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NC0040797_Instream Assessment_19940114
NPDES DOCUMENT !MANNINO COVER SHEET NPDES Permit: NC0040797 Henry Fork WWTP Document Type: Permit Issuance Wasteload Allocation Authorization to Construct (AtC) Permit Modification Complete File - Historical Engineering Alternatives (EAA) Correspondence Owner Name Change _..._ ....._......e......,,,,....„ 47-164;tream Assessment (67135'\ ../ Speculative Limits Environmental Assessment (EA) Document Date: January 14, 1994 Thiss cicsic•uurrkexkt i prirrted. tart. retinue paper — ligrio•re airy cioirkterkt CM. the x• evrerase esidLe DIVISION OF ENVIRONMENTAL MANAGEMENT January 14, 1994 MEMORANDUM TO: Rex Gleason THROUGH: Ruth Swanek a Carla Sanderson FROM: Jason C. Doll SUBJECT: Instream Assessment City of Hickory, Henry Fork WWTP NPDES No. NC0040797 Catawba County EMC WQ -93-024 Summary and Recommendations: The Technical Support Branch has completed the instream assessment for the City of Hickory, Henry Fork WWTP. The City is requesting an increase in domestic flow of 0.28 MGD and relaxed BOD5, TSS and Chronic Toxicity limits. With the addition of 0.28 MGD flow to the average yearly flow of 3.6235 MGD, the plant will reach a flow of 3.9035 MGD, which is below its current design capacity (6.0 MGD). The Mooresville Regional Office has recommended a BOD5 limit of 45 mg/1 and a TSS limit of 45 mg/l. Aquatic Toxicology has recommended a quarterly Full Range Chronic Toxicity Test (Ceriodaphnia) at effluent dilutions of 13%, 19.5%, 26%, 39% and 52%. A Level-B analysis was performed to assess the impact of the additional flow and relaxed BOD5 limit. The modeling analysis for this assessment indicates that the additional waste flow under the proposed interim limits will not cause a violation of the EMC 67 (b) criteria (not causing a DO sag of greater than 0.5 mg/I and not extending the DO sag length greater than 0.5 miles). The currently requested flow increase and limits did not cause a violation of the 5.0 mg/I instream DO standard, but did lower DO to 5.02 mg/1 (TABLE 1). Any additional flow increases would be likely to cause violations of the standard. Technical Support concurs with the recommendations of Aquatic Toxicology and the MRO with regard to flow and limits. All other limits during the SOC should remain the same as required in the permit issued December 1, 1993. The existing permit requires the facility to conduct instream monitoring for Temperature, DO, Fecal Coliform, Conductivity and Color. Their permit requires two downstream monitoring sites at State Road #1143 in the Henry Fork River and at Highway 10 in the South Fork Catawba River. The instream data should be tracked closely during the SOC period in order to confirm the results of the modeling analysis. The lowest point in the DO sag actually occurs between the two downstream sites at the mouth of the Henry fork River. 