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HomeMy WebLinkAboutNC0020231_WASTELOAD allocation_19901105WDE5 DOCUNEXT SCANNIMO COVER SKEET NPDES Permit: NCO020231 Louisburg WWTP Document Type: Permit Issuance Wasteload Allocation Authorization to Construct (AtC) Permit Modifiratinn Complete File - Historical Data Monitoring Report Speculative Limits Instream Assessment (67b) Environmental Assessment (EA) Permit History Document Date: � November 5, 1990 1 This document is priated ozM reuse paper - iMaore an<y conite,Mt on. the reamer side NPDES WASTE LOAD ALLOCATION PERMIT NO.: NCO020231 PERNT= NAME: Town of Louisburg / Louisburg Wastewater _ Facility Status: Existing Tre0. -�+e t4- Plct-+ Permit Status: Modification / Review cLI Major Minor Pipe No.: 001 Design Capacity: D.$ MG D — Eyaivs Domestic (% of Flow): Industrial (% of Flow): Comments: 94 % 6** % I A UWA ftinne RECEIVING STREAM: Tar River Class: WS-III NSW Sub -Basin: 03-03-01 Reference USGS Quad: C25SE, Louisburg n (please attach) County: Franklin Regional Office: Raleigh Regional Office Previous Exp. Date: 6/30/91 Treatment Plant Class: Classification changes within three miles: None within 3 mi. Requested by Prepared by: Reviewed by 7Babw 13— - L,o QI EL 9/1 %/90 Date: -4AMM Date: Date: 0 Modeler Date Rec. # �o Sala Z • Drainage Area (mil) 7 Avg. Streatnflow (cfs):46,0 7Q10 (cfs)) Winter 7Q10 (cfs)P"b 30Q2 (cfs) Toxicity Limits: IWC S % Acut Chronic Instream • g Monitorin • Q P�� Parameters P.O. i—Vmp. COLT C0M PU GTJ J(T -f Upstream Location r `C T- fao� upsT� e4^ Downstream ` Location K S• At Ptw v 5rRrA"k Effluent Characteristics ��,Ant7-,S BOD5 (m ) p NH3-N (mg/1) D.O. (mg/1) s TSS (mg/1) -3© F. Col. 000 ml) zoo PH (SU) Comments: TR2 tLJA BASiN SrEA '4 Pry ure " 6305-TIN4 Fgclu rlES To A"" ITo4 -{-o kL- /%7_XJPAN AA,�D TorAL•- Pk0S ofzou .4 ftANRLt iaAS�S. tIC-ADwA2rcS A/VAUIS(S S►{©uc� E3C ��i2Fa,PME�j (AK W"C SF�clF{Ctj �2 � � EX�,4,USrDai L�o� Request ------------------- WASTELOAD ALLOCATION APPROVAL FORM Facility Name: NPDES No.: Type of Waste: Status: Receiving Stream: Classification: Subbasin: County: Regional Office: Requestor: Date of Request: Quad: Louisburg WWTP NCO0202031 94% Domestic/6% Industrial Existing/, Tar River WS-III, NSW 030301 Drainage Franklin Summer RRO Winter Jule Shanklin Average 9/18/90 C25SE No. 5.8,62 area: 437.0 sq;,mi 7Q10: 14.00 cfs 7Q10: 48.00 cfs flow: 460.00 cfs 30Q2: cfs -------------------- RECOMMENDED EFFLUENT LIMITS ------------------------- EXISTING EXISTING/UPDATED Wasteflow (mgd) : BOD5 (mg/1) : NH3N (mg/1) : DO (mg/1): TSS (mg/1) : Fecal coliform (#/100ml): pH (su) : 0.80 0.80 30 30 5 5 30 30 1000 200 6-9 6-9 **Toxicity Testing Req.: Chronic Q P/F: 8. % OCT a _ "�990 ---------------------------- MONITORING ---------------------------------- Parameters: D.O., temperature, Fecal coli, conductivity Upstream (Y/N): Y Location: at least 100 ft upstream Downstream (Y/N): Y Location: approximately 5.7 miles downstream of discharge. lwii� ExvA��on1 j ----------------------------- COMMENTS ----------------------------------- Louisburg WWTP proposes to expand its facilities. A wasteload has already been performed for the expansion. Because renewal of the existing 0.8 MGD facility is required by next summer, it will be done now. This renewal is per current policy with renewal facilities (i.e. standard Fecal update and checking for ammonia toxicity, etc.). Tar River basin strategy requires existing facilities to monitor total Nitrogen and total Phosphorous on a monthly basis. Headworks analysis should be performed (as was specified for the expansion Recommended by: Date: Reviewed by Tech Support Supervisor: Regional Supervisor: Permits & Engineering: RETURN TO TECHNICK Date: Date: 6 z o Date: (.66fVe� E-xPfttnJ5 toN) at AT CAARENr F'ww — , Facility Name LOUIS&A" --WW7-P Pennit # N(f.00 Z02pZj J CHRONIC TOXICITY TESTING REQUIREMENT (QRTRLY) The