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HomeMy WebLinkAboutNC0004375_Regional Office Historical File Pre 2018 (3)Michael F. Easley Governor NCMD ENR William G. Ross, Jr,, Secretary North Carolina Department of Environment and Natural Resources %W Kerr T. Stevens, Director Division of Water Quality January 29, 2001 v, k)(7L y DERSON .poration 9246 rE, NC 28266 Subject. Renewal Notice"'131ijs '00' NIADES Permit NC IM-544,kit Mount Hotly Road site Mecklenburg County, tee: -subject permit expires on August 31, 2001. North Carolina Administrative Code (15A NCAC 2H,0105(c)) requires cation for permit renewal be filed at least 180 days prior to expiration of the current permit. If you have already r renewal application, you may disregard this notice, satisfy this requirement, your renewal package must be sent to the Division postmarked no later than Match 4, 2001 quest renewal of the permit by this date may result in a civil assessment of at least $500.00. Larger penalties may be ,ending upon the delinquency of the request. permit must be renewed. Discharge of wastewater without a vabd permit would violate North Carolina General Sta and could result in assessment of civil penalties of up to $25,000 per day. If all wastewater discharge has ceased at your faciliq, and you wish to rescind this permit, contact Bob Sled ' Division's Compliance Enforcement Unit at (919) 733-5083, extension 547, You may also contact the Mooresville I Office at (704) 663-1699 to begin the rescission process. Use the enclosed checklist to complete your renewal package. The checklist identifies the items you must! - ----- I Tr__ L­­ _­ ...... a:-__ ___­ ­ Al., -1-1- C__ --l- - address are listed at the bottom of this page. Sincerely, Q , I I/` Charles If. V"eaver, Jr. NPDES Unit cc: Central Files Mooresville Regional Office, Water Quality Section NPDES File 1617 Mail Service Center, Raleigh, North Carolina 27699-1617 919 733-5083, extension 511 (fax) 919 733-0719 VISIT US ON THE INTERNET @ http://h2o.enr.state.nc,us/NPDES e-mail: chades.weaver@nemail.net NPPE S Pertrift NCO004375 Clariant Corporation Mecklenburg County The following items are REQUIRED for all renewal packages: FJ A cover letter requesting renewal of the permit and documenting any changes at the faciliq, since issuance of the last permit. Submit one signed original and two copies. U The completed application form (copy attached), signed by the permittee or an Authorized Representative. Submit one signed original and two copies. U If an Authorized Representative (such as a consulting engineer or environmental consultant) prepares the renewal package, written documentation must be provided showing the authority delegated to any such Authorized Representative (see Part 11,13. 1 Lb of the existing NPDES permit). J A narrative description of the sludge management plan for the facility. Describe how sludge (or other solids) generated during wastewater treatment are handled and disposed. If your facility has no such plan (or the permitted facility does not generate any solids), explain this in writing. Submit one signed original and two copies. The following items must be submitted ONLY b es dischar in ocess Industrial facilities 9� 9 12 r wastewater: U Industrial facilities classified as Primary Industries (see Appendices A-D to Title 40 of the Code of Federal Regulations, Part 122) must submit a Priority Pollutant Analysis (PPA) in accordance with 40 CFR Part 122.21. If the PPA is not completed within one week of March 4, 2001, submit the application package without the PPA. Submit the PPA as soon as possible after March 4, 2001. The above requirement does NOT -apply tomunicpal or non-industtial. aciHties. PLEASE NOTE: Due to a change in fees effective January 1, 1999, there is no renewal fee required with your application package. Send the completed renewal package to: Mr. Charles H. Weaver, Jr. NC DENR / Water Quality / NPDES, Unit 1617 Mail Service Center Raleigh, NC 27699-1617 State of North Carolina Department of Environment Yk and Natural Resources Division of Water Quality Ukki p, MOLE James B. Hunt, Jr., Governor "Rolk ff m-CDENR Bill Holman, Secretary Vft%,� swqu NoRTH CARouNA DEPARTMENT or Kerr T. Stevens, Director ENVIRONMENT ANo NATURAL RESOURCES January 5, 2001 Mr. Gay P. Sanderson Clariant Corporation P.O. Box 669246 Charlotte, No Carolina 28266 Subject- NPDES Permit NCO004375 Clariant Corporation/Mount Holly Plant Mecklenburg County Dear Mr. Sanderson: The Division has reviewed the letter describing the future activities at the Clariant Corporation's Mount The Division suggests a modification to the existing NPDES permit rather than applying for a new NPDES permit. Based on the information provided, the Division could not determine if a major or or modification is appropriate. As long as the activity will not result in an increase in flow or a change in the wastewater characteristics, a or permit modification is appropriate. For a or permit modification, a letter detailing the proposed activities and the requested changes to the permit should be submitted to the NPDES Unit at the address listed below. The Authorization to Construct required for the modifications to the treatment system requires that detailed plans and specifications (stamped by a PE registered in North Carolina), along with design calculations be submitted in triplicate. In addition, 3 copies of the following are required: a letter describing the project, flow schematic and construction sequence. The information listed above should be submitted to the NPDFS Unit at the address fisted below. If you have any questions concerning, please contact Michael Myers at telephone number (919) 733-5083, extension 508. Sincerely, David A. Goodrich NPDES Unit Supervisor cc: Central Files *,00 tion,i NPDES Unit 1617 Mail Service Center, Raleigh, North Carolina 27699-1617 Telephone (919)733-5083 FAX (919)733-0719 An Equal Opportunity Affirmative Action Employer VISIT US ON THE INTERN ET 0 hftpl/h2o.enr,state,ne.us/NPDES Clariant Corporation P.O. Box 669246 Mt. Holly Plant Charlotte, NC 2 266 704.8 7.9651 44 7F "Cla rangy .�. Dp October 29 1996 { l) � " <x g� ),Ys David A. Goodrich, Supervisor 1'NOV 1 1996 NPDES Permits Group Division 671. WaterQuality ' S S CY P.C. fox 29535 Ittt ttttWRL tdjrit Raleigh, North Carolina 276 6-0535 °. Re: Draft Permit NPDES Permit NCO004375 Clariant Coporation - Mount Holly Plant Mecklenburg County Dear Mr. Goodrich: Clariant Corporation hereby submits written comments on the draft permit received with your letter dated September 25, 1996. The draft permit was received on October 1, 1996. Clariant requests that these comments become a part of the record for the permit. Clariant wishes to acknowledge the considerable effort put forth by the Division to review the permit application and develop the draft permit. We especially appreciate the visit to the Mt. Holly site and the opportunity to explain our operations to you. Nevertheless, Clariant has grave concerns over several items in the draft permit which pose significant threats to continued operations at the Mt. Holly site. Specific comments on these and other items in the draft permit e contained in the attached pages. e propose a meeting, at the earliest possible date, with you, Mr. Nizich and others you deem necessary, to discuss the draft permit and our comments. I will call you or Mr. Nizich in early November to schedule a dater Clariant appreciates the opportunity to comment and looks forward to working cooperatively with you during this renewal process. If I can be of assistance or if additional information is needed for your review, please do not hesitate to contact me at (704) 822-2743. Sincerely, '1414� Gary P. Sanderson, P.E. Safety & Environmental Manager Clariant Corporation Comment ##1 k, PERMIT CONDITION: PART I, SECTIC)N �(l A. Contested Permit Condition: ' BOD, discharge limits of 366.2 lbs/day [monthly average] and 988.8 lbs/day [daily maximum] (effective 12/1/97). B. Comments: 1.The proposed BOD5 effluent limits of'366.2 lbs/day [monthly average] and'988.8 [daily maximum] beginning on 12/01/97 constitutes almost a 5 % reduction from the current limits. The facility's 196 DMRs show that the facility cannot achieve these more stringent BOD, limits within the short time period specified in the permit without substantial modification to the existing treatment system. Clariant estimates it would take a minimum of 12 months from the effective date of the permit just to evaluate .how to comply with the :more stringent BOD, limits. The actual design, approval and construction of a new treatment system would take longer. 