4 Background Information: The City of Hickory, Henry Fork WWTP discharges into the Henry Fork River, a class C stream, which flows to the South Catawba River in Catawba County directly south of Hickory. The river drains approximately 102 square miles at the discharge site. Using the hydrologic regional equations developed by the USGS and a weighted average with an upstream flow gage site the following flows were calculated at the discharge site: summer 7Q10 = 26.4 cfs, winter 7Q10 = 38.5 cfs, and average flow = 122.4 cfs. The creek is slow moving with a stream bed gradient of about 3-4 feet per mile. The Henry Fork WWTP was originally permitted in 1978, but since 1988 has had consistent and ongoing compliance problems. Civil penalties have been assessed against the facility twice in 1993 for repeated prior violations of permit limits. The plant has had problems meeting BOD5 limits due to the routine mechanical failure of several RBC units and problems meeting TSS limits because the contract hauler has been unable to remove sufficient sludge volumes from the plant, where storage capacity is inadequate to meet needs during longer durations of inclement weather. The problems with effluent toxicity have been attributed to high TRC levels caused by the lack of sufficient holding time in the poorly designed chlorine contact basin and an inability to pace chlorination / dechlorination activities with flow. On December 1, 1993 the City received a permit modification allowing them to increase the design flow at Henry Fork from 6.0 to 9.0 MGD and convert to an activated sludge system, but to date they have no Authorization to Construct in house for the upgrades and expansion. The pending upgrade to an activated sludge facility with a new chlorine contact basin should alleviate most or all of the compliance problems. Analysis and Discussion: An instream assessment was performed using the Level B framework. A comparison was made using the monthly average flow for the past year (3.6235 MGD) and the monthly average flow for the past year plus the requested increase in domestic flow (3.9035 MGD). Both model runs were performed with the requested BOD5 limit of 45 mg/1. Ammonia was modeled with values at the permitted limit of 9.0 mg/l. The BOD5 and NH3-N parameters were input to the model as CBOD and NBOD using multipliers of 2.0 for BOD5 and 4.5 for NH3-N. The DO in the pre-SOC flow model was 0.1 to 0.14 mg/1 higher than in the model run with the additional flow requested (TABLE 1). cc: Kent Wiggins John Leslie - MR0 Central Files 4 TABLE 1. Instream Assessment Summary for the Henry Fork WWTP. Waste flow Assumptions Design Capacity Pre-SOC (12/92 - 11/93) SOC Flow Requested Pre-SOC + SOC Flow Model Input Summary Headwater conditions: 6.0000 MGD 3.6235 MGD 0.2800 MGD 3.9035 MGD 7Q10 26.4 cfs Qavg 122.4 cfs Design Temperature 25.0 °C CBOD 2.0 mg/1 NBOD 1.0 mg/1 DO 7.44 mg/I Wastewater Inputs: 1st Waste flow 2nd Waste flow CBOD (2.0*BOD5) NBOD (4.5*N1I3-N) Model Output Summary 3.6235 MGD 3.9035 MGD 90.0 mg/1 40.5 mg/I Qw DO Net Distance Net (MGD) Min. Change <5.0 mg/1 Change (mg/1) (mg/1) (m1) (m1) 3.6235 5.16 NA NA NA 3.9035 5.02 0.14 NA NA 4 jay6 ifb,Wern croel b coo,- cicy) 'ram_ tricurAbt.LL 10 do 44u2_ tte,_Torta.51 efc, have_ r ereived ece14119 Li4.01._ Ma) 1)..tni- 3DC,U your ba6n eine I region 4-0 ZN20 fact 1,4, Eubrnatid appli cab on . Cif cleoiqn F loco, do c,urtrekti- pcv pvo fed- ? Uilc42 roct9 upahni- fb discus5 co(i2t inc.Q_ L,SOunCtA Chi YnCisi hal C_ hp go 441 vouSh p(ac‘COC1Ld- CAPKGA5 