effluent discharge shall at no time exhibit chronic toxicity in any two consecutive toxicity tests, using test procedures outlined in: 1.) The North Carolina Ceriodaphnia chronic effluent bioassay procedure (North Carolina Chronic Bioassay Procedure - Revised *September 1989) or subsequent versions. The effluent concentration at which significant mortality is . % (defi; document). eer:mit holder shall compliancg th he permit condi& issuanceurtn _ samplrII �' hrrg.shafl7be z : 9 ts�:, All toxic_ i Dis ' coded ". �itetttrt� Z�p there may be no observable inhibition of reproduction or led As treatment two in the North Carolina procedure perform guartcrjy monitoring using this procedure to establish $Me. fast test will be performed after thirty days from tO of Effluent Etnmed at the NPDES :permitted final effluent discharge below I'm of this permit condition will be entered tin the Effluent c :month in which it was performed, using:he ar meter T1(original.)is to be sent to the followurg�pddress: vrronmental Sciences`Branch. Idrth Carolina Division of Environmental Management P.O. Box 27687 Raleigh, N.C. 27611 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 doselresponse data. Total residual chlorine of the effluent toxicity sample must be measured and reported if chlorine is employed for disinfection of the waste stream Should any single quarterly monitoring indicate a failure to meet specified Iimits, then monthly monitoring will begin immediately until such time that a single test is passed. Upon passing, this monthly test requirement will revert to quarterly in the months specified above. 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 strearn,'this permit may be re -opened and modified to include alternate monitoring requirements or limits. NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum control organism survival and appropriate environmental controls, shall constitute an invalid test and will require immediate retesting(within 30 days of initial monitoring event). Failure to submit suitable test results will constitute noncompliance with monitoring requirements. 7Q10 14 cfs Permited Flow O. MGD IWC%_ 16.1 Basin & Sub -basin osy sot 171201 Receiving Stream TAp=p/E2 County F Recommended by: Date zo 0 "Chronic Toxicity (Ceriodaphnia) P/F at $—.L%, 1,,0 real, MAR, JU , See Part 3 , Condition . "/z, /I o 0203©1 Go,� .„ �,f G i✓WT� 5 A LA) J� . �JS- / NS W /J 7, 40 05 Tay I-AGrJ,/Ty Co&t D > 6V 7 4077 ffitrn^ �NrA GSM/ l�owevEi2� 't'a/�f ^� <,! (</14 `r,ll, n/ %I LlM ftn/D `J 7Ak-FAML/CO gi✓612 BAS%W 63O30/ ). CXt5!-//CI4 CICI LAR4 74 Tv-iN 7a03 i-tMo- pnPal�p �'Gf = O Qj Wou�G I_Rc 0.028.E ca,: ,,,�€ CFl�of�en�€ �9u� 3Le = D, Zo j " /Ua f t/�cuE = 2.14j.4� Gxrt� �` � g/��, ortr�2 AvNnky AR.t, BM W 0 • Z �( 0796y Wtu. N-t' 401- Nt13 -/O-y eWOJCO. W,LL Ce,- Toy L-1mrr 3ecAa37r -Oil'- /N -1Yc .9A5r Ciy4ck4r/ JD14/N/5TX47-1 ✓& l.6-1T AcuTE ioJca4ZY - /X&,v LY dAUNr ,1 ,t2? Ob\ITF ,4/1. qwFp_ ©. S PA -z4s7p L qAk='oohs 7plg1014C4 9 5A-VV 'i 7�'SOj RUN �:rL�rieduri / /qo� i�r. q 4v,4, /✓ /a" G/!:� - ,2F �/f k/f G l2f f), t44:' L; ZalljA/ 7Wcl /diE. if"fCr° -fry �f/ rlD�J H%ate iffAf F/�� !`�( Wj" c!l'!PE�/Z 4N SOG 50anlJ -r. 30� 5 30 3 0 C5U/I 4 ��� o� y�/;� ;zou,�,; i�: Ch S• / �' %Jv0 Zo fq 4-9 0.g nd q F u '4' iTH✓ F 1f15 Gf )�' 2i, n-�/J. N93-�J % LOW,) — °l. 9 ,�/� 6wr) N 143 IJ (16, IAAJ ) : 6 3 1� It (W1,l)) CP1 A;o & AMMONIA ANALYSIS: SUMMER 7Q10: 14.00 cfs NH3-N Effl. Conc: 21.10 mg/1 Standard (1 mg/1): 1000 ug/l Upstream NH3-N Conc.: 220.00 ug/l Design Flow: 0.8000 MGD Predicted NH3-N Instream: 1918.9 ug/1 1.9188 mg/l NH3-N Limit: 9806.4 mg/1 +MI (pt?aoDt «�°'C 196N4 1 7Q10: 48.00 cfs NH3-N Effl. Conc: 21.10 mg/1 Standard (1.8 mg/1): 1800 ug/l Upstream NH3-N Conc.: 220.00 ug/1 Design Flow: 0.8000 MGD Predicted NH3-N Instream: 745.82 ug/l 0.7458 mg/l NH3-N Limit: 62961. ug/l 62.961 mg/1 No z�M'r eri , A J AA / 7- /-J-0 x -r6 51