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HomeMy WebLinkAboutNC0021491_wasteload allocation_19930429 NPDES DOCUMENT SCANNIN& COVER SHEET NPDES Permit: NCO021491 Document Type: Permit Issuance Wasteload Allocation Authorization to Construct (AtC) Permit Modification Engineering Alternatives Analysis Permit History Date Range: Correspondence Document Date: April 29, 1993 THIS DOCYNENT IS PRINTED ON REUSE PAPER - ISHORE ANY CONTENT ON THE REVERSE SIDE 4 .. NPDES WASTE LOAD ALLOCATION PERMIT NO.: NC0021491 Modeler Date Rec. # PERMITTEE NAME: Town of Mocksville '" „i ,al ;, FACILITY NAME: Dutchman's Creek WWTP Drainage Area (mil ) 1 gq Avg. Streamflow (cfs): Facility Status: Existing 7Q10 (cfs) 15 Winter 7Q10 (cfs) 30Q2 (cfs) Permit Status: Renewal Toxicity Limits: IWC % Acute/Chronic Major Minor Instream Monitoring: E/F Pipe No.: 001 Parameters Tfa4;? Arw2r, -V.O. GEtA cot con7ucr� Ty Design Capacity: 0.68 MGD Upstream a Location AT CfASr te)o Domestic (% of Flow): 77 %** Downstream N Location APPY. U• iut L-Es I own�5rnsan Industrial (% of Flow): 23 %** Effluent Summer Winter Comments: Characteristics **Industrial flow percentage based on permitted flow and reported SIU BOD5 (m ) 2-+ - 2-+ flows from application PIRF has been requested NH3-N (mg/1) 14 - t4 RECEIVING STREAM:DutchmanCreek D.O. (mg/1) rj 5 Class: C TSS (mg/1) 50 - 3 o Sub-Basin: 03-07-05 F. Col. /100 ml ( ) ?� Zvo Reference USGS Quad: D 16 NE (please attach) pH (SU) County: Davie - - Regional Office: Winston-Salem Regional Office " CAD-mI(AM 30 (yAiu4 4 4)( 30 Gi W ): 4,v N,;02 um Rey PreviousExp. Date: 2/28/93 Treatment Plant Class: II CsPvcn- (µ�L : xwNITaa moNrro2 Classification changes within three miles: " m-1" R nochanee D (µ}!L) M, ,VfTO(L Ab ITya- - �Alc Mod qo(� .µ ro2- _GyAuipE L �l• ?6 CoaI� Max) i6 TD 12_ .tiro iToQ- Requested by: Charles Lowe Date: 10/27/92 Prepared b P Y / �1 ido. _ Date: 4 =z 'S 7 Comments: Reviewed by: Date: i t' ,• d 1�Ir�� 'I i __ •-f nut Area Jid IP' _ t Tan., • a. .a / � r!_ � �_ / .- _ � � J ``. 74ntjho ♦ ., •.— . rr._. ,� � ` �- ,(-" sso ERN \\ �� � � r - -� �• ���Discys�.ee r •• em To er, l�� �l- r�� csus 2: M, $ll 32'30" $/2 - - — '43 • ., �.,,,. o.... •%a/,. .:w,.w,q ` e150p0'"E. 8 �SSUR" 16 M,. - - F�4f1 CI ASSIRCATION r "IVED N.C. [),e 3;. of E"s-1l R FACT SHEET FOR WASTELOAD ALLOCATION ' Request# 7175 �?,der Facility Name: Mocksville-Dutchmans Creek WWTP NPDES No.: NC0021491 Type of Waste: 77% dom/23% ind Facility Status: Existing Permit Status: Renewal Receiving Stream: Dutchmans Creek Stream Classification: C Subbasin: 030705 County: Davie Stream Characteristic: Regional Office: WSRO USGS # Requestor: C. Lowe Date: Date of Request: 10/27/92 Drainage Area(mi2): 108 Topo Quad: D16NE Summer 7Q10 (cfs): 15 Winter 7Q10(cfs): 26 Average Flow (cfs): 108 30Q2 (cfs): IWC (%): 6.55 Wasteload Allocation Summary (approach taken, correspondence with region, EPA, etc.) Mocksville is operating well below current limits. The facility has been passing its toxicity test for the past three years. Staff report indicates that the facility is well maintained, but has VI problems (although monthly average flow limit has not been violated). Instream data indicate lower D.O.'s in winter than summer (may be suspect). Facility will not receive NH3-N/tox choice due to existing stringent NH3-N limit and passing toxicity test results. Special Schedule Requirements and additional comments from Reviewers: Q£su6M I ITA t^ Recommendedby: Date: 3 t Reviewed by Instream Assessment: l C / -L( F Dater 1 r,A -Regional Supervisor: , . P__ Date: Permits &Engineering: �!� rrT � " — Date: C i APR 1993 RETURN TO TECHNICAL SERVICES BY: • 2. CONVENTIONAL PARAMETERS Existing Limits: Monthly Average Summer Winter Wasteflow (MGD): 0.68 0.68 BODS(mg/1): 24 24 NH3N(mg/1): 14 14 DO(mg/1): 5 5 TSS (mg/l): 30 30 Fecal Col. (/100 ml): 1000 1000 pH (SU): 6-9 6-9 Residual Chlorine(µg/1): Oil&Grease(mg/1): TP(mg/1): J TN(mg/1): Recommended Limits: Monthly Average Summer Winter WQ or EL Wasteflow (MGD): 0.68 0.68 BODS(mg/1): 24 24 NH3N(mg/1): 14 14 DO(mg/1): 5 5 TSS (mg/1): 30 30 Fecal Col. V100 ml): 200 200 pH (SU): 6-9 6-9 Residual Chlorine (µg/1): Oil&Grease (mg/1): TP(mg/1): TN(mg/1): Limits Changes Due To: Parameter(s) Affected Change in 7Q10 data Change in stream classification _ Relocation of discharge Change in wasteflow Other(onsite toxicity study,interaction,etc.) Instream data New regulations/standards/procedures Fecal coli New facility information (explanation of any modifications to past modeling analysis including new flows,rates,field data, interacting discharges) / (See page 4 for miscellaneous and special conditions,if applicable) 3 TOMCS/METALS Type of Toxicity Test: Chronic Quarterly Existing Limit: Chronic Qtrly P/F at 6.6% Recommended Limit: Chronic Qtrly P/F at 7% Monitoring Scheduler Apr, Jul, Oct, Jan ExistingLimits imits Daily Max. COD (mg/): Cadmium(ugh): monitor Chromium(ug/1): monitor Copper(ug/1): monitor Nickel(ugh): monitor Lead(ug/1): monitor Zinc(ug/1): Cyanide(ug/1): 76.2 Phenols (ug/1): Mercury(ug/1): Silver(ug/1): monitor Recommended Limits Daily Max. WQ or EL COD (mo: Cadmium(ug/1): 30 Chromium(ug/1): monitor Copper(ug/1): monitor Nickel(ug/1): monitor Lead(ug/1):' monitor Zinc(ug/1): monitor Cyanide(ug/1): 76 Phenols (ug/1): Mercury(ug/1): Silver(ug/1): monitor Limits Changes Due To: Parameter(s) Affected Change in 7Q10 data Change in stream classification Relocation of discharge Change in wasteflow New pretreatment information Cr,Cu,Ni,Pb,Zn,Ag Failing toxicity test Other(onsite toxicity study,interaction,etc.) effluent monitoring data, Cadmium _X Parameter(s) are water quality limited. For some parameters,the available load capacity of the immediate receiving water will be consumed. This may affect future water quality based effluent limitations for additional dischargers within this portion of the watershed. OR No parameters are water quality limited,but this discharge may affect future allocations. 