ht-c- &Lb.' latch lb vi ru frwc62/Y) FUT14 Cosiat‘IGK ptiy, Pc,L,ESS6A1770-1— C__p\A—ft-AL. cif-2) LE- LG5 6-Y) en(d4A-C:i REQUEST FORM FOR INSTREAM ASSESSMENT FOR 67b SOC NAME OF FACILITY: Hickory Henry Fork WWTP COUNTY: Catawba REGION: MR0 RECEIVING STREAM: Henry Fork River BACKGROUND DATA: A. Why is SOC needed? DESIGN FL W: 6.0 MGD SUBBAS1 N: 03-08-35 1 0 The facility has failed to meet NPDES Permit lipitations for TSS, BOD, and Toxicity. TSS violations are relatedlto poor design of the secondary clarifiers and chorine contact chamber. BOD violations have been shown to be related to repeated mechanical failure of a significant number of RBC units. Toxicity is most likely occurring because of excessive TRC concentrations. High TRC concentrations are maintained because of insufficient detention time in the chlorine contact chamber. B. History of SOC requests: No SOCs have been requested for the facility. 1. Monthly average waste flow prior to any SOC: 3.6235 MGD Time period averaged: 92/12 - 93/11 2. Previously approved SOC's-: N/A 3. Flows lost from plant (facilities that have gone off line): N/A 4. Current SOC Flow request: 280,000 gpd 5. Total plant flow post-SOC (sum of original flow and SOC flow minus losses): 3.9035 MGD 6. Is this an accurate flow balance for plant? Yes Hickory Henry Fork WWTP Instream Assessment Page 2 CURRENT SOC REQUEST: A. Request is for domestic or industrial waste? If it is a combination, please specify percentages. Domestic B. What type of industry? NA C. The region proposes the following SOC limits: BOD 45 mg/1 monthly average 60 mg/1 weekly average TSS 45 mg/1 monthly average 60 mg/1 weekly average Full Range Chronic Toxicity Test at dilutions of 13%, 19.5%, 26%, 39%, and 52%. D. What is the basis for these limits? Review of self -monitoring reports and interim limit suggestions from HDR Engineering of North Carolina, Inc., the City's consulting engineer. SUMMER MODEL RESULTS Discharger : HICKORY - HENRY FORK WWTP Receiving Stream : HENRY FORK RIVER The End D.O. is 5.80 mg/1. The End CBOD is 7.97 mg/1. The End NBOD is 3.08 mg/1. WLA WLA WLA DO Min CBOD NBOD DO Waste Flo (mg/1) Milepoint Reach # (mg/1) (mg/1) (mg/1) Ong(11 Segment 1 5.70 2.60 3 Reach 1 90.00 40.50 5.00 3.62350 Reach 2 0.00 0.00 0.00 0.00000 Reach 3 0.00 0.00 0.00 0.00000 Segment 2 7.19 0.00 1 Reach 1 31.50 72.00 5.00 0.00750 Segment 3 5.16 1.40 2 Reach 1 0.00 0.00 0.00 0.00000 Reach 2 0.00 0.00 0.00 0.00000 Reach 3 0.00 0.00 0.00 0.00000 SUMMER I Seg # 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 2 2 2 2 2 2 2 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 I Reach # I Seg Mi I D.O. 1 0.00 7.01 1 0.10 6.93 1 0.20 6.86 1 0.30 6.78 1 0.40 6.71 1 0.50 6.64 1 0.60 6.57 1 0.70 6.51 1 0.80 6.44 1 0.90 6.38 1 1.00 6.32 1 1.10 6.27 1 1.20 6.21 1 1.30 6.16 2 1.30 6.19 2 1.35 6.17 2 1.40 6.15 2 1.45 6.12 2 1.50 6.10 3 1.50 6.11 3 1.60 6.07 3 1.70 6.03 3 1.80 5.98 3 1.90 5.94 3 2.00 5.91 3 2.10 5.87 3 2.20 5.83 3 2.30 5.80 3 2.40 5.76 3 2.50 5.73 3 2.60 5.70 1 0.00 7.19 1 0.05 7.25 1 0.10 7.32 1 0.15 7.37 1 0.20 7.42 1 0.25 7.47 1 0.30 7.51 1 0.35 7.55 1 0.00 5.71 1 0.10 5.66 1 0.20 5.61 1 0.30 5.56 1 0.40 5.52 1 0.50 5.47 1 0.60 5.43 1 0.70 5.39 1 0.80 5.35 1 0.90 5.31 1 1.00 5.27 2 1.00 5.30 2 1.05 5.28 2 1.10 5.26 2 1.15 5.24 2 1.20 5.22 2 1.25 . 