2. Discharges of BOD at current levels have not caused water quality problems. During the period of the current permit (191-196), Cdlariant (formerly Sandoz) has upgraded its TP at considerable costs to improve treatment performance. No water quality violations have occurred as a result of l is wastewater discharge at current permitted BOD, levels. The Division's "Catawba River Basin Wide Water Quality Management Plan," July, 1995, indicates on Pages'4-45 that water quality standards have been met consistently in the Catawba River mainstream n of Lake Wylie from 1990 through 1995. . The BOD, limit of 366.2 lbs/day proposed by the Division is based on `an average OCPSF flow of 0.78 MGD which the Division calculated based on a long-term average VPvVTP effluent flow of 1.42 MGD from 1991-1995 and an assumed percent (i.e., 54.6%) of flow from OCPSF processing. 'Clariant's production, and subsequently the OCPSF flow, were artificially low during 1992 through 1995 due to depressed economic conditions and. sales: The Mt. Holly facility is a batch manufacturing plant serving the textile industry, and the facility's production varies with the needs of the textile industry. For example, in 1991 due to a good textile market, the WWTP effluent flow was 1.66 MGD. if this permit is based upon the low flow of 1.42 MGD, Clariant will have no flexibility during the term of this permit to manufacture products at the higher capacity observed: during the term o the current permit (i.e., 1991). EPA Guidelines (.58 Federal Register 36890) allow use of annual average flow, calculated over one year (i.., 1991), to determine OCPSF process wastewater flows. Page 1 of 17 October 3+0, 199E 4. Clariant questions whether the use of representative of the plant's operation ( data on the proper representative flow our operation, the use of the flow performance, and the operation of trez improvement. We would like to devel representative flow for use in this pern 5. In this permit, the Division has include, dye and chemical manufacturing and st( for determination of representative OCP [Attachment 1], the following wastewa be designated "contaminated non-proct wastewaters. We have confirmed thh contact for the OCPSF standard. In includes ' ^ ' ontaminated astewater Flows 1995 Flow 87,000 98,000 iinated Groundwater Treatment Filter Backwash tion Condensate WWTP is truly agreeable method to determine the ,e 1991-1995 wastewater flows from Deess) as- OCPSF process wastewater Page 2 of 17^October 30, IS '' � ' Will lip i Page 3 of 17 October 30, 1996 t a �aa cu ca Clariant Corp (NCO0043' 5) - Proposed Limits BOD5- Monthly Avg. (lb/day) BOD5- Daily Max (lb/day) OC'SF Wastewater Dye and chemical Mfg. 2 (45mg/l) (0.77 MOD) (8.34) = 289.0 (120mg/1) (0.77MGD) (8.34) = 7. Contaminated Groundwater (45mg/1) (0.130MGD) (8.34) 48.8 (120mg/1) (0.134MGU) (8.34) = 130.1 Water Treatment Filter Backwash a (45mg/1) (0. 187MG1) (8.34) = 32.7 (120mg/1) (0.087MG1) (8.34) = 87.1 Steam Generation (45mg/1) (0.098MGD) (8.34) 36.8 (120mg/1) (0.098MGD) (8.34) = 98.1 Sanitary(receiving biological treatment) (45mg/1) (( .058MGD) (8.34) = 21.8 (120ing/1) (0.058 1GU) (8.34) = 58.0 Stormwater (process)3 (45 g/1) (0.087MGD) (8.34) = 317 (120mg/1) (0.087MGD)'(8.34) = 87.1 Pesticide Mfg. (OCPSF) (45 /1) (0.074MGD) (8.34) 27.8 (120mg/1) (0.074MGD) (8.34) = 74.1 Pesticide Wastewater (1.6lbs/1000lbs)(1 ,000lb /clay) = 19.2 ("7.41 /100 lb )(12,000 s/da) = 88.8 for water (non -process) (ling/1) (0.138MGD) (8.34) = 1.2 (lmg/1)(8.138MGD) (8. 4)(1.) = 1.7 Total 51Ci.l 1,395.E Notes. 1. BOD5 allocations based on annual average wastewater flow for 1995 of 1.410 MGD. see flour schematic dated-5-20-96. . Flows indicated above are 67.7 of effluent flaw. For LTA flow of 1.42 MGD from 19914 95, BOD5 allocations are: Monthly average BOD5 =512.3 lbs/day, Daily max BOD5 = 1401.9 lbs/clay For LTA flow of 1.66 MGD, BOD5 allocations are: Monthly average 3+C1135! =573.3 lbs/day, Daily max B()D5='1564.5 lbs/day . Flow of 0.087 MGD based on annual average rainfall for areas 1,3 and 4 from stormwater runoff map. 4. Concentration based on SW application (1992). Sites average . mg/1- 3% reduction at WWTP yields 1m /l allocation. .—IV — _ __ x —I a 10'4 4DUION Led Permit Condition: i, �i t, ���� �Ii� n t- a I s• s� s IY' 1 !! it • • • • •n C. Requested Action: Modify the definition of sample location '"I ." to re manufacturing plant," and allocate the non -pesticide containin [see Comment 1(B)(4 pesticide effluent guidelines thin the pesticide category Of the 80,000 gallon/day o sip • « x ��- • :he Norfluorazon process is =dition the majority of the innately 74,000 gallons/day) ived from specialty synthetic Page 5 of 1 October '30, 1996 ^ PERMIT CONDITION: PART 1, SECTION A( A. Contested Permit Condition: Upstream ("U") and downstream ("D") monitoring location requirement for BOD,, dissolved oxygen, temperature and conductivity. B. Comments: I . Clariant has been reporting values for these parameters for the past five years as a part of its existing permit. Sampling and analyses have been performed by a third party who has recently informed Clariant that it will not perform these tests in the future because this the parameters of BOD,, dissolved oxygen, temperature or conductivity. C. Requested Action: Delete the sampling and analyses of upstream and downstream river water as a requirement of this permit for BOD,, dissolved oxygen, temperature and conductivity. N it Condition: The effluent limitatioj d ending.with "vinyl chlor B. Comment: For the reasons disc-; derived for these chemicals t C. .Requested Aetioz Effluent limitations b the OCPSF process flour des recalculated based on Page 7 of 17 October Clariant PERMIT CONDITION: A. Contested Permit Condi { }R Lh di`"t`4YY CSiiR tilhw5.i"�"A{y C9iR to 'L`dt'M �`�L1 krylonitrile ,-Dinitr+ lxachlorobe ene Be c(a) .,-Dichloropropane Be o(a -a eats: i'C Comment # chemicals: toluene 3,4-Benzofluorantl thracene Benzo(k)fluorantht gene Chrysne 6cation in the record for the tower limits. no monthly; average nor day maximum figures for most of then asted Action: vision should justify the lower concentration limits, or use the a 2. The Division should explain the absence of monthly average and daily maximum fi u Page 8 of 17 October 30,I 1 PERMrr 0 Clariant Corporation Comi IT'ION: I Permit Condition.- B. Comment.. Neither of the regulations at 40 C"FR Pi or the Federal Water Chu bath unjustified and unt C. Requested A+ The Division sho the permit. Page 9 of 17 cene yrene p cif c chemicals nor total PAH al easonable. Aion. uld delete Dibenz(ah)anthracene, T de the applicable OOP F ion at 40 C FR, Part 455, this permit is therefore Clariant Corporation Comment #7 I PERNUT CONDITION: PART 1, SECTION B( A. Contested Permit Condition: "The permittee shall comply with Final Effluent Limitations specified for discharges in accordance with the following schedule: Permittee shall comply with the Final Effluent Limitations by the effective date of the permit unless specified below." B. Comments: 1. If the Division persists in drastically reducing the facility's BOO, limits, Clariant's current wastewater treatment system cannot meet the proposed discharge limits by 12/01/97. Therefore, Mari requests that any final permit containing BOO, limits below the currently permitted limit contain a realistic compliance schedule. December 1, 1997, is not realistic. The proposed BOD5effluent limits of 366.2 lbs/day [monthly average] and 988.8 [daily maximum] beginning on 12/01/97 constitutes almost a 58% reduction from addressed in a specific compliance schedule. 2. As currently drafted, the effluent limitation for BOD, and TSS becomes effective on 12/01/97 instead of the effective date of the permit. As stated previously, Clariant objects to both the numerical BOD5 limits and the effective date. However, since the effective date specified in the permit for TSS is other than the effective date of the permit itself, this permit condition should be clarified to recognize the separate effective date. C. Requested Action: 1. Amend this provision to read as follows: "The permittee shall comply with Final Effluent Limitations specified for discharges in accordance with the following schedule: Pagge 10 of 17 October 30 0, 199 Pear. .ve date of this e it)." 