4 INSTREAM MONITORING REQUIREMENTS Upstream Location: at least 100 It upstream Downstream Location: at appx. 0.5 miles downstream Parameters: temperature, D.O., Fecal coliform, conductivity Special instream monitoring locations or monitoring frequencies: MISCELLANEOUS INFORMATION &SPECIAL CONDITIONS AAd quacy of Existing Treatment Has the facility demonstrated the ability to meet the proposed new limits with existing treatment facilities? Yes ',-'No If no, which parameters cannot be met? Would a "phasing in" of the new limits be appropriate? Yes_ No G- If yes, please provide a schedule (and basis for that schedule) with the regional office recommendations: If no, why not? Special Instructions or Conditions Wasteload sent to EPA? (Major)CN�'u' (Y or N) (If yes, then attach schematic, toxics spreadsheet, copy of model,or, if not modeled, then old assumptions that were made, and description of how it fits into basinwide plan) Additional Information attached? —&�c (Y or N) If yes, explain with attachments. r r A - - Facility Name 11' nAA�ls Permit# N c'02zl -9 I Pipe# CHRONIC TOXICITY PASS/FAIL PERMIT LIMIT (QRTRLY) The effluent discharge shall at no time exhibit chronic toxicity using test procedures outlined in: 1.) The North Carolina Ceriodanhnia chronic effluent bioassay Procedure-Revised *September 1989)or subsequent version procedure Carolina Chronic Bioassay The effluent concentration al which there may be no observable inhibition of-reproduction or significant is _96 (defined as treatment two in the North Carolina gnificant mortality � monitoring using this procedure to establish compliance with document). The permit holder shall perform Performed after thirty days from the effective date of this permit condition. The first test will be Permit during the months of Effluent sampling for this testing shall be Performed at the NPDES P final effluent discharge below all treatment processes. All toxicity testing results required as part of this permit condition will be entered on the Effluent Discharge Monitoring Foam EMR-1)for the month in which it was performed,Additionally,DEM Form AT-1 (original)is to be sent to the followin using the parameter code TGP3B. g address: Attention Environmental Sciences Branch North Carolina Division of Environmental Management 4401 Reedy Cheek Road Raleigh, N.C. 27607 Test data shall be complete and accurate and include all s . association with the toxicity tests, as well"as all dose/response danta.cTo�tal dual chorine of tmeasure�lte effl performed t toxicity sample must be measured and reported if chlorine is employed for disinfection of the waste stream, ty Should any single quarterly monitoring indicate a failure to meet begin immediately until such time that a single test is passed. Upon limits, then monthly monitoring will revert to quarterly in the months specified above, P Fen Passing, this monthly test requirement will Should any test data from this monitoring requirement or tests performed by the North Carolina Environmental Management indicate potential impacts to the receiving eceivin s Division of modified to include alternate monitoring requirements or limits. g �' this permit may be re-opened and NOTE: Failure to achieve test conditions as specked in the cited document, such as minimum survival and appropriate environmental controls, shall constitute an invalid test and will mqu control organism retesting(within 30 days of initial monitoring event). Failure to submit suitable test results will constituteimmediate. noncompliance with monitoring requirements. 7Q10 I S CA , Permitted Flow o,&8 MGD IWC S5 Recommended by: Basin & Sub-basin _ oso7O, v��0 Receiving Strom �U- MAr�s County -ppcdi E Date A b A QCL P/F Version 9/91 ' Oxygen Consuming Waste 1 . WATER QUALITY CRITEIRIA The North Carolina Administrative Code ( Section 15 NCAC 2B . 0211 ) requires that a minimum concentration of dissolved oxygen ( DO) be maintained in freshwater systems dependent on stream clas- sification . -Cf•or designated "trout"waters , DO concentrations shall not Tall below 6 . 0 mg/l . For non-trout waters , DO concen-trations shall not fall below a daily average of 5 . 0 mg/ 1 nor a minimum instantaneous value of 4 . 0 mg/ l . Exceptions are made f designated "swamp" waters , which may have lower values if they caused by natural conditions . Per 15 NCAC 2B . 0206 , the governing flow criterion for water quality standards , including dissolved oxygen, generally shall be the minimum average flow for a period of seven consecutive days that has an average recurrence of once in ten years ( i . e . 7Q10 ) . 'However , in cases where the stream flow is regulated , the governing flow for all standards shall be the instantaneous minimum flow , or if deemed appropriate by the Environmental Management Commission , an alternative flow. Alternative governing flow strategies are subject to review on a case-by-case basis . 11 . MODEL DESCRIPTION A modified version of the Streeter - Phelps coupled BOD/DO equation is used to simulate impacts to dissolved oxygen from oxy- gen consuming waste . This model assumes that the receiving waters can be represented by : a) a one-dimensional system, b) steady-state conditions , and c ) advective transport only . Waste inputs are separated into nitrogenous (NBOD) and carbonaceous ( CBOD) components . The integrated form of the equation is : -k„x/u K,, -k„x/u -k„x/u k, -k„x/u -k_x/u D = D„ e + I k„-k,, (e - e ) CBOD + k„-k„ (e e ) NBODI Where : D = DO deficit at milepoint x (mg/ 1 ) D„ = initial DO deficit (mg/ 1 ) x = distance (mi ) u = velocity (mi/day) k„ = reaeration rate ( /day) k,, = CBOD decay rate (/day) k„ = NBOD decay rate (day) CBOD = initial CBOD concentration (mg/ 1 ) NBOD = initial NBOD concentration (mg/ 1 ) r 1. 11 . MODEIL ( L EIVEL B) INPUT In the absence of actual stream data Cor model calibration , a Level B (desktop) model-ing analysis can be performed . Level B modeling incorporates the use of empirical model input equations and DEM procedures to establish model input parameter values . These empirical equations and procedures are summarized below by type of input . a) Model Hydraulics Model hydraulic considerations include streamflow, runoff , stream velocity, channel width and depth, and stream bed gradient ( i . e. slope) . Streamflow and runoff , although not directly dis- played in the model equation affect 'instream concentrations of DO , CBOD, and NBOD. streamflow -- for free-flowing streams , streamflow estimates (both upstream and tributary) for average flow, summer (Apr - Oct ) 7Q10 , winter .