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HomeMy WebLinkAboutNC0003760_Wasteload Allocation_19900613NPDES DOCUMENT :SCANNING COVER SHEET NPDES Permit: NC0003760 DuPont Kinston facility Document Type: Permit Issuance .''' Wasteload Allocation Authorization to Construct (AtC) Permit Modification Complete File - Historical Engineering Alternatives (EAA) Correspondence Owner Name Change Approval Instream Assessment (67b) Speculative Limits Environmental Assessment (EA) Document Date: June 13, 1990 This document is printed on reuse paper - ignore any content on the resrerse side 0o-re : 3 Lot -As NPDES WAS I LOAD ALLOCATION PERMIT NO.: NC0003760 PERMIFLEE NAME: E. I. Dupont de Nemours and Co. / Kinston Facility Status: Existing Permit Status: Renewal Major Minor Pipe No.: 001 Design Capacity: 3.6 MGD Domestic (% of Flow): 4 % Industrial (% of Flow): 96 % Comments: Effluent characteristics based on long term average flows totaling 2.475 MGD through plant (see attached calculations) RECEIVING STREAM: the Neuse River Class: C-NSW Sub -Basin: 03-04-05 Reference USGS Quad: F 29 SW (please attach) County: Lenoir Regional Office: Washington Regional Office Previous Exp. Date: 4/30/90 Treatment Plant Class: Class 2 Classification changes within three miles: none Requested by: Prepared by: Reviewed by: w(GL Rosanne Barona Dg FT E r Modeler Date Rec. # .Torn 3-zd_ r'0 56so Drainage Area (mi2 ) a55 o .3 Avg. Streamflow (cfs): l5 I LI- 7 Q10 (cfs)M, 1 Winter 7Q10 (cfs) I , (p 30Q2 (cfs) Toxicity Limits: IWC ! . I % Acute hronic Instream Monitoring: Parameters 1ent-A DO. CUy1eUCHO ► 0,4 5 CS o zyk Upstream y Location C01-/-0 Location / et-n S 444- L3 nu. dd1on571110.4'n-� Downstream V Effluent Characteristics —1 BOD5 `..' rl (EL) NH 3-N ` b.3. (LW) D.O. (mg/1) — TSS 'u b3-3 (EL) �, - _» , _ ',) 0 Cwo � - Covnp►;av�lc: CO t3 k2� , may i, Iatf pH (SU) \ TEE.,--ITTCH D L13T o . L l m I T5 k)ir aravli e -e0^s re y u Ir.i-eo/ GCP3F 6Jb/ZL.r1 - LinAt-1-5 are .0 y 0/win/wilts Comments: r" r FOR APPROPRIATE DISCHARGERS, LIST COMPLETE GUIDELINE LIMITATIONS BELOW Effluent Characteristics Monthly 0DailyC7 Averageaximum M Comments rho 1i5 � 35`% 7/4 dointes1cafi 3o4 fP ysrmy/P S TS 6 3 3 l/ 9O f (ocPsF440 _ 4/4,4‘0)t (ocPsF 0 • j- q 649 ..d,a, ate° Ize cadio ated,,,,,,,,f . ts--66„ eito,_ez-c-f-,4-.=&;..5- /CPSF 55J4I Y/4V 9d *),12,tv-tt't-"ui•-&-li klete ,t_e‘j--(..6a64.&. fet.e.44--gf_04.43 vi.i-E1 6;-. 0 - 'IA ifek ci.s$(., Type of Product Produced Lbs/Day Produced Effluent Guideline Reference ro-Pirwt"- AlZe ciptoc:66,4to arickncz,,IL Request No.: 5650 WASTELOAD ALLOCATION APPROVAL FORM Facility Name: NPDES No.: Type of Waste: Status: Receiving Stream: Classification: Subbasin: County: Regional Office: Requestor: Date of Request: Quad: E.I. Dupont de Nemours and NC0003760 )Ipe 00k 4% Domestic/96% Industrial Existing/Renewal Neuse River C NSW 030405 Lenoir Washington R. Barona 900329 F 29 SW RECOMMENDED EFFLUENT Wasteflow (mgd) : BOD5 (#/day) : NH3N (#/day) : TSS (#/day) : pH (su) : Total Phosphorus (mg/1) : EXISTING Daily Avg 3.60 476 63.4 790 6-9 n/a Other parameters as re- gulated by OCPSF Subpart I: Toxicity Requirement: n/a n/a • MONITORING Co NGTON OFFICE REGULATED Drainage area: Summer 7Q10: Winter 7Q10: Average flow: 30Q2: LIMITS MAY 2 1990 D. E. M. 2552.3 283.10 291.60 1514 sq mi cfs cfs cfs cfs PROPOSED 3.60 Mo. Avg. 357 Mo. Avg. EL 63.4 