3"2 Ibsr a minimu 1197)"'to 11 Page 11 of 17 3 1996 Clariant Corporation Comment #8 PERMIT CONDITION: PART III, SEC�=ION D A. Contested Permit Condition: The permittee shall continually evaluate all wastewater disposal alternatives and pursue the most environmentally sound alternative of the reasonably cost effective alternatives. If the facility is in substantial noncompliance with the terms and conditions of the NPDES permit or governing rules, regulations or laws, the permittee shall submit a report in such form and detail as required by the Division evaluating these alternatives and a plan of action within sixty (60) days of notification by the Division. B. Comment: There is no regulatory or statutory authority to reouire the nermittee to ennfinttalk requires that disposal alternatives be considered at the time of the permit decision. C. Requested Action. - Delete the word "continually." Page 12 of 17 October 30, 1996 Clariant Corporation Comment #9 PERMIT CONDITION: PART M, S A. Contested Permit Condition: "The effluent discharge shall at no ti-Tne exhibit chronic toxicity using te outlined in ... B. Comment. - Parkhurst, B.R., W. Warren -Hicks and L.E. Noel, "Performance Characteristics of Effluent Toxici; Tests: Summarization and Evaluation of Data," Environmental Toxicity and Chemistry, Vol 11, pp. 771-791, 199: Page 13 of 17 October 30, 19� Clariant Corporation Comment #10 PERMIT CONDITION: PART III, SECTION A. Contested Permit Condition: Staging requirement. B. Comments: Clariant fully supports the inclusion of the staging requirements in this permit. However, the formulas contained in this condition are not consistent with the BOD, and NH3 effluent limits set in Part 1, Section (A)(1). VVhile Clariant continues to object to the lower BOD, limits in Part 1, Section (A)(1), the permit conditions for staging still need to be consistent with the final BOD5 limits. C. Requested Action: . The staging requirement limits in Part 111, Section F, should be consistent with the limits for BOD, and NH3 set elsewhere in the permit. Page 14 of 17 October 30, 1996 t t o f � e r M • e •.® 332 e nutrient study should be completed by November 1, 19 following address% .." B. Comments. - s de copies of specific is that the Division on to conclude that (er Basin throua-h the Page 15 of 17 October 30 1996' Ivyal IVI %IlalLailt WaZIM-IVVM�I az�, a WIMILIVII VI VVLZLUIUIV, U115 pennit. C. Requested Action*. Delete pennit condition Part 111, Section G. Page 16 of 17 October 30, 1996 2. The effluent lim� effluent guidelin at 12. 3. Four of the eighi are identified eh Clariant Cox oration Comment #12 mit Condition: Ls on the following chemicals: thane, thane le the above eight chemicals appear to be derived fr( 0 CFR Part 455, Table 4. The proper table is Tabli The f6llowing chemicals are duplicates: Chloromethane = methyl, chloride Dichloromethane = methylene chloride Tetrachloromethane = carbon tetrachloride Trichloromethane = chloroform C. Requested Action: Identify the sample location for the eight pesticide regulated chemicals as L recalculate the effluent limits using 40 CFR Part 455, Table 5. Page 17 of 17 October 30 United Stress 9ndustriri TochnoloW Division EPA 4 Q11.87t 009 Environmental taction WN 552 October 1997 Agency WaSh4ww". Dc Zwo WaterE PA •° soft 'Oft soft jW CIO et it ATTACHMENT LmJFVk;Un1t;1 I f o%rrw FA-.- T f I a will 111111 T11"S Ulf n d u*djml The b --tandards for A ur---an c 'hem*calft Plastics and %in-t-he't 1* C volumeFibers t000int %jource U a t e gov o r lys P==gC01jC :) 6v ��wUlll �M� U..C7PAF€i11r;UTtCMMr-=C NA7iCNAL ICAL fNFC .RMATICN SEnViCE SPR1N P ELt,s, VA, 22161 'IONS DEVELOPMENT location with I MGD of process wastewater flow that was combined with 9 uncontaminated nonprocess cooling water flow, then the BOD . concentrate VII-153 the process wastewater` alone was actually 280 mg/1 before dilution. This conservatively assumes that the cooling water flow is free of BOD, and TSS. However, in the Agency's judgment, many of the sources and flows< reported' as nonprocess wastewater by plants in their respective Section 308 Question_'_ naires are contaminated by process sources ' 0 of BOD, and TSS. Table VII-5 presents a list of the miscel * laneous wastewaters reported in the Section 308 ..1-4 -L LlttA I— flnal^ nMn tnm_ d mated (and therefore process wastewater) or uncontaminate with conventional pollutants. The Agency reviewed this list after receiving public comments on both NOAs criticizing some of its assignments and determined that, in general -its assignments were correct. Since the limitations apply to process wastewater (which includes "contaminated nonprocess" wastewater) only, the relative contributions of process wastewater versus "uncontaminated nonprocess" wastewater.were deter-, mi . ned at the influent and effluent sample sites. These data were used to calculate plant -by -plant "dilution factors" for use in adjusting pollutant concentrations at influent and effluent sampling locations as appropriate. The general procedure for determining sample -site dilution factors and adjusting HODS and TSS values was as follows: Sum uncontaminated nonprocess wastewater flows for an individual plan (e.g., Plant No. 61 uncontaminated nonprocess wastewater flow 0.280 MGD) 9 Sum process wastewater flow for an individual plant (e.g., Plant No. 61 process wastewater flow - 0.02 MGD) # Divide the sum of uncontaminated nonprocess wastewater flows by the total process wastewater flow to determine dilution factor (e.g., for Plant No. 61, 0.280 MGD/ 0.02 MGD - 14.0) Apply the sample -site dilution factor (plus 1) by multiplying by the reported BOD_ or TSS value to be adjusted (e.g., for Plant No. 61, 196 mg/l effiuent BOD, x (14.0 + 1) 2,940 mg/l effluent BOO.. VIi-154 TABLE VTI-50. stew t rs Uncontaminated Nongroce .s WT ' teve s iter (B5) Non -Contact Cooling Vat r ) • r ss- Y � • ar s TABLE VI - 0. CONTAMINATED AND UNCONTAMINATED MISCELLANEOUS "NONPROC SS" WASTEWATERS REPORTED IN THE 1983 SECTION 308 QUESTIONNAIRE (Continued) Cont•.minated "Nonprocess" Wastewaters Uncontaminated Nonprocess 'Wastewaters (therefore designated'as process wastewater) 1: Water Softening Backvash B and CO Generation 'Lab Drains Oeineralizer Spent Regener 'ts i Closed Loop Equipment Overflow Lime Softening of Process filter Baca h� Miscellaneous Service Water ` Deminerali er Wastewater Recirculating Cooling System Laboratory Offices RWAC Blowdovn Lab Utility Demineral ,zer Blovdown Condenser Water Backwash Utility Clarifier Blovdown Deonflem Regenerant Steam Generation Raw Water Filter Backwash RO Rejection Water distribution Power House Blovdovn Inert Gas Gen. Blovdovn . fContaminated Groundwater =Potable Water Treatment Unit Washes Non -Contact Floor Cleaning Slop; Water from Dist Facilities Laboratory and Vacuum Truck Ion Bed Regeneration Tankcar Washing (H Film Wastewater: Generafor`Blowdovn Air Sluice Water Research and Development Quality Control Steam Desuperheating Pilot Plant Other Company Off -site Waste Ion Exchange Resin Rinse; WWII-136 (Continued) therefore designated as process wastewater) Iron Filter Backwash Area Vashdown Vacuum Puma Wastewater Garment Laundry Hydraulic Leaks Grinder Lubricant Utility Area. Process Contact Rainwater Alum Cater Treatment Incinerator H 20 Product Wash ackf.ush from lemineralier Water Clarifier Plowdown Water Treatment Filter Wash Equipment Cooling H.0 Belt Filter Wash Ejector OgPSF Flow from Another Plant VII-1,57 Co 0 n n 0 (D cr co 0 0 co (IQ qQ IQ (4,) (it -PP Ql UJ W --4 Ul 00 (it V) �.O (.A Ct W Q1 -4. -,1 00 -ice 00 — C) w C) -4 C) 4., C> kA W W W C> " W — — W ON ON 0 (:;I\ 00 4a iJt 01 " 0\ ON " �o -,) --) --j 00 :P. 60 il) 6 Lo Ij (J') (ji C� -,3 4- -,,) trj --j Q4 ON C> 1,0 4L. (O�N C) -4 \0 Ul) 110 C� t.A C) ✓ CT`4. tJ (it 41, -P- p. IQ i J ON IQ -Al. uj a C caa CN w 110 1 J C> ON 00 00 -P C> 0 -P. (,A "o " "0 *,0 " ',0 -.1 (.A oo CN -4, — U.) --4 w C) A. 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Hunt, Jr., Governor k Jonathan B. Howes, Secretary FE A. Preston Howard, Jr., PE., Director Ka DEPT. OF FlEALT11, NATURAL RESOURCES September 25, 1996 OCT 1, 1996 Mr. Gary Sanderson Clariant Corporation WSKA or ENVIRONNUMU zIAVZILIEKT P.O. Box 669246 IRKSYLE KUM OFFICE Charlotte, North Carolina 28266 Subject: Permit Changes NPDES Permit NC O004375 Mt. Holly Plant Mecklenburg County Dear Mr. Sanderson - The following is a list of significant changes to the existing permit: • BOD5 and TSS limits (outfall 001) - These have been reduced based on application of the 7pmp rnits wilfbein �"i6 time. mp iance capability. The previous permit Em= developed if Clariant would prefer that compliance were evaluated for COD on the total wastestream. • Total phosphorus (TP) and total nitrogen (TN) - Part 111, Condition H requires evaluati( of the ability to meet TP and TN limits of I mg/I and 6 mg/I (sunimer) respectively. • The definition of "daily" has been removed from the effluent sheets since this term is defined in 15A NCAC 2B .0503(5). • Iron monitoring - This requirement has been dropped. • Mercury monitoring - This requirement has been reduced to quarterly. If this parameter not detected during the next periiiii cycle it will be dropped from the permit. • Manaanese monitorine, - Based on the levels detected, monitoring is still required, how( 4-1 Z:� the frequency has been reduced to quarterly. P.O. Box 29535, Raleigh, North Carolina 27626-0535 Telephone 919-733-5083 FAX 919-733-0719 An Equal Opportunity Affirmative Action Employer 50% recycled/ 10% post -consumer paper • MBAS - Monitoring