5.21 I CBOD 17.44 17.36 17.29 17.22 17.15 17.08 17.00 16.93 16.86 16.79 16.72 16.65 16.58 16.51 16.12 16.09 16.05 16.02 15.99 15.82 15.75 15.69 15.63 15.56 15.50 15.43 15.37 15.31 15.24 15.18 15.12 5.07 4.82 4.59 4.38 4.20 4.03 3.87 3.73 15.07 15.00 14.94 14.87 14.81 14.75 14.68 14.62 14.56 14.49 14.43 14.29 14.26 14.23 14.20 14.17 14.14 I NBOD 7.93 7.88 7.83 7.78 7.74 7.69 7.64 7.59 7.55 7.50 7.45 7.41 7.36 7.32 7.15 7.12 7.10 7.08 7.06 6.99 6.95 6.90 6.86 6.82 6.78 6.74 6.70 6.66 6.62 6.57 6.54 8.39 7.77 7.22 6.73 6.29 5.90 5.54 5.22 6.53 6.49 6.44 6.40 6.36 6.32 6.28 6.24 6.20 6.16 6.12 6.06 6.04 6.02 6.00 5.98 5.96 I Flow I 32.02 32.03 32.05 32.06 32.08 32.09 32.11 32.12 32.14 32.15 32.17 32.18 32.20 32.21 33.11 33.12 33.13 33.13 33.14 33.54 33.56 33.57 33.59 33.60 33.62 33.63 33.65 33.66 33.68 33.69 33.71 0.11 0.12 0.13 0.13 0.14 0.15 0.15 0.16 33.87 33.88 33.90 33.91 33.93 33.94 33.96 33.97 33.99 34.00 34.02 34.42 34.42 34.43 34.44 34.45 34.45 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 I Seg # 2 1.30 5.19 14.11 5.94 34.46 2 1.35 5.17 14.08 5.92 34.47 2 1.40 5.16 14.05 5.90 34.48 3 1.40 5.96 9.81 4.18 53.18 3 1.60 5.94 9.73 4.13 53.28 3 1.80 5.91 9.65 4.08 53.38 3 2.00 5.89 9.57 4.03 53.48 3 2.20 5.88 9.49 3.98 53.58 3 2.40 5.86 9.41 3.93 53.68 3 2.60 5.85 9.33 3.88 53.78 3 2.80 5.83 9.25 3.83 53.88 3 3.00 5.82 9.18 3.79 53.98 3 3.20 5.81 9.10 3.74 54.08 3 3.40 5.80 9.02 3.69 54.18 3 3.60 5.80 8.95 3.65 54.28 3 3.80 5.79 8.88 3.60 54.38 3 4.00 5.78 8.80 3.56 54.48 3 4.20 5.78 8.73 3.52 54.58 3 4.40 5.78 8.66 3.47 54.68 3 4.60 5.78 8.59 3.43 54.78 3 4.80 5.78 8.52 3.39 54.88 3 5.00 5.78 8.45 3.35 54.98 3 5.20 5.78 8.38 3.31 55.08 3 5.40 5.78 8.31 3.27 55.18 3 5.60 5.78 8.24 3.23 55.28 3 5.80 5.79 8.17 3.19 55.38 3 6.00 5.79 8.10 3.15 55.48 3 6.20 5.80 8.04 3.11 55.58 3 6.40 5.80 7.97 3.08 55.68 Reach # I Seg Mi I D.O. I CBOD I NBOD I Flow I *** MODEL SUMMARY DATA *** Discharger : HICKORY - HENRY FORK WWTP Subbasin : 0308 Receiving Stream : HENRY FORK RIVER Stream Class: C. Summer 7Q10 : 26.4 Winter 7Q10 : 38.5 Design Temperature: 25.0 ILENGTHI SLOPE' VELOCITY 1 DEPTH' Kd I Kd I Ka 1 Ka I KN I KN I KNR I KNR I SOD I SOD mile I ft/mil fps 1 ft ldesignl @20 ldesignl 20 'design' @20 'design' @20 'design' @20 1 1 1 1 1 1 1 1 Segment 1 1 1.301 4.101 0.468 1 2.14 1 0.29 1 0.23 1 1.88 1 1.691 0.44 1 0.30 1 0.44 1 0.00 1 0.00 1 0.00 Reachil 1 1 1 1 1 1 1 1 1 1 1 1 I 1 1 1 Segment 1 1 0.201 4.101 0.470 1 2.17 1 0.29 1 0.23 1 1.89 1 1.701 0.44 I 0.30 I 0.44 1 0.00 1 0.00 1 0.00 Reach2l 1 1 1 I 1 l 1 1 1 1 1 1 1 1 1 1 Segment 1 1 1.101 4.101 0.472 1 2.18 1 0.29 1 0.23 1 1.90 1 1.701 0.44 1 0.30 I 0.44 1 0.00 1 0.00 I 0.00 Reach3I 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Segment 2 1 0.351 50.001 0.094 1 0.31 1 0.48 1 0.38 1 9.46 1 8.491 0.73 1 0.50 1 0.73 1 0.00 1 0.00 1 0.00 Reachil 1 I l 1 1 1 1 1 1 1 I 1 1 1 1 Segment 3 1 1.001 3.101 0.437 1 2.28 1 0.28 1 0.22 1 1.33 1 1.191 0.44 10.30 1 0.44 1 0.00 I 0.00 1 0.00 Reachll 1 1 I 1 1 1 1 1 1 1 1 l 1 1 1 1 Segment 3 I 0.401 3.101 0.438 1 2.29 1 0.28 1 0.22 I 1.33 1 1.191 0.44 1 0.30 1 0.44 I 0.00 1 0.00 1 0.00 Reach2l 1 1 1 1 1 1 l 1 Segment Reach 11 1 1 