivalent to the existing area and location which currently discharges to the existing detention area. Uncollected runoff from proposed pervious area is included in the total runoff calculations for each study point as well as the entire site. The results of these calculations can be broadly reviewed in Table 10 and in greater detail in Appendix 3. Lowe also calculated the pre -developed and post -developed comparisons of peak flowrates and hydraulic volumes for each study point and rain event. Table 5 shows the flowrates and hydraulic volumes for all events for "Study Pt. #1". Table 6 shows the flowrates and hydraulic volumes for all events for "Study Pt. #2". Table 7 shows the flowrates and hydraulic volumes for all events sitewide. Tables 8 and 9 show pre- and post -development comparisons for the site. Table 10 shows that the overall post -developed site peak hydraulic volumes are less than a 10% increase for all events, and therefore adheres to the limits set by the NCDEQ Stormwater Design Manual. Note: Values for the following tables are the results of Hydraflow Analysis (Appendix 3). Table 5: Study Point #1 Post -Development Peak Flows (Post -Basin #1) Frequency (yr) Peak Discharge (cfs) Hydraulic Volume (W) 1 16.89 35,686 2 20.08 43,870 5 25.48 58,000 10 30.27 70,341 25 37.41 88,330 50 43.27 102,905 100 49.19 118,070 Table 6: Study Point #2 Post -Development Peak Flows (Post -Basin #2) Frequency (yr) Peak Discharge (cfs) Hydraulic Volume (W) 1 4.10 7,432 2 4.87 9,471 5 6.32 13,079 10 7.65 16,306 25 9.71 21,102 50 11.39 25,053 100 13.17 29,21 Table 7: Overall Site Post -Development Peak Flows (Post -Basin #1 & Post -Basin #2) Frequency (yr) Peak Discharge (cfs) Hydraulic Volume (ft3) 1 20.99 43,118 2 24.94 53,341 5 31.80 71,079 10 37.92 86,648 25 47.12 109,432 50 54.65 127,958 100 62.36 147,28 Table 8: Study Pt. #1 Pre -Development & Post -Development Comparison Frequency (yr) Pre -Development Peak Discharge (cfs) Pre -Development Hydraulic Volume (ft3) post -Development Peak Discharge (cfs) Post -Development 3 Hydraulic Volume (ft ) 1 14.96 34,925 16.89 35,686 2 18.16 42,587 20.08 431870 5 24.02 56,083 25.48 58,000 10 29.25 68,059 30.27 70,341 25 1 36.94 1 85,714 37.41 881330 50 43.21 100,134 43.27 102,905 100 49.73 115,208 49.19 118,070 Table 9: Study Pt. #2 Pre -Development & Post -Development Comparison Frequency (yr) Pre -Development Peak Discharge (cfs) Pre -Development Hydraulic Volume (ft3) post -Development Peak Discharge (cfs) Post -Development 3 Hydraulic Volume (ft ) 1 2.46 4,981 4.10 7,432 2 3.42 6,877 4.87 9,471 5 5.17 10,408 6.32 13,079 10 6.75 13,670 7.65 16,306 25 9.17 18,612 9.71 21,102 50 11.14 22,723 11.39 251053 100 13.20 27,067 13.17 29,210 Table 10: Overall Site Pre -Development & Post -Development Comparison