for this parameter has been reduced to quarterly based on levels detected. • Five specific phenols - Monitoring for these parameters has been dropped. • Chronic toxicity language - The policy prohibiting any test from indicating toxic effects has been in place since 1993 for all facilities monitoring toxicity. ; An NOVis not necessarily sent to the permittee as a result of a single test failure. • Nutrients - It has been determined by the Division through intensive water quality studies that discharges upstream of Lake Wylie, including this discharge, need to control nutrients through the application of the best available technology (BAT) that is economically achievable. The perniittee shall provide the Division with a study which fully investigates the feasability of meeting an average TP limit of 1.0 mg/l and a summertime TN limit of m/l. If you have any questions regarding these changes please call Mr. Greg Ni ich at 919-733-50 3, extension 541. Sincerely, David A. Goodrich, Supervisor NPDES Permits Group Attachnnent cc: enmt File OCT 1 AL I-1,BSOURGES DIVISION or tw"ROKURTAL MAKAMEN, Permit No. STATE OF NORTH CAROLINA DEPARTMENT OF ENVIRONMENT, HEALTH, AND NATURAL RESOURCES DIVISION OF WATER QUALITY PERMIT' TO DISCHARGE WASTEWATER UNDER THE N TI NAL POLLUTANT DI :H R E ELIMIN TI N SYSTEM In compliance with the provision of North Carolina General Statute 143- 1.1, other lawful standards and regulations promulgated and adopted by the North Carolina Environmental Management Commission, and the Federal Water Pollution Control Act, as amended, Clariant Corporation is hereby authorized to discharge wastewater from a facility located at Mount Holly Plant NC Highway 27 north of Charlotte Mecklenburg County; to receiving waters designated as the Catawba River in the Catwaba River Basin in accordance with effluent limitations, monitoring requirements, and other conditions set forth in Parts s I,11 111, and IV hereof. This permit shall become effective This permit and authorization to discharge shall expire at midnight on July 31, 2001 Signed this dayboom I" A. Preston Howard, Jr., P.F., Director Division of Water Quality By Authority of the Environmental Management Commission Pe it No NCO00437 SUPPLEMENT TO PERMIT COVER SHEET Clariant Corporation is hereby authorized to: 1. Continue to operate a 3.9 MIS wastewater treatment facility consisting of two basins for biological waste treatment, stormwater equalization basin for non aline wastewater, stormwater equalization basins for alkaline wastewater, vity secondary clarifiers, acid neutralization, gravity primary clarifiers, air stripper, sludge dewaterin , effluent polishing pond, staged discharge facility including effluent storage, and post aeration, and, treat herbicide manufacturing wastewater, with discharge via the acid sewer to the 3.9 MGD treatment plant, located at Mt. Holly Plant, NC Highway 27, ' north of Charlotte, Mecklenburg County (See Part III of this Permit), and . Discharge from said treatment works at the location specified on the attached map into the Catawba River which is classified Class W -III waters in the Catawba River Basin. During tt outfallts) serial Permit No. NC 0043i 3ermittee is authorized to discharge from ified below: f t h r t s' f7i r Lf 'i s M t l it `mints I.bsl0a-y tJrut S `ecif } Measurement Sample Sample Mon Avg. C?aily Max: Mctn Avg. C?aiiv Marc. Fie uenc} 1 Lacticrnt Flow , 3.9 MGD Continuous Recording I or E BEAD, 5-Day, 20"C'(until 12/1/97)2 852.0 2236.0 Gaily Composite E,U,D BOD, 5-Day, 200C (eff 12/1/97)2 366.2 988,8 Daily Composite E,U,D TSS (until 1 /1/9) 976;0 2928.0 Daily Composite E TSS (eff 12/1197) 504.6 1502.8 Gaily Composite E NH3 as N2 651.0 977.0 Daily Composite E 108.0 156.0 Daily Composite 12 OCD Weekly Composite E Total Phenols 3.9 Weekly Grab E Dissolved Oxygen Daily Grab E,U,D Fecal Goliform Monthly Grab E Total Nitrogen (NO2 +N + TKN)3 Monthly Composite E Total Phosphorusa Monthly Composite E Temperature Daily Grab E,U,D Conductivity 1 Grab U,D Chronic Toxicity4 Quarterly Composite E l Sample locations: E - Effluent, I - Influent, 12 - Pesticide Manufacturing Plant, U = Upstream at NC Highway 27, D - Downstream at 1-85. All stream samples shall be grab samples. Upstream and downstream monitoring shall be conducted three times Per weep during June, July, August and September and since per week during the remaining months of the year. Staging Requirements (Applicable April I - October 31) - See Part Ill., Condition F. 3 See Part 111, Condition G. 4 Chronic Toxicity, (Ceriodaphma) PIF @ 1.8%; March, June, September and December, sec Part Ill, Condition E. The pH shall not be less than .0 standard units nor greater than 9.0 standard units and shall be conducted daily at the effluent by grab sample. There shall be no discharge of floating solids or visible foam in ether than trace amounts. 622 27 '� � '� t ' i • tC40 Wa er* p sass .11 4 ,Utt5t ,�3905 , r r 6 f/f$`i " ~' Sewage 0sal r' 3004 -17 t, rf ilp 4 y 1 y cl:FSiS i.^+„ j' `✓ t �.. Y t A ¢ "j / 73 3 f\i .�.�*• r .; �Y 2D93 a; -x&sr �u t j n � *Etpnemer Ch' `"a = t= w : U_ e Li 3902 +� Q'��.- �...._ � 73cty �� �*� 1s `�• r r'--. s' --" �"` c': v� � `�... } t �`--' r � w y� I ont Abbe w 0 Col e �! Rest Arias Pill r c = 4 ^ Cem�.1t]Colnets 273 ! a« b �' ti jaam.m, 1rC i 1, w� r 6 t"aN£- 533 * YotthaTrailer Ales chi .. .. �� Park i i rMM�` Sure f3eart _ "_�—__* t - ,"� �:� 1 ' > '��J° 1�J` 'CHAt; C}7'T£ 12MJ. '9� i ,r»xER,c�a—ce��oo�cx�s�a�E*. wxs�.FNcrow a c.—tsxz r '96 ' 30" 9� f2 49 E. " ROAD CLASSIFICATION -v "LE Primary highway. Light -duty road, hard or x EFFLC1ENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL NCO004375 During the period beginning on the effective date of the pemiit and lasting until expiration, the Pernrittee is authorized to discharge from ourfall serial number 001. Such discharges shall be limited and monitored by the permittee as specified below: Effluent Characteristics Mon. Avg Daily Max Daily Max Measurement Sample *Sample lb/day lbs/day Frequency+ Type Location Acenapthene 0,16 0.43 Annually Grab E Acrylonitrile 0.69 29.5 gg/I Annually Grab E Benzene 0.29 1.07 Annually Grab E Carbon Tetrachloride 0.13 0.27 Annually Grab E Chlorobenzene 0.12 0.22 Annually Grab E 1,2,4-Trichlorobenzene 0.49 1.01 Annually Grab E Hexachlorobenzene 0.375 gg/l Annually Grab E 1,2-Dichloroethane 0.54 1.67 Annually Grab E 1, 1, 1 -Trichloroethane 0.17 0.43 Annually Grab E Hexachloroethane 0.15 039 Annually Grab E 1, 1 -Dichloroethane 0.16 0.43 Annually Grab E 1, 1,2-Trichloroethane 0J5 039 Annually Grab E Chloroethane 0.75 1.94 Annually Grab E Chloroform 0J5 033 Annually Grab E 2-Chlorophenol 0.24 0.77 Annually Grab E 1,2-Dichlorobenzene 0.61 119 Annually Grab E 1,3-Dichlorobenzene 0.22 0.32 Annually Grab E 1,4-Dichlorobenzene 0.12 0.22 Annually Grab E IJ-Dichloroethylene 0.13 0.20 Annually Grab E 1,2-trans-Dichloroethylene 0.17 0A3 Annually Grab E 2,4-Dichlorophenol 0.31 0.88 Annually Grab E 1,2-Dichloropropane 28.8 gg/I Annually Grab E 1,3-Dichloropropylene 0.23 0.35 Annually Grab E 2,4-Dimetbylphenol 0.14 0.28 Annually Grab E 2,4-Dinitrotoluene 0.82 55.0 gg/I Annually Grab E 2,6-Dinitrotoluene 1.84 4.63 Annually Grab E Ethylbenzene 0.25 0.85 Annually Grab E Fluoranthene 0J8 0.49 Annually Grab Methylene Chloride 0,29 O.64 Annually Grab E Methyl Chloride 0,62 1.37 Annually Grab E Hexachlorobutadiene 0.14 0.35 Annually Grab E Naphthalene O.17 0.47 Annually Grab E Nitrobenzene 0.20 0.49 Annually Grab E 2-Nitrophenol 0.30 0.50 Annually Grab E 4-Nitrophenol 0.52 0.90 Annually Grab E 2,4-Dintrophenol 0.51 0.89 Annually Grab E 4,6-Dintro-o-cresol 0.56 100 Annually Grab E Phenol 0.12 0.21 Annually Grab E Bis(2-ethylhexyl)phthalate 034 2.02 Annually Grab E Di-n-butyl phthalate 0.20 0A1 Annually Grab E Diethyl phthalate 0.59 1 A7 Annually Grab E Dimethyl phthalate 0.14 0.34 Annually Grab E Benzo(a)anthracene 120 gg/1 Annually Grab E A. (1). EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL During the period beginning on the effective elate of the permit and bating until expir _ .. number 001.(Continued) Effluent +harae#;r#ic irsarge 1.irtri#a#urns Ibslday Units fS Mon. Avg. Dam Max. Mon. Avg. 1 MBAS Manganese Mercury Total Sulfate Chlorides2/Month Composite i o. Nt O0043' 5 autfall serial t t s am le Location't !� is a � • Y , irJANIUMVII x i, ; e non -detection are achieved, the monitoring frequency will avert to annually. Part III Permit No. NCO004 75 -Iql E. CHRONIC TOXICITY PASS/FAIL PERMIT LIMIT (QRT Y The effluent discharge shall at no time exhibit chronic toxicity using test procedures outlined in i #G. NUTRIME # North Carolina Division of Water Quality Water Quality Section %Technical Support Branch P,O, Box '2 35 Raleigh, NC 2726-053 State of North Carolina Department of Environment, Health and Natural Resources Division of Water Quality ; Jamey B. Hunt, Jr., Governor ,IdIft law .