(Nov - Mar) 7Q10 , and 30Q2 conditions are obtained from the U. S . Geological Survey (USGS) . Regulated streams are handled on a case-by-case basis . runoff -- incremental flow is incorporated through calcu- lation of runoff rates . The difference between upstream and downstream flows , after subtracting out the flow contributed from point sources and tributaries , can be divided by the distance between the two points to arrive at appropriate runoff rates . Runoff should be calculated for average flow, summer 7Q10 , and winter 7Q10 conditions . stream velocity (U) -- in' the absence of instream time-of- travel data , the empirical regression equation developed by DEM can be used to predict stream velocity. The equation is based on a cross-section of data from 125 time-of-travel studies performed on North Carolina streams , such that : U = 0 . 124 Qact' - " slope' - 79 Qact' . 3-5 Where : Qact = 7Q10 + wasteflow (cfs) Qavg = average stream flow (cfs ) slope = stream bed gradient, (fpm) U = stream velocity (fps) channel width (W) and depth (H) -- the Level B -model assumes that stream channel width (W) = 15 depth . Depth (H) is calcu- lated in the model using this assumption along with the relation- ship between flow (Q) and instantaneous velocity M : -2- V = Q/A wher.-e . A cross-sectional channel area ( f t' ) therefore : V = _ Q W H ( 15 '' H) * 1-1 or H = (Q/15V)" - s slope -- stream bed gradients are calculated from land elevation data contained on USGS topographical maps . Maps dis- played on a 72 min. ( 1 : 24000) scale are preferred when available . Distances along the streambed between contours are measured and the net elevation changes are divided by the distance to obtain the slopes . Large differences in streambed slope should be delineated by individual model reaches . b) Model Reaction Rates Model reaction rates include CBOD decay (kc,) , NBOD decay (kT,) , and reaeration (k„) . CBOD decay rate , k,i (20'C , base e) -- where field data are not available for model calibration, DEM employs a modified ver- sion of the Bosko ( 1966) equation. The method retains the format of the Bosko equation, but alters the CBOD bottle decay rate (k, ) as a function of instream CBOD concentration. The final. equation is : kit = k, + n (V/H) where : n = coefficient of bed activity = exp (-2 .8105 + 0 .598 -; In ( slope) ) k, = CBOD bottle decay rate = 0 . 2/day for instream CBOD <_ 50 mg/1 ' = 0 . 4/day for instream CBOD > 50 mg/l NBOD decay rate , kT, ( 20'C , base e) -- in the absence of field-calibrated rates , DEM uses the EPA default values for k_ : kT, = 0 . 3/day for streams with slope <_ 20 fpm = 0 .5/day for streams with slope > 20 fpm reaeration rate , kA ( 20°C , base e) -- reaeration is deter- mined using the empirical relationships developed by Tsivoglou ( 1976 ) : -3- Qact - 10 ct!s ' k,. 1 - 8 s1ope V 10 c [ s < Q:act < 25 cfs , k„ 1 . 3 = s1opo V Qact- > 2`) cfs , K„ 0 . 88 slope V Note : the following equations are used by DEN to adjust the re- action rates to reflect the model design temperature ( T) k„ (T) k,, ( 200C) a 1 . 047 T k„ (T) = k„ ( 200C) ;t 1 . 080 k„ (T)  k„ ( 200C) 1 . 022 c ) Model Design Temperature Model design temperature (T) is based upon the season and physical location of the stream within the State - Applicable inputs are summarized below: Summer Winter }lydro-Environmental Area IF ( °C ) 'I' ( °C ) Mountains 23 Upper Piedmont 25 14 Middle Piedmont 26 14 Lower Piedmont 26 13 Eastern Piedmont 26 14 Sandhills 27 16 Inner Coastal Plain 27 16 Outer Coastal Plain 28 to _ d ) Background and Boundary Conditions Headwaters -- headwater or boundary conditions are needed for CBOD , NBOD, and DO concentrations . Where instream data are not available.,_ the following default values are assumed : CBOD = 2 mg/ 1 NBOD = 1 mg/ 1Q" \ DO = 90% saturation at T Note : DO saturation values are obta-in-ed from the APHA Standard Methods manual ( 1986 ) -- See Appendix A. Runoff , Tributaries -- background conditions for runoff and tributary flow are also needed for CBOD, NBOD , and DO . Where instream data are not available , the same default values applied to the headwaters are used . 1V . MODEL OUTPUT Waste load allocations derived from the model are output in terms of CBOD and NBOD. For NPDES permit limitations , these components must be transformed into corresponding values of BOD, and NH,-N. The NH,-N limit is determined simply by dividing the allowable NBOD by 4 .5 (approximate stochiometrical ratio) . BOD:, , on the other hand , must be calculated using a CBOD/BOD.S ratio that varies according to type of waste . In the absence of waste- specific CBOD/BODS data, the following assumptions can be used : Waste type CBOD/BODS ratio pure domestic 1 . 5 > 10% industrial 2 . 0 pure industrial 3 . 0 DO can be added to the effluent as a trade-off for either NBOD or CBOD as long as the instream DO standard is maintained . V . SPECIAL CONSIDERATIONS Igor proposed discharges of oxygen-consuming wastewater to streams with a 7Q10 of 0 . 0 cfs , the following Division procedures apply: a) If the 7Q10 = cfs and the 30Q2 > 0 cfs , as verified by the USGS , the applicant will receive the following effluent limitations : Stunmer Winter BODS (mg/1) 5 10 NH,-N (mg/1) 2 4 DO (mg/1) 6 6 TSS (mg/1) 30 30 However , it there are multiple discharges to the stream and the model predicts that the above limits will not protect the DO standard instream, then a discharge will be prohibited . b) If the 7Q10 = 0 cfs and the 30Q2 = 0 cfs , as verified by the USGS , a proposed discharge will be denied. Discharges to lakes and estuaries will be handled on a case- by-case basis . In most situations , the procedures described above will not apply. -5 - , d References Bosko , K. 1966 . Advances in Water Pollution Research . International Association on Water Pollution Research _ Munich . Tsivoglou, E.C. and L.A. Neal. 1976 . Tracer measurement of reaeration: predicting the reaeration capacity of inland streams . Journal WPCF, Vol . 