1 5'.001 3.101 0.494 1 2.71 1 0.28 1 0.22 1 1.50 I 1.351 0.44 I 0.30 1 0.44 1 0.00 1 0.00 I 0.00 1 11 1 1 1 Flow 1 CBOD l NBOD 1 D.O. I cfs 1 mg/1 1 mg/1 1 mg/1 I Segment 1 Reach 1 Waste 1 5.616 1 90.00.0 1 40.500 1 5.000 Headwatersl 26.400 1 2.000 1 1.000 1 7.440 Tributary 1 0.000 l 2.000 1 1.000 1 7.440 * Runoff 1 0.150 I 2.000 1 1.000 1 7.440 Segment 1 Reach 2 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Tributary I 0.900 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 1 Reach 3 Waste I 0.000 1 0.000 1 0.000 1 0.000 Tributary 1 0.400 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 2 Reach 1 Waste 1 0.012 1 31.500 1 72.000 1 5.000 Headwatersl 0.100 1 2.000 1 1.000 1 7.440 Tributary 1 0.000 1 2.000 1 1.000 1 7.440 * Runoff 1 0.140 1 2.000 1 1.000 1 7.440 Segment 3 Reach 1 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Headwatersl 28.600 1 2.000 1 1.000 1 7.440 Tributary 1 0.000 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 3 Reach 2 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Tributary 1 0.400 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 3 Reach 3 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Tributary 1 18.700 1 2.000 1 1.000 1 7.440 * Runoff 1 0.500 1 2.000 1 1.000 1 7.440 * Runoff flow is in cfs/mile SUMMER MODEL RESULTS Discharger : HICKORY - HENRY FORK WWTP Receiving Stream : HENRY FORK RIVER The End D.O. is 5.69 mg/1. The End CBOD is 8.43 mg/1. The End NBOD is 3.25 mg/1. WLA WLA WLA DO Min CBOD NBOD DO Waste Flo (mg/1) Milepoint Reach # (mg/1) (mg/1) (mg/1) (LIO) Segment 1 5.60 2.60 3 Reach 1 90.00 40.50 5.00 3.90350 Reach 2 0.00 0.00 0.00 0.00000 Reach 3 0.00 0.00 0.00 0.00000 Segment 2 7.19 0.00 1 Reach 1 31.50 72.00 5.00 0.00750 Segment 3 5.02 1.40 2 Reach 1 0.00 0.00 0.00 0.00000 Reach 2 0.00 0.00 0.00 0.00000 Reach 3 0.00 0.00 0.00 0.00000 SUMMER I Seg # I Reach # I Seg Mi I D.O. I CBOD I NBOD I Flow I 1 1 0.00 6.99 18.41 8.36 32.45 1 1 0.10 6.90 18.33 8.31 32.47 1 1 0.20 6.82 18.26 8.26 32.48 1 1 0.30 6.74 18.18 8.21 32.50 1 1 0.40 6.67 18.10 8.16 32.51 1 1 0.50 6.59 18.03 8.11 32.53 1 1 0.60 6.52 17.96 8.06 32.54 1 1 0.70 6.45 17.88 8.01 32.56 1 1 0.80 6.39 17.81 7.97 32.57 1 1 0.90 6.32 17.73 7.92 32.59 1 1 1.00 6.26 17.66 7.87 32.60 1 1 1.10 6.20 17.59 7.82 32.62 1 1 1.20 6.14 17.51 7.77 32.63 1 1 1.30 6.09 17.44 7.73 32.65 1 2 1.30 6.12 17.03 7.55 33.55 1 2 1.35 6.10 16.99 7.52 33.55 1 2 1.40 6.07 16.96 7.50 33.56 1 2 1.45 6.04 16.92 7.48 33.57 1 2 1.50 6.02 16.89 7.46 33.58 1 3 1.50 6.04 16.71 7.38 33.98 1 3 1.60 5.99 16.64 7.33 33.99 1 3 1.70 5.94 16.58 7.29 34.01 1 3 1.80 5.90 16.51 7.25 34.02 1 3 1.90 5.86 16.44 7.20 34.04 1 3 2.00 5.82 16.37 7.16 34.05 1 3 2.10 5.78 16.31 7.12 34.07 1 3 2.20 5.74 16.24 7.07 34.08 1 3 2.30 5.70 16.18 7.03 34.10 1 3 2.40 5.67 16.11 6.99 34.11 1 3 2.50 5.63 16.04 6.95 34.13 1 3 2.60 5.60 15.98 6.91 34.14 2 1 0.00 7.19 5.07 8.39 0.11 2 1 0.05 7.25 4.82 7.77 0.12 2 1 0.10 7.32 4.59 7.22 0.13 2 1 0.15 7.37 4.38 6.73 0.13 2 1 0.20 7.42 4.20 6.29 0.14 2 1 0.25 7.47 4.03 5.90 0.15 2 1 0.30 .7.51 3.87 5.54 0.15 2 1 0.35 7.55 3.73 5.22 0.16 3 1 0.00 5.61 15.92 6.90 34.30 3 1 0.10 5.56 15.85 6.85 34.32 3 1 0.20 5.50 15.79 6.81 34.33 3 1 0.30 5.45 15.72 6.76 34.35 3 1 0.40 5.41 15.65 