� Jonathan B. Hawes, SecretaryIMIF� A. Preston Howard, Jr., P.E., Director NW'RONMENT, HEALTH, July', 196 Gary Sanderson Cl 'ant Corporation P.O. Box 66246 Charlotte, North Carolina 28266 DIVISION of M0990,11AL tIANA RIIIP WRIESVILE A1:1A1 Ilfll Subject: Additional B D Allocations NPDES Permit NCO0 4375 :Mount Dolly Plant Mecklenburg County Dear Mr. Sanderson l have ;reviewed the information contained in your letter of June 24, 1996 and -have the following; comments: • Steam Generation - Please verify that the 0.0686 MGDof condensate is not Presently include) in the 0.770 MGD from the OCPSF process area shown on the flow schematic even though it is reused in OCPSF processes. • Filter Backwash - The Division has never given ]BD allocations for this type of wastestre . The $"1:... ,.: ,..... L.... .. ns....L7'_L.., A......,.:—a.....s.....ts...'.s... 71—!­C.,..: i'T"('C C`5 ..a'If1 _..,_f[ ..:::.Y.r.L4... --A AC`:..u......_di ,Y....,:9__ A • Poding and Re -treatment MGD provided the flexi proposed. ty to stare wastewater during winter months. No change to this flow lire Once again, myself and the otner start members appreciated touring your facility on June 1`3, and hope me information obtained is helpful in resolving permit issues expeditiously. Give me a call at 1 -'7 3-50 3, ext. 541 if you have any questions. Sincerely, Greg N rch, vironmemal Engineer NPDES Permits Group Rapid Assessment Group Permit File P.O. Box 29535, Raleigh, North Carolina 27626-0535 Telephone 919-733-5083 FAX 919-7 3-0719 An Equal Opportunity Affirmative Action Employer 50% recycled/ 1 % past -consumer paper Clariant Corporation P.D.Box 669246 t. Holly Plant Charlotte, NC26266 70U27.9651 l and Julie 24, 1996 Mr. Greg Nizich, Environmental Engineer NPDES Permits Group Division of Environmental Management P.O. Box 29535 Raleigh, North Carolina 27626-055 Re: NPDES Permit NC004375 CariantCorp.=Mt. Holly Plant Charlotte, North Carolina, Dear Mr. Nizich. We appreciate the plant visit you and your associates made to our site. Both Mr. Coleman and I wish to thank you for taking the time to tour our plant and discuss issues with us on June 13t . Below is the data requested on our RCRA groundwater pumping system at the wastewater treatment plant. RCRA Groundwater COD BD Composite Sample o. 1 99 ppm 24 ppm o. 2 112'ppm 39 ppm No. 3 99 ppm 30 pptn o. 4 110 ppm 36 ppm After studying the information you supplied regarding proposed limits, I have a few comments and requests that I hope you will consider as you work up limits for the plant°s new permit. For clarity, I have catagorized there as they appear on the water flow schematic. I. Steam Generation' The site does not have a condensate return system. Approximately 70% of the water used to generate steam, 0.0686 MGD, ends up being consumed in the production processes. Some as wash water, some as hot water for vessel make up, and some as clean-up water for production' areas. This portion of the steam generation water really ends up in the wastewater treatment plant as all OCPSF source. NPDES Permit NC004375 ........ June 24, 1 { 11. Filter Backwash The 0.07 MGD backwash from our pros, T. The suspended material represents river intake plant. The backwash flows th effluent canal. While we have not perforr TSS contribution to our effluent, there is source is needed. /Letter . page water intake facility contains significant .ids removed from raw river water by our ugh a settling canal prior to entering the d analyses to determine the exact level of ne. Allowance for TSS and BOD from this 111 Stormwater 0.087 MGD of the 0225 MGD of stormwater flow results from runoff of rainfall on OCPSF portions of the facility. While the other 0.138 MGD of stormwater runoff may not have have fallen on production area locations, it is a contributor of BOD and. TSS to our wastewater treatment plant. Contribution to effluent may not be as great as OCPSF sources, but it is not zero. IV. Ponding and Re -treatment Operations e usually have to store portions of our treated water from December until April, because'BOD removal is impaired by low biological activity. We re -treat and release the stared water during the warmer months. This is normally done during June - September. Average effluent flow rates during these months can range from 1.5 - 2.6 MGD, 6 - 85% higher than the annual daily average. We need some latitude to allow this situation t continue. We look forward to working with you during the permitting period. If you need any ffirther information, please let me know. Sincerely. Gary P. Sanderson, P.E. Safety & Environmental Manager 101 1Q1E,C �aI4es of�4to W�O per day. i shall consist of the following information: the renewal. )lication form (copy attached), signed and submitted in triplicate. is based on the design or permitted flow, whichever is appropriate. 4. Primary industries listed in Appendix A of Title 40 of the Code of Federal Regulations, Part 122 shall also submit a priority pollutant analysis in accordance with Part 122.21, 5. Facilities which have not been constructed within the last permit cycle and are therefore, considered "new" facilities, shall also submit an Engineering Alternatives Analysis, referenced in 15A NCAC Subchapter 2H .0103 and Subchapter 2B 0201(c), 6. If the facility covered by this permit contains some type of treatment works, a narrative description of the sludge management plan must be submitted with the application for renewal. In addition to penalities referenced above, a permit renewal request received after the expiration date will be considered as a new application and will require the higher application fee. 15A NCAC 2H .0105(b)(2) requires payment of an annual Administrative and Compliance Monitoring fee for most permitted facilities. You will be billed separately for that fee (if applicable), after your permit is approved, Utter to Mike Teague January 18,1996 The letter requesting renewal, the Mr. David A. Goodrich Permits and Engineering Unit Division of Environmental Manage Post Office Box 29535 Raleigh, North Carolina 27626-05+ wmcn may tie lent/Q Section 5 e to the North Carolina Department of Envirc :D HNR. IF FACILITY A Mt. Holly Plant Facility Status: Existing Permit Status: Renewal Major or .Pipe No. 001 Design Capacity: 3'.M1D Domestic (% of Flow): % Industrial (% of Flaw): % Comments: RECEIVING STREAM: the Catawba River Class: S-III Sub -Basin: 03-0 -34 Reference USGS Quad: F14SE (please attach) County: Mecklenbur Regional Office: Mooresville Reional Office Previous Exp. Date: 8/31 6 Treatment Plant Class: Classification changes within three miles: Modeler Date Rec. # Drainage Area (mi ; t? Avg. Streamflow (cfs): > , 7Q1 (cfs) Winter (cfs) 3 Q2 (cfs) /,,, Toxicity Limits: I C % Acu Khroni Instream Monitoring: Parameters Upstream Location Downstream Location tvtonthly Average Daily i5^I.Y, WQ or F.L Wastellow (MGD): BOO (lb/day): 3 9 366.2 9888 r•.l. Bpi NH3- Ob/dA TSS (lb/day): 651 977 504.6 1502.8 EL COD (mg/1), 108 156 EL, p (S(): 6-9 6.9 Dissolved Oxygen (rngA)., monitor Fecal Conform (100ml): monitor "total Phosphorus (mgll) monitor Total Nitrogen (mgft monitor MSAS (#gig/l): Qrtrly monitor Manganese (49/1): Qrtrly monitor Total Phenols (lblday)* 3.9 Mercury (µg/0} rtrly monitor Total Sulfate (mgll): monitor Chlorides (mgl* monitor PSP guidelines Qrtrly monitor J FACTSHEffr FOR WASMLOAD ALLOCATION Request # 8459 Facility Nzirne: Clariant Corp -Mt. Holly Plant NPDES No.: NCO004375 Type of Waste: Industrial - 100% Facility Status: Existing Pein-tit Status: Renewal Receiving Stream: Catawba River Stream Classification: WS-III Subbasin: 030834 County: Mecklenburg Str az Claar cter tic. Regional Office: Mooresville Requestor: Nizich Date of Request: 3/11/96 Topo Quad: F14SE 117-t-I-A A Q­­­ n, EPA, etc.) USGS # Date: Note staging requirement condition on page 4. (WLAFile notes attached) Special Schedule Requirements and additional corn eats from Reviewers: Recommended by: Date:_U§D_� Reviewed by Instream, Assessment: t Date: �p Regional Supervisor* < Date. A Pennits & Engineering: Date: RETURNTO TECHNICAL SERVICES BY: EP TOXICS/METALS/CONVENTIONAL PA AINi T R Type of Toxicity Test: Chronic Ceri daphn a P/lw Existing Limit: 1.8% Recommended Limit: 1.8 Monitoring Schedule: MAR JUN SEP DEC Extst�n l ifTi9t Monthly Avg. Daily Max, Wawsteflo (MGD): 3.9 BOD5 (lb/ ): 852 2236 EL N143-N (lb/d):( 651 977 Bpi T (lb/d): 976 2928 EL PH (S C): 6-9 6-9 EL Dissolved Oxygen (mg/1): monitor Fecal Colifonn (/100ml): monitor Total Phosphorus (mg/1): monitor Total Nitrogen (mg/1): monitor Manganese (gtgft monitor COD (mg/1): monitor MBAS (goo): , monitor Iron (mg/1): monitor 4-Cliloro--methylphenol Qrtrly monitor -ethylphenol Qrtrly monitor 4,6-dimethylphenol Qrtrly monitor Pentachlorophenol Qrtrly monitor ,4, -tr chlorophenot Qrtrly monitor Total Phenols (lb/day): 1.8 3.6 Mercury ( g/f} 0.022 (Wkly .Avg,) 2A Total Sulfate(mg/1): monitor Chlorides (mg/1): monitor OCPSF guidelines Qrtrly monitor c min rt Luni s Monthly Average Daily Max, WQ or E Wasteflow (MCI)). 