Mo. Avg. WQ 633 Mo. Avg. EL 6-9 Min -Max EL 2 * Mo. Avg. WQ * T P Compliance date: May 1, 1993 Daily Max. as per a tacked list Chronic Ceriod. Qrterly Upstream (Y/N): Y Location: 200 yds upstream from outfall Downstream (Y/N): Y Location: At Planks Landing (3 mi. downstream) COMMENTS The following instream parameters should be monitored: Temp, DO, cond, pH, and BOD5 during the summer months only. Prepared by: Juan C. Mangles ./ Reviewed by Instream Assessment: Regional Supervisor: Permits & Engineering: RETURN TO TECHNICAL SUPPORT BY: aMc.Ctnasv•-- M1Y26W O Date: Date: Date: Date: L/ j 21/ 40 q/acylqd List of Chemicals A B C D 1 2 Daily Max Units Criteria 3 Effluent Characteristics 4 5 Acenapthene 8469 ng/I VvQ 6 Acrylonitrile 242 ug/I EL 7 Benzene 1 3 6 ug/I EL 8 Carbon Tetrachloride 38 ug/I EL 9 Chlorobenzene 28 ug/I EL 1 0 1,2,4-Trichlorobenzene 140 uq/I EL 1 1 Hexachlorobenzene 0.2 ug/I / W 1 2 1 ,2-Dichloroethane 211 ug/I EL 1 3 1 ,1 ,1-Trichloroethane 54 ug/I EL 1 4 Hexachloroethane 54 ug/I EL 1 5 1,1-Dichloroethane 59 ug/I EL 1 6 1,1,2-Trichloroethane 54 ug/I EL 1 7 Chloroethane 268 ug/I EL 1 8 Chloroform 46 ug/I EL/' 1 9 2-Chlorophenol 27 ug/I 'v 2 0 1 ,2-Dichlorobenzene 1 63 ug/I EL / 2 1 1 ,3-Dichlorobenzene 44 ug/I EL 2 2 1 ,4-Dichlorobenzene 28 uq/l EL 2 3 1,1-Dichloroethylene 25 ug/I EL 2 4 1,2-trans-Dichloroethylene 54 ug/I EL 2 5 2,4-Dichlorophenol 82 ug/I WO 2 6 1,2-Dichloropropane 230 ug/I EL 2 7 1,3-Dichloropropylene 44 ug/I EL 2 8 2,4-Dimethylphenol 36 uq/I EL 2 9 2,4-Dinitrotoluene 285 ug/I EL 3 0 2,6-Dinitrotoluene 641 ug/I EL 3 1 Ethylbenzene 1 0 8 ug/I EL 3 2 Fluoranthene 68 ug/I EL 3 3 Bis(2-Chloroisopropyl)ethe 757 ug/I EL 3 4 Methylene Chloride 89 uq/I EL 3 5 Methyl Chloride 190 ug/I EL 3 6 Hexachlorobutadiene 49 ug/I EL 3 7 Naphthalene 8469 ng/I VbQ 3 8 Nitrobenzene 68 ug/I EL 3 9 2-Nitrophenol 69 ug/I EL 4 0 4-Nitrophenol 1 24 uq/I EL 4 1 2,4-Dintrophenol 1 23 ug/I EL 4 2 4,6-Dintro-o-cresol 277 ug/I EL 4 3 Phenol 26 ug/I EL 4 4 Bis(2-ethylhexyl)phthalate 279 ug/I EL 4 5 Di-n-butyl phthalate 57 ug/I EL 4 6 Diethyl phthalate 203 uq/I EL 4 7 Dimethyl phthalate 47 ug/I EL 4 8 Benzo(a)anthracene 8469 ng/I VC Page 1 List of Chemicals A B C D 4 9 Benzo(a)pyrene , 8469 nq/l ,' WC) 5 0 3,4-Benzofluoranthene '' 8469 ng/I J Vfl 5 1 Benzo(k)fluoranthene ✓ 8469 ng/I v INQ 5 2 Chrysene v 8469 ng/I \/ VW) 5 3 Acenaphthylene 8469 ng/I \ VAQ 5 4 Anthracene ✓ 8469 ng/I v VbQ 5 5 Fluorene 8469 ng/I V VbQ 5 6 Phenanthrene 8469 WIV WJ 5 7 Pyrene v 8469 ng/I `/ i". 5 8 Tetrachloroethylene 56 ug/I EL 5 9 Toluene 80 ug/I EL 6 0 Trichloroethylene 54 ug/I EL 6 1 Vinyl Chloride 268 ug/I EL 6 2 Total Chromium) 2587 ug/I ✓ WC) 6 3 Total Copper 362 u q/ I ' VVQ 6 4 Total Cyanide `-'^j ^1=1-, 259 uq/I ,i VbQ 6 5 Total Lead 690 u g/ I EL 6 6 Total Nickel 3980 ug/I EL 6 7 Total Zinc _ 2587 ug/I ' \AO Page 2 10/89 Facility Name Permit# OC_00 0 3-76C� O%A 001 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 concentratioaat which there may be no observable inhibition of reproduction or significant mortality is 1 • % (defined as treatment two in the North Carolina procedure document). The permit holder shall perform quarter1v monitoring using this procedure to establish compliance with the permit condition. The first test will be perfonved after thirty days from issuance of this permit during the months of TC n 1` J v l O 0 tK . Effluent