6.72 34.36 3 1 0.50 5.36 15.59 6.68 34.38 3 1 0.60 5.31 15.52 6.63 34.39 3 1 0.70 5.27 15.45 6.59 34.41 3 1 0.80 5.23 15.39 6.55 34.42 3 1 0.90 5.18 15.32 6.51 34.44 3 1 1.00 5.14 15.26 6.46 34.45 3 2 1.00 5.17 15.11 6.40 34.85 3 2 1.05 5.15 15.07 6.38 34.86 3 2 1.10 5.13 15.04 6.36 34.87 3 2 1.15 5.11 15.01 6.34 34.87 3 2 1.20 5.10 14.98 6.32 34.88 3 2 1.25 5.08 14.95 6.30 34.89 3 2 1.30 5.06 14.92 6.28 34.90 3 2 1.35 5.04 14.88 6.26 34.90 3 2 1.40 5.02 14.85 6.24 34.91 3 3 1.40 5.87 10.37 4.41 53.61 3 3 1.60 5.84 10.28 4.36 53.71 3 3 1.80 5.82 10.20 4.30 53.81 3 3 2.00 5.80 10.11 4.25 53.91 3 3 2.20 5.78 10.03 4.20 54.01 3 3 2.40 5.76 9.95 4.15 54.11 3 3 2.60 5.74 9.86 4.10 54.21 3 3 2.80 5.73 9.78 4.05 54.31 3 3 3.00 5.72 9.70 4.00 54.41 3 3 3.20 5.70 9.62 3.95 54.51 3 3 3.40 5.69 9.54 3.90 54.61 3 3 3.60 5.69 9.46 3.86 54.71 3 3 3.80 5.68 9.39 3.81 54.81 3 3 4.00 5.67 9.31 3.76 54.91 3 3 4.20 5.67 9.23 3.72 55.01 3 3 4.40 5.67 9.16 3.67 55.11 3 3 4.60 5.66 9.08 3.63 55.21 3 3 4.80 5.66 9.01 3.58 55.31 3 3 5.00 5.66 8.93 3.54 55.41 3 3 5.20 5.66 8.86 3.50 55.51 3 3 5.40 5.66 8.79 3.46 55.61 3 3 5.60 5.67 8.71 3.41 55.71 3 3 5.80 5.67 8.64 3.37 55.81 3 3 6.00 5.67 8.57 3.33 55.91 3 3 6.20 5.68 8.50 3.29 56.01 3 3 6.40 5.69 8.43 3.25 56.11 I Seg # I Reach # I Seg Mi I D.O. I CBOD I NBOD I Flow I *** MODEL SUMMARY DATA *** Discharger : HICKORY - HENRY FORK WWTP Subbasin : 0308 Receiving Stream : HENRY FORK RIVER Stream Class: C Summer 7Q10 : 26.4 Winter 7Q10 : 38.5 Design Temperature: 25.0 'LENGTH' SLOPE' VELOCITY 1 DEPTH' Kd 1 Kd 1 Ka I Ka I KN I KN I KNR I KNR 1 SOD 1 SOD mile 1 ft/mil fps 1 ft Idesignl @20 'design' @20 'design' @20 'design' @20 'design' @20 1 Segment 1 1 1.301 4.101 0.472 1 2.14 1 0.29 1 0.23 1 1.90 1 1.701 0.44 1 0.30 I 0.44 1 0.00 I 0.00 1 0.00 Reach 1 1 Segment 1 I 0.201 4.101 0.475 1 2.17 1 0.29 1 0.23 I 1.91 I 1.711 0.44 I 0.30 1 0.44 1 0.00 1 0.00 1 0.00 Reach 2 Segment 1 1 1.101 4.101 0.477 1 2.18 1 0.29 1 0.23 1 1.92 1 1.72' 0.44 1 0.30 1 0.44 1 0.00 1 0.00 I 0.00 Reach 3 Segment 2 1 0.351 50.00' 0.094 1 0.31 1 0.48 1 0.38 1 9.46 1 8.491 0.73 1 0.50 1 0.73 1 0.00 1 0.00 1 0.00 Reach 1 1 Segment 3 1 1.001 3.101 0.441 2.28 0.28 0.22 1.34 1.201 0.44 0.30 0.44 0.00 10.0010.00 Reachil 1 1 1 1 1 1 1 1 1.1 1 1 Segment 3 1 0.401 3.10' 0.442 1 2.29 1 0.28 1 0.22 1 1.34 1 1.211 0.44 1 0.30 1 0.44 1 0.00 1 0.00 1 0.00 Reach2l 1 1 1 1 1 1 1 1 Segment 3 1 5.001 3.101 0.497 2.71 0.28 0.22 1.51 1.351 0.44 0.30 0.44 0.00 0.00 0.00 Reach3l 1 1 1 1 1 1 1 1 Flow 1 CBOD 1 NBOD 1 D.O. I cfs 1 mg/1 1 mg/1 1 mg/1 I Segment 1 Reach 1 Waste 1 6.050 1 90.000 1 40.500 1 5.000 Headwatersl 26.400 1 2.000 1 1.000 1 7.440 Tributary 1 0.000 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 1 Reach 2 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Tributary 1 0.900 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 1 Reach 3 Waste I 0.000 1 0.000 1 0.000 1 0.000 Tributary I 0.400 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 2 Reach 1 Waste 1 0.012 1 31.500 72.000 1 5.000 Headwatersl 0.100 1 2.000 1 1.000 1 7.440 Tributary 1 0.000 1 2.000 1 1.000 1 7.440 * Runoff 1 0.140 1 2.000 1 1.000 1 7.440 Segment 3 Reach 1 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Headwatersl 