3.9 BOD5 '(lb/clay): 366.2 988.8 EL NH3-N (lb/d):( 651 977 BPI T S (lb/day): 504.6 1502.8 E COD (m11/1): 108 156 EL PH (S U): 6-9 6-9 Dissolved Oxygen (mgA): monitor :Fecal Colif'onn'(/10 ml): monitor Total Phosphorus (mg/1): monitor Total Nitrogen (mg/1): monitor MBAS (g.tg/l). Qrtrly monitor Manganese (p,g/1): Qrtrly monitor Total Phenols (lb/day): - 3.9 Mercury (gt /l): Qrtrly monitor Total ,Sulfate (n g/i): monitor Chlorides (mg/1): monitor OCPSF guidelines Qrtrly monitor 3 LLtrn_iALf hangL— DtL uA-ip rW Aff (�d Updated and revised effluent guidelines (see attached) BOD5,COD,TSS 30Q2 flow rather than 7Q10,used to calculate limit (an Total Phenols aesthetic parameter for taste and odor) Results of reasonable potential toxicity analysis Iron, 4-Chloro-3-methylphenot, 2-methylphenol, 4,6- dimethylphenol, Pentachlorophenol, 2,4,5- trichlorophenol, f1g, MBAS, Manganese dischargers within this portion of the watershed, INSTREAM MONITORING REQUIREMENTS xearn Location: * instream Location: meters: irag locations or monitoring frequencies: MISCELLANEOUS INFORMj f Exisling Treatment lit y demonstrated the ability to mee, �es No —V' Would a "phasing in" of the new limits be appropriate? Yes t-� No Ifyes, please provide a schedule (and basis for that schedule) with the region office recommendations: n z LC 't07" _t LZc- If no, why not? 4 SDCcial 1nstructLQDaqL Conditiona the following formulas: When the daily river flow is calculated to be � 175 efs: BOD5 + C �. 566.4 lb/day When the daily river flow is calculated to be > 175 el's but < 250 H3-N) :5. 1044 lb/day iese staging requirements are to avoid dosing during minimum relea� isteload sent to EPA? (Major) _ (Y or N) Additional Information attached? (Y or N) If yes, explain with attachments. CLARIANT CORP.- MT. HOLL CATAWBA RIVER 030834 (Formerly known as Sandoz Chemica' existing NPDES permit. The 3.9 MCI. Chlorinated org,, of the aeration b A - -.. _I - -1 r JMN 4/26/96 assin-dlation into wastewater. iie compounds have not been detected in the effluent since the upgi sin has been completed. modillication requests to the draft pennit. Final Limits assigned as followed: Wasteflow 3.9 MGD Monthly Avg. Daily Max. BOO 5 852 lbs/day 2236.0 lbs/day TSS 976 lbs/day 2928.0 lbs/day N113-N 651 lbs/day 977 lbs/day Mercury monitor Total Phenols 3.9 lbs/day pH 6-9 SU 6-9 SU DO monitor Fecal Coliform monitor Tot. P monitor Tot. N monitor COD monitor MBAS monitor Manganese monitor Iron monitor Chlorides mon tor Sulfate monitor Quarterly monitoring for 4-chl oro- 3- ineth yl phenol, 2-methylphenol, 4,4 dimethylphenol, pentachlorophenol, and 2,4,5-trichlorophenol. Chronic Toxicity P/F @ 1.8% -MAR JUN SEP DEC OCPSF guidelines are also applied. -From the 1993 -95 data detected parametel include chlorobenzene, 1,2 Dichlorobenzene, 2,4 Dinitrotoluene, 2-Nitrophenol, 2,4- Dinitrophenol, and Total Cyanide, Staging Requirements- Submitted by Clariant in Jan. 1990 letter to DET Applicable April 1-October 31 Permittee will calculate a running daily average stream I as determined by turbine operations at Mt. Island Dam, leakage at the dam (80 cfs) anc 7QIO flow (15 cfs) of Dutchman's Creek. Effluent release is to be controlled such that projected release of BOD and NH3 using the most recent analytical values for these parameters will not exceed the value given in the following formulas: I I ling and CLARZANT CORP.- M`T". HOLLY PLAINT- IM page (1) When the daily river flow is calculated to be < or = 175 cfs BO 5 + 0.54 (NH3- 566.4'lb./day (2) When the daily river flaw is calculated to be > 175 cfs but < or = 250 cfs: BOD5 + (NID-N) < 44 lb./day These staging requirements are to avoid dosing during minimum release periods. Revision to Phenols Limit in 7/93: Early in 1993, Sandoz obtained an estimate c the 30Q2 flew of 716 cfs from USGS and requested that this flog be used to recalculate their phenol limit, instead of the inimum dully average flow of 329 cfs that had been u in the' 89 ..'90 W A process. Limit revised from monthly avg. of 1 lbs/day and da of 3.6 Ibs/day to a new monthl ' avg. limit of 3.9 i s/clay since it was determ. ined that " the modification should, not detrimental effects on water quality. ..Taste and odor problems at water supply intakes are caused by chlorinated phenols, and many of these, limited through the OCPSF guidelines " . Permit Adjudication of Mercury Limit in 8/ I - Plant adjudicated permit becau mercury limit of 0.022 ptg/l (weekly avg.) and 2.4 �tg/l (daily max) given and facility liew+ iry limit be dropped and mercury monitoring be continued to the lowest It )- 's modification requests in current rene al,application Feb tg/l, recommend mercury limit be dropped. Continue with monitoring. dropped, f red ily -e s predicted value > than 1/10 of the allowable and monitoring would be still be recommended. Since the 9.1 mg/I value seems to be real (also reported by facility in data seat in with application), will not recommend Mn limit but continued' monitoring. MBA - max. predicted value > than 1/10 of allowable. however none of the actual values > than 1/10 of allowable. Recommend Quarterly monitoring or dropping it all together. Five specific phenols - all values B I., except for 1 in 4 years of sampling, recommend quarterly monitoring be dropped. CLA iANTCORP.- MT. HOLLY P page M carith thra f`nr�ilitcr Tk- rc>errait car f / in/aa t. Iivtarcn iyyv memo toaanaoz Me TT"OM K. eK) The NH3 limit was not changed with the updated guidelines in this VELA. Revised /1,1 6 - r Clarlrant Corp (1' + O004375) _ Proposed Limits Q_Q- - Monthly AV . (lb/day) Q-Q5 Daily Max., (lb/day) OCPSF Process Waterl (45 mg/1)(0.78 MGD)(8.34) = 292.7 (120mg/1)(0.78 MGD)(8.34) = 780.6 Pesticide wastewater (1.6 lbs/1 C lbs)(12,000 lb/day) = 19 (.4 lb /I000 lb )(12,000 lbsJ ay) 88.8 Groundwater2 (32 mg/1)(0.17)(0.13 MGD)(8.34) 5.9 (32 mg/l)(0.17)(().13 MGD)(8.34)(1.5)" = 8.8 Stormwater (process)3 (45 mg/1)(0.087 MGD)(8.34) 32.7 (120 mg/1)(0,087 MGD)(8.34) = 87.1 Stormwater (non-proc)4 (1 mg/1)(0.138 MGD)(8.34) 1. (1 mg/1)(0.138 MGD)(8.34)(1.5) - 1.7 Sanitary (0 mg/1)(6.058 MGD)(8.34) = 4 (0 mgt1)(0.058 MGD)(8.34)(1.) �-213 (j 366.2 988.8 TSS - qnthl AV' . (lb/day) TSS - Daily -Max. (lb/day) OCPSF Process Wat rl (57 mg/1)(0.78 MGD)(8.34) = 370.8 (183 mg/1)(0.78 MGD)(8.34)_ =1190.5 :Pesticide wastewater (1.8 lbs/1000 lbs)(12 000 lb/day) = 21.8 (6.1 lbs11000 l s)(12,000 lb/day) = 73.2 Groundwater - = 0.0 = O3 O Filter Backwash (30 m /l)(0.08" MGD)(8.34) = 21.8 (5 mgt1)(0.087 MGD)(8.34) = 32.7 Stormwater (Process)3 (57 mg l)(0.08 ' MGD)(8.34) = 41 A (183 mrg/1)(0.087 MGD)(8.34) = 132.8 Stormwater (non-Proc)4(30 mgl1)(0.138 M I)(8. 4) = 34.5 (45 mg/1)(0.138 MGD)(8.34) 51.8 Sanitary (30 rmgt1)(0.08 MGD)(8.34) = JAL 30 mg11)(6.058 MGD)(8.34)(1.5) =2 1.Jo 504.6 1502.8 Summary E isting Permit Proposed Permit Mo. Avg. (lb/clay) Daily Max. (lb/day) Mo. ,erg. (l lday) Daily Max. (lb/day) COD 108 156 108 156 BC D5 852 2236 366.2 988.8 TSS 976 2928 564.6' 1502.8 1-. Flow of 0.78 MGD based can LTA of 1.42 MGD from 1991 - 1995. Flow schematic shows 54,6% of flow is from OCPSF processing. g. 2 Assumes no BOD5 reduction in air stripper. 83% reduction in WVVTP. Conic. of 32 mg/l from Clariant'data submitted 6-24- 6. 3 Flow of 0.087 MGD based on annual average rainfall for areas 1,3 and 4 from stormwater runoff map: Concentration based on SW application' (1992). Sites average 5 m/l - 8 reduction at WVV7P yields 1 mgtl allocation. FACILITY C:lariant carp, OCPSF Flow= 0.78 MGD Flow is based on processes waters only 7010s 329 cis Qavg 3016 cis Human Hith PF 3,9 MGD Human Hlth Stdrd (WS) Allowable Allowable Limit Limit Fedl Standard Stdrd(WS) Allowable Allowable Aquatic Life Human Hith Limit Daily Monthly Daily Monthly Daily Monthly State Aquatic Water& cone. Aquatic cone Water&Orrg Based Max Avg. max avg max avg Lite organisms Lite Water&Org on: Parameter ugll ugrl #td #Id stdrd ggA po 4gA pelt; Wday #relay Vday Acenaphthene 59 22 0. 