48 , No . 12 . Other Useful References USEPA. 1985 . Rates , Constants , and Kinetics : Formulations in Surface Water Quality Modeling ( 2nd edition) . EPA/600/3-85/040 . USEPA. 1983 . Technical Guidance for Performing �Waste Load Allocations , Book II Streams and River, Chpt . 1 BOD and DO . EPA-440/4-84-020 . USEPA. 1980 . Simplified Analytical Method for Determining NPDES Effluent Limitations for POTWs Discharging into Low Flow Streams . Monitoring and Data Support Division (WH-553 ) . v APPENDIX A. TABLE 421:1. SOLUBILITY Of OXYGEN IN WATER EXPOSED TO WATER-SATURATED AIR AT ATMOSPHERIC PRESSURE(101.3) KPA' Oxygen Solubility mg/L Temperature .0 Chlorinity:0 5.0 10.0 15.0 20.0 23.0 0.0 14.621 13.728 12.888 12.097 11.355 10.657 1.0 14.216 13.356 12.545 11.793 11.066 10.392 2.0 13.929 13.000 12.21E 11.483 10.790 10.139 3.0 13.460 12.660 11.906 11.195 10.526 9.897 4.0 13.107 12.335 11.607 10.920 10.273 9.664 5.0 12.770 12.024 11.320 10.656 10.031 _ 9.441 6.0 12.447 11.727 11.046 10.404 9.799 9.22E 7.0 12.139 11.442 10.783 10.162 9.576 9.023 8.0 11.943 11.169 10.531 9.930 9.362 8.826 9.0 11.559 10.907 10.290 9.707 9.156 9.636 10.0 11.28E 10.656 10.05E 9.493 9.959 9.454 11.0 11.027 10.415 9.835 9.287 8.769 8.279 12.0 10.777 10.193 9.621 9.089 8.586 8.111 13.0 10.537 9.%1 9.416 9.899 9.411 7.949 14.0 10.306 9.747 9.218 8.716 9.242 7.792 15.0 10.094 9.541 9.027 8.540 9.079 7.642 16.0 9.970 9.344 8.9" 9.370 7.922 7.4% 17.0 9.665 9.153 8.667 8-207 7.770 7.356 18.0 9.467 9.969 8.497 8.049 7.624 7.221 19.0 9.276 9.792 9.333 7.8% 7.483 7.090 20.0 9.092 8.621 8.174 7.749 7.346 6.964 21.0 8.915 8.456 8.021 7.607 7.214 6.942 22.0 8.743 9.297 7.873 7.470 7.087 6.723 23.0 8.57E 8.143 7.730 7.337 6.%3 6.609 24.0 9.418 7.994 7.591 7.208 6.9" 6.498 25.0 8.263 7.850 7.457 7.083 6.728 6.390 26.0 8.113 7.711 7.327 6.962 6.615 6.285 27.0 7.968 7.575 7.201 6.945 6.506 6.194 28.0 7.827 7.444 7.079 6.731 6.400 6.085 29.0 7.691 7.317 6.%1 6.621 6.297 5.990 30•0 7.559 7.194 6.845 6.513 6.197 5.8% 31.0 7.430 7.073 6.733 6.409 6.100 5.806 32.0 7.305 6.957 6.624 6.307 6.005 5.717 33.0 7.193 6.843 6.518 6.208 5.912 5.631 34.0 7.065 6.732 6.415 6.111 5.922 5.546 35.0 6.950 6.624 6.314 6.017 5.734 5.464 36.0 6.837 6.519 6.215 5.925 5.64E 5.384 37.0 6.727 6.416 6.119 5.835 5.564 5.305 38.0 6.620 6.316 6.025 5.747 5.481 5.228 39.0 6.515 6.217 5.932 5.660 5.400 5.152 40.0 6.412 6.121 5.842 5.576 5.321 5.07E 41.0 6.312 6.026 5.753 5.493 5.243 5.005 42.0 6.213 5.934 5.667 5.411 5.167 4.933 43.0 6.116 5.943 5.581 5.331 5.091 4.862 44•0 6.021 5.753 5.497 5.252 5.017 4.793 45.0 5.927 5.665 5.414 S.'174 4.944 4.724 46.0 5.835 5.578 5.333 5.097 4.872 4.656 47.0 5.744 5.493 5.252 5.021 4.801 4.589 48.0 5.654 5.40E 5.172 4.947 4.730 4.523 49.0 5.565 5.324 5.094 4.972 4.660 4.457 50•0 5.477 5.242 5.016 4.799 4.591 4.392 From: Standard Methods for the Examination of Water and Wastewater. Sixteenth Edition. American Public Health Association. ' 1985. k. EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS - Final qn, aD/ ` During the period beginning on the effective date of the permit and lasting until expiration the permittee is authorized to discharge from outfall serial number - 001 . Such discharges shall be limited and monitored by the permittee as specified below: l fluent Characteristics Discharge Limitations Monitoring Requirements Kg/day (lbs/day) Other Units (Specify) Measurement Sample Sample* Monthly Avg. Weekl Av . Monthly Avg . Weekly Avg . Frequency :Type Location low 0. 68 MGD Continuous Recording I or E OD,5Day, 20'OC** 24.0 mg/1 36. 0 mg/l 2/Month Composite E, I otal Suspended Residue** 30. 0 mg/l 45 . 0 mg/l 2/Month Composite E,I as N 14. 0 mg/1 21 . 0 mg/1 2/Month Composite E i'ssolved -Oxygen (minimum) 5 . 0 mg/l 5 . 0 mg/l Weekly Grab E,U,D ecal Coliform (geometric mean) 1000. 0/100 ml 2000.0/100 ml 2/Month Grab E,U,D esidual Chlorine Daily Grab E empe•rature Weekly Grab E,U,D otal Nitrogen (NO2 + NO3 + TKN) Quarterly Composite E otal Phosphorus Quarterly Composite E oxicity *** *** Quarterly Composite E y.anide Tao 0.0762 mg/l **** 2/Month Grab E otal CadmiumI6�1 Monthly Composite E otal Chromium103' Monthly Composite E otal Nickel ►b6i Monthly Composite E otal Lead 1b51 Monthly Composite E 'otal Silveri0T1 Monthly Composite E 'otal Copper ibU'- Monthly Composite E 'onductivity. Weekly Grab U,D Z 8V,�/��` r,zj` fir' C) m r, 0 i�Y Y - As-- 'he pH shall iiot 79e;'�11 ess than 6 .0 standard units nor greater than 9 . 0 standard units ind shall be ' 4'n•itor*ed ?/Month at the effluent by grab samples . Chere shall ben scharge of floating solids or visible foam in. other than trace amounts . A. EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS - Final _ During the period beginning on the effective date of the permit and lasting until expiration, the permittee is authorized to discharge from outfall serial number ' - 001 . Such discharges shall be limited and monitored by the' permittee as specified below: fluent Characteristics Discharge Limitations Monitoring Requirements . Kg/day (lbs/day) Other Units (Specify) Measurement Sample Sample Monthly Avg_ Weekly__Avg Monthly_Avg .. Weeks Ayl_ Frequency. TyEe Location *Sample locations : E - Effluent, I - Influent , U - Upstream, D - Downstream Upstream and downstream samples shall be grab samples . **The monthly average effluent BOD5 and Total Suspended Residue concentrations shall not exceed 15% of the respective influent values (85% removal) . ***See Part III, Condition No. I . ****Daily Maximum Limitation Part III • Permit No . NC0021491 I. Toxicity Testing Requirement The effluent discharge shall at no time exhibit chronic toxicity using test procedures outlined in: 1 . The North Carolina Ceriodaphnia chronic effluent bioassay procedure (North Carolina Chronic Bioassay Procedure - Revised *February 1987) or