sampling for this testing shall be performed at the NPtDE ermittedfinal effluent discharge below all treatment processes. p g 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 parameter code TGP3B. Additionally, DEM Form AT-1 (original) is to be sent to the following address: Attention: Environmental Sciences Branch North Carolina Division of Environmental Management P.O. Box 27687 Raleigh, N.C. 27611 Test data shall be complete and accurate and include all supporting chemicaVphysical measurements performed in association with the toxicity tests, as well as all dose/response 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 limits, 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 stream, 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 2$ 3 . i cfs Permited Flow 3 ( MGD Recommended by: IWC% k • q Basin & Sub -basin Q 30 `I 0 Receiving Str am QU. ` County " o" Date 2oia� **Chronic Toxicity (Ceriodaphnia) P/F att.%, n , Psi"' r , See Part , Condition PERMIT NO.: NCO() 0 3 7o (' FACILITY NAME- e L D1 t6/ dw Facility Status: (circle one) Permit Status: /RENEWAL } MODWICA11oN UNPERWITED NEW (circle one) Major b` Minor. Pipe No• 0 O Design Capacity (MGD): Domestic (% of Flow) - Industrial (X of Flow): Continents: RECEIVING STREAM: an IAA 'canna/ 'Fr`'h� y '�o Class- . C-JV51/L) k1- euse ,ve, Sub -Basin• o —OS Reference USGS Quad: f County: . �.0 D r Regional Office: As Fa Mo (circle ens) Requested By: k• 8a.r0 rtfi- Prepared By: Reviewed By: kotov = N/A (please attach) Wi WS Date: Date: Date - /3 5o lNPDES WASTE LOAD�l C a, Modeler h. Date Rec. TG Pvt 3.29-7o 56 5 / I Drainage Area (mi2 )C (9• O Avg. Streamflow (cfs)- 7Q10 (cfs) Winter 7Q10 (cfs) 30Q2 (cfs) Toxicity Limits: IWC U % (circle one) Acute / Chronic Instream Monitoring: ; Parameters ;_ Upstream Location Lo ation CoI Cu) S* AY Effluent Characteristics Summer Winter BODE (mg/I) NHa N (mg/1) D.O. (mg/I) TSS (mg/1) F. Col. (/100m1) pH (SU) 6 _ q --1v\rzk cakit W tu) S t7 —F o c.) 3 2_ , A O Cr, .w Y\ Cu ajcn t 4 4,<c),),x11),a- cuni\In-t:1 ATTACHMENT #2 SUBJECT: BIOCIDE SHEETS, REVISED ACTIVITY DESCRIPTIONS FOR MINOR OUTFALLS 002 AND 003 BIOCIDE SHEETS C/x4k C-Vuta-ci' Biocide - Betz Slimicide C-68 Worksheet Form 101 attached. This additive was submitted and approved for use in October 1987, Ref. letter R. Paul Wilms to J. D. Henderson dtd. 10/2/87. Biocide - Betz C-77, C-78-BCDMH additive. Form 101 attached - Ref. letter R. Paul Wilms to J D. Henderson 10/2/87 expressed concern for carryover of residual chlorine from this additive. Recommended testing was conducted. Following two months testing (results attached) meeting was held with DEM, at which time DEM indicated further testing was not necessary due to low chlorine carryover and the additive was approved for use. Ref. letter dtd. 6/23/88, R.P. Wilms to K. J. Kozelski. All cooling water is treated in the wastewater treatment system prior to discharge. RECEIVED WASHINGTON OFFICE MAY 21990 Request No.: D. E. M. WASTELOAD ALLOCATION APPROVAL FORM Facility Name: NPDES No.: Type of Waste: Status: Receiving Stream: Classification: Subbasin: County: Regional Office: Requestor: Date of Request: Quad: 5651 E.I. Dupont de Nemours and Co./Kinston NC0003760 P't�C p0a. Industrial Existing/Renewal UT to Neuse River C-NSW 030405 Lenoir Washington R. Barona 032790 F 29 SW RECOMMENDED EFFLUENT LIMITS EXISTING PROPOSED Wasteflow (mgd) : pH (su) : 6-9 Turbidity (NTU) : Temperature: Metals (ug/1) : 6-9 50 32° C (MAX) Quarterly metal scans 3ti& 141 , Clew M,ONITOCR0NG p deJ e Upstream (Y/N): N Downstream (Y/N): N Location: Location: ehr COMMENTS * The discharge shall not cause the receiving water's temperature to exceeA 2.8°C above background and in no case cause it to exceed 32°C. TRC should be monitored at the eff. if CL2 is added to cooling water Prepared by: Juan C. Mangles Reviewed by Instream Assessment: / Date: V72 9 OD Regional Supervisor: Permits & Engineering: RETURN TO TECHNICAL SUPPORT BY: Date: 4/�616 Date: Date: MAY 2 6 1990 PERMIT NO.: NCOO 037 (p 0 DRAfTsTR FACILITY NAME- € • r• j Facility Status: (circle on.) Permit Status: (circle one) Major N1noz, Pipe No: DD MOOFICATION UNPFSI,QI'IED NEW Design Capacity (MGD): Domestic (% of Flow): Industrial (X of Flow): Comments: CO RECEIVING STREAM: Class:: e Sub -Basin: 0 3 (-/: 6) `5. . Reference USGS Quad: Pr? County: Let' 0 - Regional Office: As Fa Mo . Ra lclrcl..ns) Requested By: f aro ea tiera'am i5re nch (please attach) Date: Prepared By: �• • �r•�:f ��-•++� Date: Reviewed By: cDv I-14 ate- Wi WS 3/; 7/c.o (Geci QUE&T Dr —A u Modeler 5 52_ JC M Drainage Area (m1 ) Date Rec. 3-27- 96 Avg. Streamflow (cfs). 7Q10 (cfs) r Winter 7(210 (cfs) 30Q2 (cfs) Toxicity Limits: IWC X (circle on.) Acute / Chronic Instream Monitoring: NArA"-Z-k-titr4- ch—k-kA(a•Z SAL4 Parameters Upstream Location AA- 1JC 11 Downstream L---.. A(L �L o a At. Vt„,z_ sr.xca.r9d V lC&)JJ+-1? :...ntAitosa Effluent Characteristics Summer Winter BOD5 (mg/I) NH5 N (mg/1) D.O. (mg/I) TSS (mg/l) . F. Col. (/l00mi) pH (Su) 4 -- Q via ,,AA — -4 W,Ae.f,, A2AQ,- 'cot,c`�, , sue d AY • C v ( i , Pb, i v) + a ,\ a) , -rtc S�0AA4� _g oM„ �"rcl eX,aceed ,-,, Coa�to•"�q tau" Comments: MC4i.0 \hq 0. Off- 6& C Odd ex U& ! 3 2° c . i�e C Sc� °A ce s r�i ti c c 2 , S ,e w►e Qna.f. owe, A o. A k\ 0 co.a1Z -%o C a D WASH NGTONLOFFICE MAY 2 1990 D. E. Request No.: 5652 WASTELOAD ALLOCATION APPROVAL FORM Facility Name: E.I. Dupont de Nemours and Co./Kinston NPDES No.: NC0003760 P(Pe 003 Type of Waste: Industrial Status: Existing/Renewal Receiving Stream: Beaverdam Branch Classification: C-NSW Subbasin: 030405 County: Lenoir Regional Office: Washington Requestor: R. Barona Date of Request: 032790 Quad: F 29 SW RECOMMENDED EFFLUENT LIMITS EXISTING PROPOSED Wasteflow (mgd) : pH (su) : 6-9 6-9 Turbidity (NTU) : ** Temperature: Metals(ug/1): Quarterly metal then? 51141 (' 1Y6114;°1I)L Z'`MONITOR 6td e( � `%l'P e Upstream (Y/N): Y Downstream (Y/N): Y Location: At NC 11 Location: At railroad track scans PFRViITS r-,.�,. COMMENTS The following instream parameters should be monitored: temperature and turbidity. ** The discharge shall not cause the turbidity of the receiving waters to exceed 50 NTU. If turbidity exeeds these levels due to natural backgrouC-- conditions, the discharge level can not cause any increase in turbidity in the receiving waters. * The discharge shall not cause the receiving water's temperature to exceed 2.8°C above background and in no case cause it to exceed 32°C. TRC should be monitored at the eff. if CL2 is added to cooling water Prepared by: Juan C. Mangles \A,c0--civC I Reviewed by Instream Assessment: Art Regional Supervisor: Permits & Engineering: RETURN TO TECHNICAL SUPPORT BY: Date: Date: Date: Date: MAY 26 1990 V2-3/9° (//d-60/1