84 0,143 FC no stunt 1200 no stun 66510,17 no stdrd 2161.581 OCPSF 0.384 #Ill ay O A 43 Acrylonitrile(c) 242 96 1,574 0.624 FC no stdrd 0,059 no stdrd 29.50 no stdrd 0.959 CHRONIC 29,496 I,cg/l 0,624 Benzene (c) 136 37 0,885 0,241 SS no stdrd 1 A9 no stdrd 594.94 no stdrd 19.335 OCPSF 0.885 # id ay 0,241 Carbon Tetrachloride (t) 38 18 0,247 0,117 SS no stdrd 0.254 no stdrd 126,98 no stdrd 4,127 0CPSF, 0, 247 Vday 0117 Chlorobenzene 28 15 0A82 0.098 FC no stdrd 680 no stdrd 37689A0 no stdrd 1224:896 OCPSF 0,182 Vday 0.098 1,44•Trichlor nzene 140 68 0,911 a442 FC no stdrd no stdrd no stdrd no stdrd no stunt no stdrd OCPSF O.91 1 #/day O;442 Hexachlorobenzene (c) 28 15 0.182 0.098 FC no stdrd 0,00075 no stdrd 0,315 no slam 1.22E-02 CHRONIC 0.375 it fl 1,2-Dichloroethane(c) 211 68 1.373 0442 FC no stun 0.38 no stdrd 1W97 no stdrd 6A74 OCPSF 1.373 Vday 0,442" 1,1,1-Trichloroethane 54 21 0,351 0,137 FC no eldrd net stdrd no stdrd no stdrd no stdrd no stdrd 0CPSF 0,351 #/day 0137 Hexachloroethane (c) 54 21 0.351 0,137 FC no stdrd 1.9 no stdrd 949,86 no stdrd 30,870 OCPSF 0.351 Vday 0,137 1,1-Dichloroethane (c) 59 22 0,384 0,143 FC no stdrd no stdrd no stdrd no stdrd no stdrd no start OCPSF 0.384 Vday 0,143 1,1,246chloroethane (c) 54 21 0.351 0,137 FC no stdrd 0.6 no stdrd 299,95 no stdrd 9,749 OCPSF 0,351 #/day 0,137 Chloroethane 268 104 1343 0,677 FC no stdrd no stern no stdrd no stdrd no stdrd no stdrd OCPSF 1.743 Vday O.6 77 Chloroform (c) 46 21 0,299 0.137 FC no stdrd 5.7 no stdrd 2849.57 no stand 92,611 OCPSF 0, 299 /day O A 37 2-Chlorophenol 98 31 0,638 0202 FC - no stunt 120 no stdrd 6651.02 no stdrd 216,158 0C:PSF 0,638 Vday 0,202 1,2-Dichlorobenzene - 163 77 1.060 0.501 FC no stdrd 2700 no stdrd 14 7,89 no stdrd 4863,556 OCPSF 1,060 Ud a;y 0 501 1,3-Dichlorobenzene 44 31 0.286 0,202 FC no stdrd 400 no stdrd 22170.06 no stdrd 720.527 OCPSF ` 0,286 /day 0,202 1,4-Dichlorobenzene 28 15 0A82 0,098 FC no stdrd 400 no stdrd 2217006 no stdrd 720,527 OCPSF 0,182 Vday 0.098 1,1-Dichloroethylene (c) 25 16 0.163 0.104 FC no stun 0.057 no solid 28,50 no stare 0.926 OCPSF : 0,163 Vday O A 04 1,2-trans-Dichloroethylene 54 21 0.351 0.137 FC no staid 700 no stdrd 38797.60 no stun 1260 922 OCPSF 0.351 ##/d ay 0,137 2,4-Dichlorophenot 112 39 0.729 0,254 FC no stdrd 93 no stdrd 6154.54 no stdrd 167,523 OCPSF 0.729 #/clay 0,254 1,2-CDichioropropane 230 153 1,496 0.995 FC no stdrd Oi52 no stdrd 28.82 no stdrd 0.937 CHRONIC 28.821 pgA 1,3-Dichloropropylene (c) 44 29 0,286 0.189 FC no stdrd to no stdrd 4999,25 no stdrd 162A76 OCPSF 0,286 #/clay 0,189 2,4-Dimethylphenot 36 18 0.234 0.117 FC no stdrd 540 no stdrd 29929,58 no stun 972,711 OCPSF 0.234 Vday 0,11.7 2,4=Dinitrotoluene (c) 285 113 1.854 0.735 FC no stdrd 0,11 no stdrd 54.99 no stdrd - 1387 CHRONIC 54.992 lrtj/1 0,735 2,6=Dinitrotoluene (c) 641 255 4,170 1,659 FC no stdrd no stdrd no stdrd no stdrd no stdrd no stdrd 0CPSF 4,170 #Id ay 1,659 Ethytbenzene 108 32 0.703 0,208XQiNO t 325M0 3100,000 1801317 17181795 585,428 5584083 OCPSF 0303 #1day 0,208 Fiouranthene 68 25 0.442 0.163 FC no stdrd 300 no stdrd 1662/,54 no stdrd 540.395 OCPSF 0.442 #/clay 0,163 Methylene Chloride (c) 89 40 0,579 0260 FC no stdrd 4.7 no stdrd 2349.65 no stdrd 76.364 OCPSF 0.579 #Id y 0.260 Methyi Chloride 190 86 1.236 0,559 FC no stdrd no stdrd no stdrd no stdrd no stdrd no stdrd OCPSF : 1,236 Vday 0,559 Hexachlorob ttadiene (c) 49 20 0.319 0A30 SS no stdrd 0445 no stdrd 222.47 no store 7,230 OCPSF 0.319 Vday 0,130 Naphthalene 59 23 0,384 0.143 FC no stdrd no stdrd no short no stint no stdrd no stdrd ()CPSF 0,384 Vday 0,143 Nitrobenzene 68 27 O.442 0,176 FC no stdrd 17 no stdrd 94223 no stdrd 30,622 OCPSF 0,442 Vday O A 76 2-Nkrophenoi 69 41 0.449 0,267 FC no stdrd no stdrd no stdrd no stdrd no stdrd no stdrd OCPSF: Oi 449 Vday 0.267 4-Nitrophenol 124 72 0,807 0.468 FC no stdrd no stdrd no stdrd no stdrd no stdrd no stdrd OCPSF 0,807 /d ay 0. 468 2,4-Dinftrophenol 123 71 0.800 0,462 FC no stdrd 70 no stdrd 3879.76 no stdrd 126.092 OCPSF 0,800 Vday 0,462 4,6-Dinitro-o-cresol 277 78 1.802 0,507 FC : nostdrd 13.4 no stdrd 742,70 no stdrd 24,138 OCPSF 1.802 #/day 0,507 Phenol 26 15 OA69 0.098 FC no stdrd 21000 no stdrd 1163928,04 no stdrd 37827,661 OCPSF 0,169 Vday 0,098 8/12/96 1 FACILITY cianant com, OCPSF Flow 0.78 MOD Flow is based on processes waters only 7010s 329 ds Qav9 3016 do Human Hith PF 3,9 MGD Human Hith Stdrd (WS) Allowable Allowable Limit Unat Feell Standard Stdrd(WS) Allowable Allowable Aquatic Life Human Hith Limit Daily Monthly Daily Monthly Daily Monthly State Aquatic Water & cone. Aquatic cone Water&Org Based Max Avg. max avg max avg Life organisms Life Water&Org on: Parameter UgA UgA #/d #/d stdrd 14911 ggA pgA VgA Wday Wday Vday Bis(2-ethylhexyl) phthalate (c) 279 103 1.815 0,670 FC no stdrd 1.8 no stdrd 899.86 no stdrd 29,246 OCPSF 1.815 #/d ay O670 Dibutyl phthalate 57 27 0.371 0,176 FC no stdrd 2700 no stdrd 149647,89 no stdrd 4863,556 OCPSF 0.3711 Vday 0,176 Diethyl phthalate 203 81 1,321 0,527 FC no stdrd 23000 no stdrd 1274778.33 no stdrd 4143Q296 OCPSF 1 .321 #/day 0,527 Dimethyl phthalate 47 19 0.306 0,124 FC; no stdrd 313000 no slum 17348070.31 no stdrd 563812,285 OCPSF 0,306 Uday 0,124 Benzo(a)anthracene (c, PAR) 59 22 0.384 0.143 FC no stdrd 0.0044 no stdrd 220 no stdrd OXI CHRONIC 2.200 pg/1 Benzo(a)pyrene (c, PAR) 61 23 0.397 0.450 FC no stdrd 0.0044 no stdrd 2.20 no stdrd 0.071 CHRONIC 2.200 pg/1 3,4-Benzofluoranthene (c, PAN) 61 23 0.397 0A50 FC no stdrd 0,0044 no stunt 2,20 no slam 0,071 CHRONIC 2.200 }tgfl Benzo(k)fluoranthene (cPAH) 59 22 0.384 0,143 FC no stdrd 0,0044 no stdrd 220 no stdrd 0,071 CHRONIC 2,200 p,g/I Chrysene (c, PAH) 59 22 0.384 0,143 FC no stdrd 0.0044 no stdrd 2.20 no stdrd 0.071 CHRONIC 2.200 l,tg/l Acenaphthylene 59 22 0394 0A43 FC no stdrd no stdrd no stdrd no suird no stdrd no stdrd OCPSF 0.384 Vday OA43 Anthracene 59 22 0.384 0,143 FC no stdrd 9600 nostdrd 532081,39 no stdrd 17292,645 OCPSF 0,384 Uday 0,143 Fluorene 59 22 0.384 0,143 FC no stdrd 1300 no staid 72052,69 no stdrd 2341112 OCPSF 0,384 Uday 0.143 Phenanthrene, 59 22 0.384 0143 FC no stdrd no stdrd no stdrd no skird no shim no stdrd OCPSF 0.384 Vday 0.143 Pyrene, 67 25 0.436 0,163 FC no stdrd 960 no stdrd 53208A4 no slum 1729,265 OCPSF 0.436 Vday OA63 Tetrachloroethylene (c) 56 22 0,364 0A43 FC no stdrd O's no slum 399.94 no slum 12,998 OCPSF 0,364 Vday 0,143 Toluene 80 26 0.520 0,169 MAO I I .000 6800.000 609,68 376890.98 19.814 12248.957 OGPSF 0,520 Uday 0,169 Trichlororethylene (c) 54 21 0,351 0,137 SS no stdrd 3.08 no stdrd 1539.77 no stdrd 50,042 OGPSF 0,351 #/day O137 Vinyl Chloride (c) 268 104 1.743 0,677 SS no stdrd 2 no stdrd 999.85 no stdrd 32,495 OCPSF 1.743 Vday O677 P no stdrd 0,0028 n Total Chromium 2770 1110 0.000 0,000 SS 50.000 no stdrd 2771.26 no stdrd 90.066 no stdrd OCPSF 0,000 #/day 0006 Total, Copper 3380 1450 0,000 (r000 SS -AL 7.000 no stdrd 387.98 nostdrd 12,609 no stdrd OCPSF O.000 Uday 0.000 Total Cyanide 1200 420 0.000 0.000 Ss 5,000 no stdrd 277.13 no stdrd 9.007 no stdrd OCPSF O.000 #/day 0.000 Total Lead 690 320 0,000 0.000 Ss 25,000 no stdrd 138&63 no stdrd 45.033 no slam OCPSF 0.000 #/day 0,000 Total Nickel 3980 1690 0.000 0.000 SS 88.000 25 4877A1 138563 158.516 45.033 OCPSF 0.000 Vday 0,000 Total Zinc* 2610 1050 0.000 0.000 SS -AL 50,000 no stdrd 2771.26 no stdrd 90.066 no stdrd OCPSF O.000 #/day 0;000 *Total Zinc for Rayon Fiber Manufacture Metal should only be limited if Total metal beating wasleWw, that uses the viscose process and Acrylic process contains metal bearing wasteflow, Fiber Manufacture that uses zinc Cyanide should only be limited it Total cyanide bearing wasteflow: chloride/solvent process is 6,796 ug/L and process oDmains cyanide beating wasteflow, 3,325 uWL for maximum for any one day and maximum for monthly average, respectively, 8/12/96 2 w Facility Marne Clariant Carp. CI- RONIC TOXICITY Y PASS/ The effluent discharge shall at no time exhibit chronic t Additionally, DEM Form AT-1 (original) is to 1 sent to the Attention: Environmental Scie North Carolina Divi EnvironmentalMan 4401 Reedy Creek l Raleigh N.C. 276, Test data shall be complete and accurate and include all supf association with the toxicity tests, as well as all dose/respon sample must be measured and reported if chlorine is employ Should any single quarterly monitoring indicate a failure to i Permit # NC000437 Pipes #001 VERI MIT LIMIT ((; RTRLY) using test procedures outlined in: y procedure' (North Carolina Chronic Bioassay is. e inhibition of reproduction or significant mortality a procedure document). The permit holder shall r compliance with the permit condition. The first W of this permit (luring the rnonthv cry )r this testing shall be performed at the NPDES S. :ion will be entered on the Effluent Discharge rmed, using the parameter code TGPB. Alow ng address. es Branch ;rn of ement d fing chemical/physical measurements performed in data. Total residual chlorine of the effluent toxicity l for disinfection of the waste stream. et specified limits, then monthly monitonng 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. 