subsequent versions . The effluent concentration at which there may be no observable inhibition of reproduction or significant mortality is 6.6% (defined as treatment two in the North Carolina procedure document) . The permit holder shall perform quarterly monitoring using this procedure to establish compliance with the permit condition. The first test will be performed within thirty days from issuance of this permit. . Effluent sampling for this testing shall be performed at the NPDES permitted final effluent discharge below all treatment processes . All toxicity testing results required as part of, this permit condition will be entered on the Effluent Discharge Monitoring Form (MR-1) for the month in which it was performed, using the appropriate parameter code. Additionally, DEM Form AT-1 (original) is to be sent to the following address : Technical Services Branch North Carolina Division of Environmental Management PO Box 27687 Raleigh, North Carolina 27611-7687 Test data shall be complete and accurate and include all supporting chemical/physical measurements performed in association with the toxicity tests, as well as all dose/response .data. Total residual chlorine must be measured and reported if employed for disinfection of the waste stream. Should any test data from this -monitoring requirement or tests performed by the North Carolina Division of Environmental Management indicate potential impacts to the receiving stream, this permit may be reopened and modified to include alternate monitoring requirements or limitations. Note: Failure to achieve test conditions as specifi ' ,�in the cad document, such as minimum control organism survival n'd ay"ipp6iate - J C � C� environmental controls, shall constitute an invalid est an�`_wi116= require immediate retesting. Failure to submit sui bl �ti.. results will constitute a failure of permit conditio�s . 3uy U� ^�' �L FILE 4 NOXnl CAROLLiA DEPT. OF NATUi2AL RESOURCES AND COMMUNITY DEVEL ENVIRONMENTAL MANAGEMENT CnMMISSInN FOR AGENCY VSE NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM APPLICATION FOR PERMIT TO DISCHARGE WASTEWATER �b o0 STANDARD FORM A — MUNICIPAL `IS �yC�u SECTION L APPLICANT AND FACILITY DESCRIPTION Unless otne,wlse apa,,med on this form all Items are to be completed. It an Item Is not applicable indicate'NA.' ADDITIONAL INSTRUCTIONS FOR SELECTED ITEMS APPEAR IN SEPARATE INSTRUCTION BOOKLET AS INDICATED. REFER TO BOOKLET BEFORE FILLING OUT THESE ITEMS. Please Print or Type 1. Cobh Name of Applicant 101 Town of Mocksville (see Instructions) d. Mailing Address of Applicant (see Instructions 1 7 1 Clement St . ._ Number 6 Street 102a -- Mocksville City 10=a North Carolina Stan 1024 27028 Zip Code 1024 0. Applicant',Authorized Agent Isae instructions) Terry B r a l l e y Name and Title 1030 Town Manager _. Number 6 Street 103a 171 Clement St . Mocksville City 103C '— North Carolina State - 103d 27028 Zip Code 103a 704 634-2259 Twephone 1031 Ana Number a. Previous Application Coo. II a previous appllcatl.h for a per- mit under the National Pollutant Discharge Elimination System has been made,give the date of --— application. 104 YR MO DAY I certify that I am familiar with the Information contained In this application and that to the past of my knowledge and belief such Information Is true,complete.and accurate. Terry L . Bralley _ 102e Town Manager Printed Name of Person Signing Title 92 9 29 1021 YR MO DAY SI nature of Applicant or Authorie• nl Data Application Signed Nur L'❑ Carolina General Statute 143-215.6(b) (2) .provides that: Any person who knowingly makes any false statement representation, or certification in any application, record, report, plan, or other document files or required to be maintained under Article 21 or regulations of the Environmental Management Commission implementing that Article, or who falsifies, tampers wit:), or knowingly renders inaccurate any recording or monitoring device or method required to be operated or maintained under Article 21 or regulations of the Environmental Management Commission implementing that Article, shall be guilty or a misdemeanor punishable by a fine not to exceed $10,000, or by imprisonment not to exceed six months, or by both. (18 U.S.C. Section l001 provides a punishment by a fine or not more than $10,000 or imprisonment not more than 5 years, or both, for a similar offense.) FOR AGENCY USE S. Facllity.(see instructions) Givrthe name,ownership,and physi- cal location of the plant or other operating facility where discharge($) presently occur(s)or will occur. x ::. N D u t c h m a n s Creek' W W T P Name �` Ownership(Public,Private or Both Public and Prlvab). ❑PUB ❑PRV ❑BPP CMck block If a Federal facility aQiO '❑FED and give GSA Inventory Control' Number Location: O f f N C S R 1605 _. Number i Street City A�o��: near Mocksvi l l e _ County 101</''. 'DaVie County _. ':. North Carolina _. State iglr> i. Discharge to Another Municipal Facility(see instructions) a. Indicate If part of your dischargeOiiA. ❑Yes ❑No Is Into a municipal waste trans• port system under another re- sponsible organization. If yes, complete the rest of this Item and continue with Item 7. If no, go directly to Item 7. b. Responsible Organization Receiving Discharge Name '10ip Number&Street fOto City State Zip Code tOfif c. Facility Which Receives Discharge IDoi. Give the name of the facility (waste treatment plant!which►r calves and Is ultimately respon- sible for treatment of the discharge from your facility. d. Average Dally Flow to Facility TO{h' mod (mod) Give your average daily , flow Into the receiving facility. 7. Facility Discharges,Number and Discharge Volume (see Instructions) Specify the number of discharges' ' described In this application and the volume of water discharged or lost to each of the categories below. Estimate average volume per day In Million gallons per day. Do not In- elude Intermittent of noneontinuou$. overflows,bypasses or seasonal dis- charges from lagoons,holding ponds,eta I-2 FOR AGENCY USE Number of Total volume Discharged, ' Discharge Points million Gallons'ar Day 1o7at 1 0 . 