Frequency (yr) Pre -Development Peak Discharge (cfs) Pre -Development Hydraulic Volume (ft3) post -Development Peak Discharge (cfs) Post -Development 3 Hydraulic Volume (ft ) 1 17.33 39,907 20.99 43,118 2 21.50 49,464 24.94 531341 5 29.15 66,491 31.80 71,079 10 36.00 81,729 37.92 86,648 25 46.11 104,326 47.12 1091432 50 54.35 122,856 54.65 127,958 100 62.94 142,275 62.36 147,280 V. Conclusion The proposed site plan's increase in impervious area will result in varying pre -developed and post -developed peak flowrate and hydraulic volume changes. Study Point #1 results show that pre -developed and post -developed flowrate and hydraulic volume percentage changes increase steadily as the event frequency decreases, with all runoff from all rain events resulting in slight volume increases. Study Point #2 shows similar reductions as those calculated for Study Point #1. Because the site was designed to retain the post -developed runoff generated by the first 1" of rainfall, the overall site post -developed conditions will increase hydraulic volumes for all rain events, but by less than 10%. Therefore, runoff from all storms will fall within the NC Stormwater Rule 15A NCAC 02H .1002 (44) "Runoff Volume Match" definition which states that "annual runoff volume after development shall not be more than ten percent higher than the annual runoff volume before development." Exhibits Exhibit 1 Vicinity Map Exhibit 2 Soils Map Exhibit 1 Vicinity Map E -qw3 —vww Exhibit 2 3 Soil Map —Cumberland County, North Carolina to � a* a s ' mp -S.L: 1:7,92OWPr:tEa mn h,.F,.W s {ir. 57 4—La it N w— A % o 1W a10 nao eao rt 0 -r4W Ti06 �a aai�a: vr�ntermmr carrrmurdra�: w�a Edge trnn une x�v w�a USDA Natural Resources Web Soil Survey 611512020 21111111111111 Conservation Service National Cooperative Soil Survey Page 1 or 3 Map Unit Legend Map Unit Symbol Map link Name Acres in AOI percent of AOI BaB Blaney loamy sand, 2 to 8 1.3 0.4% percent slopes BaD Blaney loamy sand, 8 to 15 60.1 20.3% percent slopes B 6 Bragg sandy loam, 1 to 4 19.7 6.7% percent slopes CaB Candor sand, 1 to 8 percent 129.2 43.7% slopes JT Johnston loam 14.7 5.01A NoB Norfolk loamy sand, 2 to 6 29.8 10.1 % percent slopes WaB Wagram loamy sand, 0 to 6 40.5 13.7% percent slopes Totals for Area of Interest 295A 100.0% 10 Appendices Appendix 1: Pope Army Airfield NOAA Precipitation Data Appendix 2: Drainage Basin Maps Appendix 3: Calculations & Hydraf low / Storm Sewer Output 11 Appendix 1 Pope Army Airfield NOAA Precipitation Data NOAA Atlas 14, Volume 2. Version 3 POPE AFB Station ID: 314=1 Location name: Pope PuTuy Air45eld, North Carolina, USA* Latitude: 35.173P, LongikAe:-79.00W �� Elevation_ Elevation Istation nleladata): 218 ft*' ' wu'ce: E3R- Map: " spuroa: UEG3 POINT PRECiPrrATION FREQUENCY ESTIMATES .a _- -- - 1 - 6 _ - ==zrosk, M.'rekta a9d G. Rehr `JClAA. F4a:.