28.600 1 2.000 1 1.000 1 7.440 Tributary 1 0.000 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 3 Reach 2 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Tributary 1 0.400 1 2.000 1 1.000 1 7.440 * Runoff 1 0.150 1 2.000 1 1.000 1 7.440 Segment 3 Reach 3 Waste 1 0.000 1 0.000 1 0.000 1 0.000 Tributary 1 18.700 1 2.000 1 1.000 1 7.440 * Runoff 1 0.500 1 2.000 1 1.000 1 7.440 * Runoff flow is in cfs/mile = cp-,s/yyl z Ptinfy KriC 7CM> So 0A-110,5 czA O./A, /0 = qt,3 M 46/"C4V) ern 17 bA= i4q, GM= cy6.0 rfij 014ff - -7&()=-- 11. 7 -7Q1Ctol ;4-7 7 Re/Hy ro* 0115 _Q 003: 3."--4• —17 OR - 1C)2-?viji \ QA z 12,2 • -1 7alo yet Ofi= 10•;- -7c2106 • -24,7 31.c, tx„c„4), 011-7 111.7 Q14 41c1 4.7 -76,0.0- (41,7 R0064) r o,13 po(70,I0) = 5, i26 (70_ 100) z 0,A0 11 Grchk*at ‘6, 0.00-76 "riga • -; 0.54 nir2 fos WI,: 045 so,o 5: /;- 010„; tA 0.1471"T -' QA 2 -70)0„ 0,7 MODEL INPUTS FOR LEVEL B ANALYSIS GENERAL INFORMATION Facility Name: i-lickory - Oa) ty 1.-9rk LAIA-)TP NPDES No.: A)G00 10-7q7 i Type of Waste: Vo ,i) a trl e-5 tic / 33 A _2-4 dik-str-\14( Facility Status: .8k / 0 !bil /5.0C Receiving Stream: H e,r1 ry"-i '.)4 ki)e-t- Stream Classification: C I Subbasin: 03-of- ,35 County:LOsiO‘k, Regional Office: M oor c-;5 1,) tile- Topo Quad: FLOW INFORMATION USGS 4/ tloqi -e, ,e.,,,,-rt 11-0 -&D I Date of Flow Estimates: eic) / eol s)d.i-srs-71. s• Drainage Area (mi2): / . 0 Summer 7Q10 (cfs): 2.(sss ti Winter 7Q10 (cfs): 31. 6 Average Flow (cfs): /.207. 30Q2 (cfs): IWC at Point of Discharge (%): Cummulative IWC (%): :.'''...iAiftfv.::'.. ..,-.4:,::',:mii•::::M.We'....::e: .: ....:A‘liviiN. .••••,0•,,, • ... :f.::•.....Ai:v..g.,,.:- .. . ....: MODEL INPUT INFORMATION LENGTH OF REACH (miles) / . 3 At ; C5 . P-. / s / INCREMENTAL LENGTH (miles) . 0, 1 b . 05 6 . I WASTE CHARACTERISTICS FLOW (MGD) .5oc, 3, 6.235 CBOD (mg/1) NBOD (mg/1) /0. 5. D.O. (mg/1) .5-. 0 RUNOFF CHARACTERISTICS 7Q10 (cfs/tni2) z,.,vrt m e--1 Os l' O. IS QA (cfs/nn12) 0.-73 0,73 0 .73 CBOD (mg/1) 01. Of) ..2.0.0 2.06 NBOD (mg/1) / • °O /. 4> 0 l• 00 D.O. (mg/1) de.Pa ,t /4 elJa.4.1.4 id-rvi,,,4 H- TRIBUTARY CHARACTERISTICS 7Q10 (cfs) 0.9 O. q QA (cfs) CBOD (mg/1) a .15 0 NBOD (mg/1) /. 00 /. 00 D.O. (mg/1) 04...,Fexa hi- 44..Fas.4 SLOPE (fpm) qs I 14. I , (.4 / Name of facii;%' MODEL INPUTS FOR LEVEL B ANALYSIS GENERAL INFORMATION Facility Name: NPDES No.: Type of Waste: Facility Status: Receiving Stream: Stream Classification: Subbasin: County: Regional Office: Topo Quad: FLOW INFORMATION USGS # Date of Flow Estimates: Drainage Area (mi2): b .(i 111. g, Summer 7Q10 (cfs): 0 ,10 ...)g. 6, Winter 7Q10 (cfs): 0 , 1 67 qi . s Average Flow (cfs): D. l'S iS3 30Q2 (cfs): IWC at Point of Discharge (%): Cummulative IWC (%): : 'N.QAPAT:0:406.4:ARV"':.,:44::....0K4NOSINEMgr".24XSINtaintalit:..Agnaggli0 MODEL INPUT INFORMATION .2.1q1 5g e _t-R LENGTH OF REACH (miles) 0.35 I- 0 INCREMENTAL LENGTH (miles) 0. 05 Oi l 0.06 WASTE CHARACTERISTICS FLOW (MGD) 0.0075 CBOD (mg/1) 31, NBOD (mg/1) D.O. (mg/1) 5. 0 RUNOFF CHARACTERISTICS 7Q10 (cfs/mi2) 0, / LI 6, 1- O. / QA (cfs/rni2) pL/L/ 0 i 73 0 .73 CBOD (mg/1) €2 . co ...2. DO , 0 b NBOD (mg/1) / . oo 1.00 1.00 D.O. (mg/1) Die---ra Lk* ple:koux if 0 I cPa L4 TRIBUTARY CHARACTERISTICS 7Q10 (cfs) 0. (/ QA (cfs) .2 • 1 CBOD (mg/1) . 