3 2- To: Surface Water �87' Surface impoundment with no Effluent 1070,.1' ilb{OY Underground Percolation 10701'' Isli4 6:Q Well(Infection) 1070;. r1Q71 t0ya:. :i;,Tj Other '::�•�Ryr; Total Item 7 107f1 1 = If'other'Is specified,describe 107l1:' ray,if any any of the discharges from this facility are Intermittent,such as from overflow or bypass points, or are seasonal or periodic from lagoons, holding ponds,etc.,complete Item S. 0. Intermittent Discharges a. Facility bypass points Indicate the number of bypass loss::, points for the facility that are discharge points.(see Instructions) b. Facility Overflow Points _ Indicate the number of overflow 10Jti., points to a surface water for the facility(see Instructions). c. Seasonal or Periodic Discharge _ Points Indicate the number of 101110 points where seasonal discharges occur from holding ponds, lagoons,etc. 9. Collection System Type Indicate the type and length(In to♦as miles)of the collection system used by this facility. (see Instructions) Separate Storm ❑SST Separate Sanitary [/SAN Combined Sanitary and Storm ❑CSS Both Separate Sanitary and Combined Sewer Systems ❑BSC Both Separate Storm an-, 10�. Combined Sewer Systems ❑SSC Length 3 6 Mlles 10. Municipalities or Areas Served Actual Population (see Instructions) Name Served 1t0, _Greater Mocksville 3 ,000 %tioe /Y 11 t►a 11 Ob t Total Population Served 1'1 ' I-3 FOR AGENCY USE 11. Average Daily Industrial Flow 3,rrva Q� (2E1 mgd Total estimated average daily waste tI O flow from all Industrial sources. `'"'ts Note: All major Industries(as defined In Section IV) discharging to the municipal system must be listed In Section IV. 12. Permits,Licenses and Applications List all existing, pending or denied permits, licenses and applications related to discharges from this facllity.(see Instructions) For Date Date Date Expirat-o- Agency Use Type of Permit ID Number Flied Issued Denied Date Issuing Agency or License YR/MO/DA YR/MO/DA YR/M /OA YR/MO/DA �:�< �:_:,�•.��: �,;, p�.S NL o021491 3/ i 88 2 28 13 2. #zt <`• 13. Maps and Drawings Attach all required maps and drawings to the back of this application. (see Instructions) 14. Additional Information Item Information Number I - I I - . POST AERATION AND I CHLORINE CONTACT TANK I Chforine I Contact Y I,1 Control �--- W Bldg 1 / elkU I I � N Flour — Settling Tank I Q Splatter ^+ — _ O° O° Sludge Sch Chamber 9 ParsAaU F Drying Beds = 1 1 Sludge i Aeration Basin 6` HoldMq v Tk. XISTING 6 scum Sludge DIGESTED SLUDGE TO SANQ BEDS SLUDGF. WASTING 4 —_� RECIR. — --Sam„—s Muge _ - ���_^• r _ SLUDGE . I WASTING I ,,hope � I 1 Holding SAND r Tk. ; 4- BEDS Setting Tank Grit Chamber fi Porti`all Flit I / L Aeration Basin PUMP i /4~ - I I STATION--,,,,. 4` F.M. TO LAND CLZ I DISPOSAL BLOC. \ t -' EO:AE AMIN ACTr . 'DOWN OF MOCKSVILLE, NC DUIYHIIANS CREEK WWPP PROCESS SCRcMA%IC PAGx6 2 o F 2 STANDARD FORM A—MUNICIPAL FOR AGE CV USE SECTION IL BASIC DISCHARGE DESCRIPTION TTI I I Complete this section for each present or p►oposod oischarge indicated In Section I,Items 7 and e,that Is to surface waters. This Includes discharges Discharges to wellsrage mustybeems In described Ich the waste here there areter does not also dischargers torsurface waters from this fach&treatment works ility.to being discharged to descriptions of each discharge are required even If several discharges originate In the same facility. All values for an existing discharge should be representative of the twelve previous months of operation. If this Is a proposed discharge,values should reflect best engineering estimates. ADDITIONAL INSTRUCTIONS FOR SELECTED ITEMS APPEAR IN SEPARATE INSTRUCTION BOOKLET AS INDICATED. REFER TO BOOKLET BEFORE FILLING OUT THESE ITEMS. 1. Discharge Serial No.and Name 001 a. Discharge Serial No. =41�•, (see Instructions) , Dutchmans Creek Discharge s b. Discharge Name 201b' Give name of discharge,If any (see Instructions) 001 c. Previous Discharge Serial No 2010. If a previous NPDES Permlt application was made for this dls- charge(Item 4,Section 1)provide previous discharge serial number. 2. Discharge Operating Dates `�'.. ]2 6 a. Discharge to Bsgin Date Me. --- If the discharge has never YR MO occurred but is planned for some future date,give the date the discharge will begin. N/A b. Discharge to End Date I/the tlls- 202b -- ' charge is scheduled to be dlscon- YR MO tinued'wlthln the next 5 years, give the date(within best estimate) the discharge will end. Give rea- son for discontinuing this discharge in Item 17. 3. Discharge Location Name the polltical.boundarles within which Agency Use the point of discharge Is located: North Carolina � State 2038 Davie County sa�b , (If applicable) City or Town 203c 4. Discharge Point Description (see Instructions) Discharge Is Into(check one) Stream(includes ditches,arroyos, 2q." UTR and other watercourses) Estuary ❑EST Lake ❑LKE Ocean ❑OCE Well (Injection) ❑WEL Other ❑OTH If'other'Is checked,specify type S"b S. Discharge Point—Lat/Long. State the precise location of the point of discharge to the nearest second. (see Instructions) Latitude :os 3 5 DEG. 5 3 MIN. 3 2 SEC Longitude late 80 DEG 3 DO MIN• 0 8 SEC II-I This section contains 8 pages. DISCHARGE SERIAL NUMBER FOR AGENCY USE DO( 6. .Discharge Receiving Water Name D u t c h m a n s Creek Name the waterway at the point of �Ilit. dlscharge.(ses Instructions) ..:. :.: For Agency Use :%'':>°:r For Agency Use Minor 303e If the discharge Is through an out. fall that extends beyond the shoreline or Is below the mean low water line, complete Item 7. 7. Offshore Discharge N/A a. Discharge Distance from Shore17i feet b. Discharge Depth Below Water N/A Surface tt@7b feet If discharge Is from a bypass or an overflow point or Is a seasonal discharge from a lagoon,holding pond,etc.,complete Items 8,9 or 10. as applicable,and continue with Item 11. S. Bypass Discharge (see Instructions) a. Bypass Occurrence Check.when bypass occurs / Wet weather tt0lat. ❑Yes Ltd No Dry weather 20tliZ.: ❑Yes' Fkr<o b. Bypass Frequency Give the actual or approximate number of bypass Incidents per year. Wet Weather- ibt 0 'times per year Dry weather ttttttt. D times per year c. Bypass Duration Give the average bypass duration In hours. Wet weather :mat D hours Dry weatherO1ai. 0—hours d.. Bypass Volume Give the average volume per bypass Incident, In thousand gallons. N/A Wet weather ` thousand gallons per Incident N/A Dry weather k thousand gallons per Incident i , ce. a. Bypass Reasons Give reasons N/A why bypass occurs. i.20N> Proceed to Item 11. 