•2 .'.e:e Z-he 3prft Maryor,d PF tabular r=3r_pr=;i I MLapL & aerials PF tabular PDS-based point precipitabon "uency estimates with 90% confidence intervals [in inche!W duration Average recurrence iniprval wears} 1 2 5 10 25 11 50 100 200 1 5E10 1OW 5-"n 0-AM D.512 0,59E Dim 0.732 0-783 0.132 0-075 0-921 0.96E 0.391-0-97I 0.461-0a?4 -OM9 0.592-0335 6.55".817 -74X-OA73 '0.738-0.925 .7744k973 ,813-1.03 .8431 10-Min GAM 0.819 11 0,955 1-05 11-17 1.25 1-32 1.39 1AT 1,53 Qs2A-11.776' 0.73M-918 RH5Q1. _4i5-1. ll 1.11-1.39 1.17-1.4 123-1.51 129-1.63 1.33-1.69 15-min 0-1167 1.03 121 1-33 1-48 1.5E 1-67 1.75 1.25 1,9'I 0.780-0.97 AV-1-15 1.09-i-35 12i"AlI1.32-1.E5 1A1-175 q 1.£2-2.0E 1.67-2.12 30-min 1.19 1AI2 1.72 1-93 L79 2.38 2-56 2.73 2,94 3-10 1.07-1.33 12P 1 1.55-1-42 1-73-2-1 196-2.44 2-13-2�fi5Y �258-327 70-3.41 1.48 1.79 2.20 251 292 3.22 153 3.22 422 4M 60�r1in 1.33-1.£5 111-2. 1. &2AI 2A1 .E13.25 2-ti8-3S9'i 3.13-3. 3.38-425 3.70,4.68 .94-5.02 1.74 210 2.63 3.03 3-% 3.9E 4-AD 4.22 5,37 5M 2fir 2.34-297 70-3 +12 -15-4.63 3-51AM 3A5-4.9E 4.19-SA3 4.fO-&W 4.%-6.FA 1m 223 2A0 326 &W 4.37 d_RR 5A1 G_14 6.73 1.55-2.09 2,53 2.50- t18 90-3�fi8 .43-4.37 3.&dA94Y 42&6.50 4.b3�s-10 525{k91 5.70-7.Sfi 220 2-" 3 35 3-90 &65 5-26 5-911 G.56 7.45 R22 6 �1r 1.99-2,45 Al-2.% 3.023-32 1-4.3x -ib5.15 &M,5d2 520-6.51 5.73-722 6AS324 .01�.Q5 2G0 3.1A 3.97 4-65 am -r. R.04 92B 10,312a1r I {2.35-2-CA1 f2AS�3.48}V 11AA1 4.1&.15 9M.15 - 5.G67AnY d.30 .98-W11 2 &57-11.2 2A�1r 3.07 ii 3.71 4.68 -1.44 6 % 7.34 821 9.11 1 d-3 113 ;2.85-3.315 II E3-d4d.06} 4.3d-5.D4 S-U43.8 e-00-7.00 15--m 90 .54-8.63 8.MAr.;9 9.42-11-1 10-3122 2_day 335E 411 1.38 6.24 TA2 835 -32 10.3 11.7 128 {3.32-363} fAA1d.d1S 5.0Y-5.7a 5-90-5.59 5.87-7.95 7-72�.96Y 8.58-16.0 .4E-11.1 10.7-12.6 11-5-13.7 3-day 3.78 4.55 5.67 G.55 T-77 8.73 9-73 14.8 12.2 13-3 ;3.53-4.045 f426d.87} 5.29£.-05 10-7.00 213.30 E08-9.33' fa-1D .89-11.5 11.1-13-0 121-142 4-dap 4.00 4.R8 5-95 6-86 8-11 9.12 10-1 11-2 12-7 13-8 3.74-425 .50-5.12 5.5663d 1-7.30 .55-B.54 6A&900 .37-1Q6 113-11.9 11.E-135 126r147 7-dap 4-63 5M 6.77 7-75 9-10 1QZ 11.3 12.4 14A 152 4.32,&95 15-�5-92 fi.30-7-M =41-30 A4-9.74 9A2-10.9 10.4-12.1 11.4-13.3 12.8-15.0 13-9-ifk3 10 5.28 629 TM 8-61 9,98 11-1 133 14-8 159 4.97-5-62 2-6 7.12 Ufi 07A-t4 .33-10.5 i�3-11-7 11-3-12.9 123-14-1 13Jfi-15.7 14-7-17J 20-d3y 7-11 8-Ai 9.97 112 12-9 I.12-1 14-2 15-5 16.1 11-6 20-0 I 5.57-7-58 A9-8-97 9.34-10jfi 10,5-11- =13.7 132-15.1 14.4-ifk5 iS5-17.9 17.1-19.9 fl&4-21A) am 10-A 122 13-5 15,3 19-6 1&0 19.3 21-1 225 y 6.34-9A2 9.82-11-t 11A-12.9 -7-t4.4 13 IL H,J 15Ap-17.7 16.E-1 1&0-2a�5 19�fi122E _ f26.&.2&1 11-2 13-1 15.1 16.6 1" 20-6 21-A 22-1 24-6 26-0 y 10.E-11.9 12.4-13. 142-150 11 17. 