00 NBOD (mg/1) .2 /. 00 D.O. (mg/1) ote A. tt / 4 SLOPE (fpm) 6043 s <3, / 3, i 1\16:rne of facility 0.5 _2.00 1, co cic-fo.LA H. Facility: Henry Fork NPDES#: NC0040797 Recieving Stream: Henry Fork River Hydrologic Area: Drainage Area Low Flow Patial Record Station: Qave Low Flow Patial Record Station: s7010 Low Row Patial Record Station: w7010 Low Flow Patial Record Station: 3002 Low Row Patial Record Station: Drainage Area New Site: MAR New Site: Qave per Report Equation: s7010 per Report Equation: w7010 per Report Equation: 3002 per Report Equation: Drainage Area Ratio: (new DA / Da at gage ] Weighted Ratio: HMO 83.20 miles squared 99.84 cfs 22.00 cfs 32.00 cfs 102.00 miles squared 1.20 cfs/miles squared 122.40 cfs 19.91 cfs 29.40 cfs 42.11 cfs 1.23:1 Continue 0.92 : 1 Drainage Area New Site: MAR New Site: Weighted Oave per Report Equation: Weighted s7010 per Report Equation: Weighted w7Q10 per Report Equation: Weighted 3002 per Report Equation: 102.00 miles squared 1.20 cfs/mIles squared 122.40 cfs 26.44 cfs 38A9 cfs USGS weighted low flow estimate procedure FacilityltIqEaf2rILI N P D ES # Et1.299.9D2 Streamitlepry Fk. Region DA_LFPR s7Q1O_LFPR DA_new MAR QA_eq STEP 1 [ HA1 0 •11=1.1•1=1.1.0•M••M•••••••110111i _ 83.2 22 2.2._ 122.40 sq mile cfs sq mile cfs/sq mile cfs calculate drainage area ratio NOTE: procedure applies for regions HA3, HA5, HA9, and HA10, else see flow SOP RATIO = new drainage area drainage area at gage IF 0.25 < RATIO < 4, CONTINUE to STEP 2, ELSE too far from gage OK, do STEP 2 now! STEP 2 determine weight of gage (weight_LFPR) A. RATIO < 1 B. RATIO > 1 weight ratio weight Mk 0 1 0 1 [ #VALUE! I see B I i 0.92 I 1.23 1 0.25 1 4 STEP 3 HA3 HA5 HA9 HA1 0 STEP 4 weight = 0.92 calculate 7010_EQ using regional equation 26.43 2.27 2.27 19.91 cfs cfs cfs cfs 7Q1O_EQ = calculate 7010 yield using weighted equation I 19.91 7Q1 Oyield = [weight_LFPR 7Q1O_LFPR] + [weight_EQ * 701 0_EQ] cfs DA_LFPR DA_new yield = 0.24 STEP 5 calculate s7Q10 7010 = 7Q10yield * DA_new summer 7010 = 26.44 cfs 1.22596154j 41.111MOOMOOM••••••=0•1=••=011 0.01 = 0.26 cfs/sq mile USGS weighted low flow estimate procedure Facility11:129.ty..E2t Region DA_LFPR w7010_LFPR DA_new MAR QA_eq STEP 1 I. HA10 •••••••••••M•21=•••••••••••.1114 83.2 32 102 1.2 122.40 NPDES # ENC0040797 I Stream Ilipary.fic..13.11 M•••••• M.1141•1••=.••=0.1M• sq mile cfs sq mile cfs/sq mile cfs calculate drainage area ratio NOTE: procedure applies for regions HA3, HA5, HA9, and HA10, else see flow SOP RATIO = new drainage area drainage area at gage IF 0.25 < RATIO < 4, CONTINUE to STEP 2, ELSE too far from gage OK, do STEP 2 now! STEP 2 determine weight of gage (weight_LFPR) A. RATIO < 1 B. RATIO > 1 weight 1.11.4 weight rag o 1 o 1 1 #VALUE! 1 see B I I 0.92 i 1.23 1 0.25 1 4 STEP 3 HA3 HA5 HA9 HA10 STEP 4 weight = 0.92 calculate 7Q10_EQ using regional equation 50.68 10.43, 10.43 29.40 cfs cfs cfs cfs 7010_E0 = calculate 7010 yield using weighted equation 29.40 cfs/sq mile 7Q10yield = [weight_LFPR * 7010_LFPR1 + [weight_E0 * 7010_E01 DA_LFPR DA_new yield = 0.36 0.02 STEP 5 calculate w7Q10 7010 = 7010yield * DA_new winter 7010 = 38.49 cfs 0.38 1.2259q1§A cfs/mile