9. Overflow Discharge(see Instructions) a. Overflow Occurrence Check when overflow occurs. '.:•.`, Wet weather xOfa't ❑Yes [04[,/No Dry weather tQFi! ❑Yes VNo b. Overflow Frequency Give the actual or approximate Incidents per year. Wet weather t•'Out: 10 times per year Dry weather ( '' �1—times per year DISCHARGE SERIAL NUMBER OR AO[NCV Uti[ Q 0( i< C. Overflow Duration Give the average overflow duration In hours. Wet weather ; 01i1. 0 hours Dry weather w '.; O Hour d. Overflow•Volums Give the average volume per overflow Incident In thousand gallons. •xs N/A Wet weather dY:'• thousand gallons per Incident .a: N/A Dry weather 4140! thousand gallons per Incident r L'r�ck�4. Proceed to Item 11 :p .-AK 10. Sessonal/Psrl odic Discharges a. Seasonal/Periodic Discharge N/A Frequency If discharge Is Inter- �lOtt' times per year mittent from a holding pond, % 's":•i: lagoon,etc.,give the actual or approximate number of times this discharge occurs per year. `^< b. Seasonal/Periodic Discharge "a:,, N/A Volume Give the average .: Air;' thousand gallons per discharge occurrence volume per discharge occurrence In thousand gallons. c Seasonal(Periodic Discharge t``""''' N/-A Duration Give the average dura 10 days tlon of each discharge occurrence In days. f N/A d. Seasonal/Periodic Discharge Occurrence—Months Check the t.1.Otk.< ❑JAN ❑FEB ❑MAR months during the year when the discharge normally occurs. s`;<.,;, ❑APR ❑MAY ❑JUN >N% %S ❑JUL ❑AUG ❑SEP ❑OCT ❑NOV ❑DEC 11. Discharge Treatment a. Discharge Treatment Description Describe waste abatement prac- tices used on this discharge with a brief narrative. (See lnstruc• x" ' Treatment consists of : Screening & Grit ss::.:k::.• tions) 1:1�<: removal , followed by activated sludge treatment followed by final setting : waste sludge goes to a holding tank , then sand beds , then land application . Clarifier effluent passes through clorination�aeration prior to discharge . U-3 DISCHARGE SERIAL-NUMBER FOR AGENCY USE 001 b. Discharge Treatment Codes S , M , G , A S E , N , PG Using the codes listed In Table 1 211*:: of the Instruction Booklet. describe the waste abatement B H X processes applied to this dis- charge In the order In which they occur.If possible. Separate all codes with Commas except where slashes are used to designate parallel operations. If this discharge Is from a municipal waste treatment plant(not an overflow or bypass).complete Items 12 and 13 12. Plant Design and Operation Manuals Check which of the following are currently available a. Engineering Design Report b. Operation and Maintenance Manual 13. Plant Design Data(see Instructions) sfi a. Plant Design Flow (mgd:) 0 . 6 8. mgd b. Plant Dmlgn BOO Removal (%) =t !; 95 % c. Plant Design N Removal (%) t111►{! 95 % d. Pliant Design P Removal(%) 2/3a M1 N A % e. Plant Design SS Removal(%) 2134 95 % f. Plant Began Operation (year) 2131 1972 . g. Plant Last Ma)or Revision(Year) .2.134 . 1984 DISCHARGE SERIAL NUMBER 001 FOR AGENCY UfE 14. Description of Influent and Effluent(see Instructions) Influent Effluent 9 0 Parameter and Code ° 7 0 < < > X> y o , .� ' e ' < > Z y (1) (2) (3) (4) (5) (6) (7) Flow Million gallons per day � 50050 0 . 318 0 . 318 0 . 237 0 . 382 Cont . 365 N/A': pH Units 00400 6 . 9 7 . 0 1/7 52 G Temperature(winter) ! `F 74028 55 : 4 55 . 4 55 . 4 57 . 2 1/7 52 G Temperature(summer) cF 74027 62 . 2 62 . 2 59 66 . 2 1 1/7 52 G Fecal Streptococci Bacteria Number/100 ml 74054 (Provide if available) X X. XN/A N/A Fecal Coliform Bacteria Number/100 ml 74055 (Provide if available) 346 2/3 0 24 G >7<X Total Collform Bacteria Number/100 ml. 74056 (Provide if available) XX N/A _N/A BOD 5-day mI 00 10 129 3 . 7 1• 7 2/30 24 G Chemical Oxygen Demand(COD) mg/I 00340 (Provide if available) N/A N/A' N/A N/A N/A N/A OR Total Organic Carbon(TOC) mg/1 00680 (Provide if available) (Either analysis is acceptable) N/A N/A N/A N/A N/A N/A Chlorine—Total Residual mg/1 50060 N/A 0 . 56 0 . 44' 0 . 70 7/7 365 G A-S DISCHARGE SERIAL NUMBER FOR AGENCY USE 14. Description of Influent and Effluent(s"Instructions) (Continued) Influent Effluent Parameter and Code o > e> ee w` < z � (1) (2) (3) (4) (5) (6) (7) Total Solids mg/l 00500 N/A Total Dissolved Solids mg/l 70300 N/A Total Suspended Solids mg/l 00530 144 6 . 6 1 25 2/30 24 G Settleable Matter(Residue) ml/l 00545 N/A _ - Ammonia(as N) mg/l 00610 (Provide if available) N/A 0 . 825 0 . 2 2 . 3 2/3 0 24 G Kicidahl Nitrogen mg/l 00625 (Provide if available) N/A 2 . 63 -2 . 4 2 . 9 1/9 0 4 G Nitrate(as N) mg/l 00620 el rovide if available) N/A 1 . 73 2 . 2 2 . 5 1/9 0 4 G Nitrite(as N) mg/l 00615 (Provide if available) N/A . 07 . 05 0 . 12 1/9 0 4 G Phosphorus Total(as P) mg/1 00665 (Provide if available) N/A 2 . 17 1 . 9 2 . 3 1 /9 0 4 G Dissolved Oxygen(DO) mg/l 00300 8 . 3 .7:8 , 9 . 13 1/7 52 G n-6 FOR AGENCY USE DISCHARGE SERIAL NUMBER 001 IS.Additional Wastewater Characteristics Cherie the box next to each parameter If It Is present In the effluent.