17A-19�E 183-21.1 0.122 21.3242 23 .2 ! j242-27.7 13.4 15 7 1-1-8 19.5 21-G 23-2 24-7 262 21.1 25-6 12.7-142Y f14.9-16.5 F6}-18-8 18.4-20. 0A-2_8 21.9-2d.4 3.3-26.1 24-5r27-7 26.4-29.E -731A 1 Pr9NR=cn teeja-: • e: -. � '9Is tatAe are based on frequency anaysle arpartial dmilon series [Pd3� Nrrnters :n parmtl_a a o-e =_ : _: = a : a-� o:rsr a-d uppeFbornds oT the 90% canlldenoe Wtereal. The prob3tClty that pre*Itatim frequency EVInnates i.ror r agiven durationand average t:. -_ :e :_- , ' be greater dean ire upper board {or less than me b1«eF board}is 5%. Estimaleaat uppertaurds are not Mecked agalnsi probable rat .. .-a:. :.:: : FMP} esti hates and may be higher liar orrrerNy valld aMP VAK%. Please reierta NOAA Atiaa 14 docu^ -,:':r more Irdormatlon. 12 Appendix 2 Drainage Basin Maps 13 Nolldla�ssa `oeLUow s�inade lvooav Web ddwa�dwvaa iNawdo�an3a-aad ®� c aecoc�as (L aw` w w w s S Of r� \Ar z - 4 r I I u } \ 0 U a u w rI y1 z / LU m r/ � O w � Q f � / i r ( 1 l � r /. 1 —> z ti d } 0 D U) � Z U_ � Z U_ Oj �w �w w� aQ w� aQ j U j U O? m co �n O a >Q5Q K W o 0 0 W �� O O I W d' aQ W d' aQ W m O U r r rn rn rn rn rn O U r r r Q > � LLI W d' a Q W d' a Q j U j U Q QO a rn rn m v o N r O a m N N m O > Q > Q Nolldla�ssa a© � H/Q,��% ddw 3odNidaa iN3wdo�3n3a-isod � `o C �w s3mna3e ivo�3v — ®c earn NI 1 11 aw` G s S $ _ I I lri_i of I co �� __ �� iOf Of O d 0 I i J° z m o� w %\eLO o I� 0w Jr CN 17 0 0 cncn U U O O > Q d' W m m m m m m m > Q d' W m m coo W a s W a s W J j U j U m Q � O a o o v N rn o m OS m N o W � w o 0 0 0 0 0 0 � w o 0 0 (� w� w� Q a Q a Q O U a O U Q 0 � � W W o 0 0 Z � � W m a m a d U U w O� O� O O O W Q a W 0 W Q W 0 Z K O Z a cn0w a a¢ o� a m O z OwZ cna O o m m Calculations & Hydraflow / Storm Sewer Output Underdrain Calculations where: D = Diameter of single pipe (inches) n = Roughness factor (recommended to I)e 0.011) = Internal slope (recommended to be 4.5%) Q = Underdrain design flow (cfs) Bioretention Cell #1 Q = Media Surface Area (ft2) * Media Infiltration Rate (f t1s) * Safety Factor in ft 1 hr = 0.00002315 s 3 Q = 1443 ft2 * 0.00002315 st * 10 = 0.334fs (0.334 f t3I * 0.011 D = 16 0 So s = 2.23 inches Table 1: Number of 4" Pipes Required in the Underdrain )f D is Less Than No- of 4'Pipes 5.13 2 &66 4 7.22 5 7.75 6 8 20 7 16 Bioretention Cell #2 Q = Media Surface Area (ft2) * Media Infiltration Rate (f t1s) * Safety Factor in ft 1 hr = 0.00002315 s 3 Q = 816 f tZ * 0.00002315 st * 10 = 0.189 f S (0.189 f t3I * 0.011 D = 16 0 So s = 1.80 inches Table 1: Number o€4"Pipes Required in the Und4erdrain WD Is Less Then No, of Pipes 5.13 5.95 a 6.66 4 7.22 5 7.75 6 8.20 ? Bioretention Cell #3 Q = Media Surface Area (ft2) * Media Infiltration Rate (f t1s) * Safety Factor in ft 1 hr = 0.00002315 s 3 Q = 1,649 f tZ * 0.00002315 st * 10 = 0.382 fs (0.382 f t3I * 0.011 D = 16 = 2.34 inches 0 So s 17 Table 1: Number o€4"Pipes Required in the Undi�rdrain If D is Less Than No, of Pipes 5.1 L 5.95 3 6.66 4 .22 5 7.75 b 8.20 7 Bioretention Cell #4 Q = Media Surface Area (ft2) * Media Infiltration Rate (f t1s) * Safety Factor in ft 1 hr = 0.00002315 s 3 Q = 610 ft2 * 0.00002315 st*10=0.141fs 3 (0.141ft )*0.011 D = 16 = 1.61 inches 0 So s Table 1: Number o€4"Pipes Required in the Und4erdraln If D is I ess Than No. of 4" Pipes 5.93 2 5.95 3 6.66 4 7.22 5 7.75 6 8.20 7 18 Bioretention Cell #5 Q = Media Surface Area (ft2) * Media Infiltration Rate (f t1s) * Safety Factor in ft 1 hr = 0.00002315 s 3 Q = 1,015 f tZ * 0.00002315 st * 10 = 0.235 f S (0.235 ft3I * 0.011 D = 16 0 So s = 1.95 inches Table 1: Number o€4"Pipes Required in the Und4erdrain WD Is Less Then No, of Pipes 5.13 5.95 a 6.66 4 7.22 5 7.75 6 8.20 ? Bioretention Cell #6 Q = Media Surface Area (ft2) * Media Infiltration Rate (f t1s) * Safety Factor in f t 1 hr = 0.00002315 s 3 Q = 1,921 f tZ * 0.00002315 st * 10 = 0.445 fs 3 (0.445 fs I * 0.011 D = 16 = 2.48 inches 0 So s 19 Table 1: Number of 4" Pipes Required in the Undi�rdrain If D is Less Than No, of Pipes 5.1 L 5.95 3 6.66 4 .22 5 7.75 6 8.20 Bioretention Cell #7 Q = Media Surface Area (ft2) * Media Infiltration Rate (f t1s) * Safety Factor in f t 1 hr = 0.00002315 s 3 Q = 2,222 f tZ * 0.00002315 st * 10 = 0.514 f S 3 (0.514fs I*0.011 D = 16 0 So s = 2.62 inches Table 1: Number of 4" Pipes Required in the Underdrain y No, of Pipes .} 2 5.95 3 6.66 4 7.22 5 7.75 6 8.20 7 20 Runoff Volume Match Calculations Discrete NRCS Curare Number Method for Runoff Depth _ 1000 - 1 CN Where: S = Maximum retention after rainfall begins (in) N = Curve number (unitless) ZZ (P—O.S)2 (P + 0. S) Where: Q' = Runoff depth (in) P = Rainfall depth (in) 21 FT. BRAGG SOF ADDITION BIORETENTION CELLS VOLUME (FT3) (NRCS) ImperviousCN Retention Depth (in) = 1 BASIN Area (sf) Area (ac) S = 0.20 1" Q (in) = 0.79 1 24829 0.57 98 1" Q Volume Required (ft3) = 1636 Retention Volume Provided (ft3) = 1752 S = 0.20 1" Post Q (in) = 0.79 2 13504 0.31 98 1" Post Q Volume (ft3) = 890 Retention Volume Provided (ft3) = 950 S = 0.20 1" Post Q (in) = 0.79 3 29621 0.68 98 1" Post Q Volume (ft3) = 1952 Retention Volume Provided (ft3) = 1969 S = 0.20 1" Post Q (in) = 0.79 4 20909 0.48 98 1" Post Q Volume (ft3) = 1378 Retention Volume Provided (ft3) = 1616 S = 0.20 1" Post Q (in) = 0.79 5 18295 0.42 98 1" Post Q Volume (ft3) = 1206 Retention Volume Provided (ft3) = 1258 Spost = 0.20 1" Post Q (in) = 0.79 6 30056.4 0.69 98 1" Post Q Volume (ft3) = 1981 Retention Volume Provided (ft3) = 2246 S = 0.20 1" Post Q (in) = 0.79 7 39204 0.90 98 1" Post Q Volume (ft3) = 2584 Retention Volume Provided (ft3) = 2627