(see Instructions) fL Parameter Parameter y 51 a (215) 2 (215) a Bromide Cobalt Thallium 71870 01037 01059 Chloride Chromium Titanium 00940 01034 01152 Cyanide Copper Tin 00720 X 01042 X 01102 Fluoride Iron Zinc 00951 01045 01092 X Sulfide Lead Algicidese 00745 01051 X 74051 Aluminum Manganese Chlorinated organic compounds' 01105 01055 74052 Antimony Mercury 00,and grease 01097 71900 00550 Arsenic Molybdenum Pesticides* 01002 01062 74053 Beryllium Nickel Phenols 01012 01067 X 32730 Barium Selenium Surfactants 01007 01147 38260 Boron Silver Radioactivity* 01022 01077 74050 i Cadmium ` 01027 *Provide specific compound and/or element in Item 17,if known: Pesticides(Insecticides,fungicides,and rodenticides)must be reported in terms of the acceptable common names specified in Acceptable Com- mon Names and Chemical Names for the Ingredient Statement on Pesticide Labels, 2nd Edition,Environmental Protection Agency,Washington, D.C. 20250,June 1972,as required by Subsection 162.7(b)of the Regulations for the Enforcement of the Federal Insecticide,Fungicide,and Rodenticide Act. II.7 FOR AGENCY USE STANDARD FORM A-MUNICIPAL SECTION III. SCHEDULED(IMPROVEMENTS AND SCHEDULES OF IMPLEMENTATION This section requires Information on any uncomlDeSsed implementationd Dy loCal,Stat orlFederah agen IC es has nor Dy court actionfor s IFIon of waste treatment YOU ARE SUBJECT TO facilities. Requirement schedules may have been SEVERAL DIFFERENT IMPLEMENTATION SCHEDULES, EITHER BECAUSE OF DIFFERENT LEVELS OF AUTHORITY IMPOSING DIFFERENT SCHEDULES(ITEM lb)AND/OR STAGED CONSTRUCTION OF SEPARATE OPERATIONAL UNITS(ITEM 1c),SUBMIT A SEPARATE SECTION III FOR EACH ONE. FOR AGENCY USE 1. Improvements Required 4' a. Discharge Serial Number Affected List the discharge serial numbers,assigned In Sec. tlon 11.that are covered by this Implementation schedule ti. Authority Imposing Requirement Check the appropriate Item Indl- cating the authority for the Irn,- _^x; plementation schedule. If the. Identical Implementation sched- ule has been ordered by more than one authority,check the ' appropriate Items. (seeln- structlons) .•:;:��'s ❑LOC Locally developed Plan ❑ARE Areawlds Plan ❑SAS Basin Plan State approved Implementation ❑SQS schedule Federal approved water quality ❑Was standards Implementation plan Federal enforcement procedure ❑ENF' . or action ❑CRT State court order ❑FED Federal court order c. Improvement Description Specify the 3-character code for the General Action Description In Table II that best describes the improvements required by the Implementation schedule. If more than one schedule applies to the faelllty because of a staged con- struction schedule,state the stage of construction being described here with the appropriate general action code. submN a seParats Section III for each stage of construction planned. Also,list ell the 3-character(Specific Action)codes which describe ln•more detail the pollution abatement practices that the Implementation schedule requires. 3-character general action description 3-character speclfic•action descriptions 301d 2• Implementation Schedule and 3. Actual Completion Dates Provide dates imposed by schedule and any actual dates of completion for Implementation steps listed below. Indicate Well as accurately as possible. (see Instructions) Implementation Steps 2. Schedule(Yr/Mo/Day) 3. Actual Completion(Yr/Mo/Day) a. Preliminary plan complete 302• b. Final plan complete . c. Financing complete 6 contract awarded d. Site acquired 302 -/-/- '0z -/-/- e. Bog in I r,or.etructlon f. End construction 30V -/-/- -/-/- g. Begin Discharge h. Operational level attained 302�? -/'-� This section contains 1 page. Ill-1 . GPO 865.707 FOR AGENCY USE. STANDARD FORM A—MUNICIPAL .1 H iTM SECTION 17. INDUSTRIAL WASTE CONTRIBUTION TO MUNICIPAL SYSTEM Submit a description of each major Industrial facility discharging to the municipal system,using a separate Section IV for each facility descrlp- tion. Indicate the 4 digit Standard Industrial Classification(SIC)Code for the Industry,the major product or raw material,the flow(in thrn;- sand gallons per day),and the characteristics of the wastewater discharged from the Industrial facility Into the municipal system. Consult :3ble III for standard measures of products or raw materials. (see Instructions) 1. Major Contributing Facility _ (toe Instructions)Name 401a LEmuc-axat J f up-w I,-rpPr- L t oos T21ES Number&Street 401b — city 401e ���' County 401d — State 4010 lV Qi2'('N AROLI N A — — Zip Code 401; 2. Primary Standard Industrial 402 Classification Code (Sae Instructions) Units(See Quantity Table I11) 3. Principal Product or Raw Material (see Instructions) Product 403a ®O� I�QN l rV Zt %48k:t 4034 Raw Material 403b �1 l►J I S N�I?S 42dA 402f. 4. Flow Indicate the volume of water 't discharged Into the municipal sys- 404a 3or�y thousand gallons per day tam In thousand gallons per day and whether this discharge Is Inter- 404b Intermittent lint)[:)Continuous(con) mittent or continuous. �� S. Pretreatment Provided Indicate If 405 ❑Yes &.N*o Pretreatment is provided prior to entering the municipal system 6. Characteristics of Wastewater (see instructions) Parameter �""• Name 4o63 ParametNumber er �0/2 rJ t9O � 406b Value' l�0 S4 —74P 29O TV-I This section contains ! page. GPO 065.706 FOR AGENCY USE. STANDARD FORM A—MUNICIPAL SECTION 17. INDUSTRIAL WASTE CONTRIBUTION TO MUNICIPAL SYSTEM Submit a description of each major Industrial alif naic to the municipal system. separate h iv for l,ch tlt descrip- tion. Indcatithe 4digit SUd srial classification Code for theIndustry, he major product or rawmateriathe flow(In thn,;- sand gallons per day).and the characteristics of the wastewater discharged from the Industrial facility Into the municipal system. Consult :3bie III for standard measures of products or raw materials. (see Instructions) 1. Major Contributing Facility (see Instructions) ROt,.� �I Name 401a Number&Street 401 b City 4014 M County 401d 1�Au 1 State 4019, Zip Code 401; 28 _, Primary Standard Industrial 402 251? Classification Code (see Instructions) Units(See Quantity Table 111 3. Principal Product or Raw • Materlr,t• ..!see Instructions) Product Raw Material 407b EP_806 R D � t=1 1.11 s l-1�S • 4. Flow Indicate the volume of water 125,��� discharged into the municipal syh 404a thousand gallons per day tam In thousand gallons per day and whether this discharge Is Inter. 404b I]Intermittent lint)aiContinuous(con) mittent or continuous. 5. Pretreatment Provided Indicate If 405 2(Yes ❑No pretreatment Is provided prior to entering the municipal system i. Characteristics of Wastewater (see Instructions) Parameter �00 SS K o Name Parameter 4063 Number fD0'3l0 00530 000OZ5 so0ti Value' 170 2GO 54- 450 O•oo4- TV-I This section contains I page. GPO $65.706