7Q1329_(R gulated), cfs Permitted Flow -.9- MGD R p9ommended by: IWC 1. °1 _1 Basin Sub -basin _CTB24 -, Receiving Stream Sa awba River County Mecklenburg Date / 12/ 6 } CLQPIF Version 9191 State of North Carolina Dapartment of Environment, Health n Natural Resources Division of Environmental Management James B. Hunt, Jr,, Governor � Jonathan B. Hawes, Secretary A. Preston Howard, Jr., P.., Director pg_ - ,W, q,: k Michael A. Teague, Ph.D._ Clariant Corporation P. 0. Box 669246 Charlotte, North Carolina 28266 1 October !4: Subject:Modification-Name Clatiant Corporation, #NC0a (formerly# •.. Chemicals Corp.) # i Sincerely, Original Sighed By .avid A. Goodrich A. Preston Howard, Jr., P.E. P.O. Box 29535, Raleigh, North Carolina 27526-0 35 Telephone 1-733-5053 FAX 919-7 3-9919 n Equal Opportunity Aff irmative Action Employer 50% recycled/ 1 OP/6 post -consumer paper State of North Carolina WMEW epartment of Environment, ealth and Natural Resources► , division of Environmental Management j 4t` . James B. Hunt, Jr., Governor Jonathan B. Howes, Secretary A. Preston Howard, Jr., P.E.,'Director 0 rY Y °# RESOURCES A'� COMMUNITY MVEL.kr September 13, 1993 - "William Archer Sandoz Chemicals Corp. P.O. Box 669246 DIVISION NE ENV r sN`'h� , f,.. 411' Charlotte, NC, 25226 WORESVIUE REGIONAL OFFICE Subject: NPDES Permit Modification Permit No. NCO00 375 Sandoz Chemicals Corp. r ` . Archer ...Nlecln County On July 12, 1991, the division of Environmental Management issued NPDES Permit No. NCO004375 to Sandoz Chemicals Corp. Per your request for a modification to the phenols limit at outfall 001, based can recently ,established 30 2 data, the Division is hereby forwarding; the following modification to the subject permit. This permit it modification changes the monthly average phenols limit from 1.8 to 3.9 lbs/day and the daily maximum phenols limit from 36 to 78 ibs/day. Please insert the enclosed effluent pages and discard the old pages. This permit modification becomes effective immediately. All other terms and conditions in the original permit remain unchanged and in fall effect. These modifications are issued pursuant to the requirements of North Carolina General Statute 143-215.1 and the Memorandum of Agreement between North Carolina and the U. S. Environmental Protection Agency elated December 6,1983: If this modification is unacceptable to you, you have the right to an adjudicatory hearing upon written request within thirty (3 days following receipt of this letter. This request must be in the form of written petition, conforming to Chapter 15 B of the North Carolina General Statutes, and filed with the Office of Administrative Hearings, Past Office Drawer 11666, Raleigh, North Carolina i27604. Unless such demand is made, this decision shall be final and binding. f you have any questions concerning this permit, please contact Mr. Greg Nizieh at telephone number 919/733-5083. Sing i/estop ` w d, r., P.E. cc Jim :Patrick, EPA Cc�mpli Central :Piles Regional Offices Asheville Fayetteville Mooresville Raleigh Washington Wilmington Winston-Salem 704/251-620919/4 6-1541 704/ - a l/ 1-4700 / 6-64l 2 %J - 0 i 1 6- 00 Pollution Prevention :Pays P.O. Box 29535, Raleigh, North Carolina 27626-0535 Telephone 9- 3-7015 n Equal Opportunity Affirmative Action Employer A. (). EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL Permit No. NCO004375 During the period beginning on the effective date of the pertnit and lasting until expiration, the Permittee is authorized to discharge from outfall(s) serial number 001. Such discharges shall be limited and monitored by the permittee as specified below: EfflueLij Characteristic. Disc harae Limitation: M_qnjj2rin9 Requirements Ltalday Units (sReclf MeasgreMent Sam is 9j ampd—e Mgn,-"v P-aft-mmaax Mon., An Me Frequenc al , T 1-0-c-aA 1-0—P V X. Flow 3.9 MGD Continuous Recorder I or E BOO, 5 Day, 20 00***"* 852.0 2236.0 Daily" Composite E,U,D Total Suspended Residue 976.0 2928.0 Daily" Composite E NH3 as N***** 651.0 977.0 Daily" Composite E,U,D Dissolved Oxygen Daily" Grab E,U,D Fecal Coliform Monthly Grab E Total Phosphorus Monthly Composite E Total Nitrogen (NO2+NO3+TKN) Monthly Composite E ow Monthly Composite E WAS Monthly Composite r= Manganese Monthly Composite E * Sample locations: E - Effluent, I - Influent, U - Upstream at NC Highway 27, D - Downstream at 1-85 Upstream and downstream samples for BOD5, NH3 as N, dissolved oxygen, temperature, conductivity, and pH shall be collected three times per week during June, July, August, and September and once per week during the remaining months of the year. Daily is defined as everyday except Saturday, Sunday, and legal holidays, Chronic Toxicity (Ceriodaphnia) P/F at 1.8%; March, June, September, and December, See Part 111, Condition D. See Part 111, Condition E. Staging Requirements (Applicable April I - October 31 - See Part 111, Condition F. + Weekly average limit The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units and shall be monitored daily at the effluent, upstream, and downstream by grab sample. There shall be no discharge of floating solids or visible foam in other than trace amounts. A. (). EFFLUENT LRAITATIONS AND MONrrORING REQUIREMENTS FINAL Permit No. NCO004375, During the period beginning on the effective date of the pen -nit and lasting until expiration, the Pennittee is authorized to discharge from outfall(s) serial number 001. (Continued) Effluent Characteristic, DIscharce LImIta la I Monitorina Reculrements Lbg/day 01her Units (specity) Measurement SarnDle *giampl MPA,-A-v4. ID—ally_M" Mon. A ppj.Ly Ma.& Freguency IY-" I—O-qAtlJQP Iron Monthly Composite E Chlorides Monthly Composite E Sulfate Weekly Composite E Mercury Monthly Composite E Conductivity Grab U'D Temperature Daily" Grab E,U,D Total Phenols 3.9 7,8 Weekly Grab E Chronic Toxicity*** Quarterly Composite E Pollutant Analysis"" Annually E 4-chloro-3-methylphenol Quarterly Grab E 2-methylphonol Quarterly Grab E 4,6-dimethylphenot Quarterly Grab E Pentachlorophenol Quarterly Grab E 2,4,5-trichlorophonot Quarterly Grab E L.S. '. $ ...` " 14 .tea UrAe Starry ry 7, y; k/ From { W I V :: N �.aST�w 4'1 WRPieF g yy yr: v f iii-(fF •••((({ I ���"' VVV"' WT q tLd �} ,-^ a r s't aryt c _Jf _ Z 0 r�Clc a78 t' ar'34, 4'AeAJ gYt3 tl -a TO ,9 PS a Y , th-+ - -o r,-,A ' 4rr tit,, ` TA I 1 P.J Z— —,7 0 ON `o f c e` ea • oi` 34 t a.�e r p A '7 ! x er Was. Grp # r. �, . aa3-s m WA4cr � o —,,or �Ctaaciar+ e4OM41 .1— y i pp r t .S4, ecr`i1i�"r' 3 // h l+cw` r ` Lard 7` G ,�j} im, dl:�r� fir" FS N( , ,, X ' iIq RV y swp f t x t N. Q DEPT, OF ATU L TIESOURCES AND COMMUNITY DEVELOPMENT ,f �... M1 r }N ykr! t "Y i^ a� ,y**. � ��� � t "'t 'g• lo OF tuf'a£.;KtK0iliit UV0,1XI State of North ar olina OOREt�ILLE RtGti R tff t Departrrrent of Ir± nvir°onnient,'Health and Natnr=al Resources Division of Environmental Management 512 North Salisbury Street *'Raleigh, North Carolina 27611 Jaynes G. Martin, Governor George T. Everett; Ph.D. William W. Coney, Jr., Secretary Director January 27 1992 CERTIFIED MAID RET RN RE EIPT RE E� r. W, M. Archer Sandoz Chemicals Corporation PO Box 00924E Charlotte, NC 28266 Subject: NPDES Permit No. N 0004375 Sandoz Chemicals Corporation Mecklenburg County Dear Mr. Archer. In accordance with your Petition for Contested Case Tearing filed on ;august 7, 1991, we are forwarding herewith a modification to the subject permit. This modification is to delete the mercury limit in the permit and to replace it with a monthly monitoring requirement. Attached are revised effluent pages for outfall 001 only. These sheets should be placed in the permit and the current outfll 001 sheets discarded. All other terms and conditions contained in the original permit remain unchanged and in full effect. These modifications are issued pursuant to the requirements of North Carolina general Statute 1-215.1 and the Memorandum of Agreement between North Carolina and the U. S. Environmental Protection Agency dated December 0, 1981 If any terms or conditions adjudicated that were resolved by this modification are unacceptable to you, you should notify us within thirty (30) days following receipt of this letter. Unless such demand is made, this decision shall be final and binding. If this permit modification is acceptable, Sandoz Chemicals Corporation must complete the attached Notice of Withdrawal of Petition form within 30 days of receipt of this `modification and submit one copy to the Attorney General's Office as specified on the withdrawal form and one copy to this division. Pollutiun Prevert ion Pays 11,0. Box ;.9535, bider h, North Carolina 27626-05:35 Teleplione 19- 7 33-7015 An Equal Opportunity Affirmarive Action Employer a � ! +r • * �: PVATEE OF NORTH CARt LINA IN THIS OFFICE F ADMINISTRATIVE HEARINGS COUN OF FILE NO. Petitioner, NOTICE OF WITHDRAWAL } OF PETITION DEPARTMENT OF ENVIRONMENT � DIVISION OF Respondent. Petitioner hereby withdraws its pe No further proceedings are needed or r captioned above. This the day of CERTIFICATE ,r a contested ease hearing. J to resolve the contested case �ERVICE follows: Attorney General's Office Environmental Protection Section PCB Box 62 Raleigh, NC 27602-062 (Date) Petitioner/Attorney for Petitioner AN 0 2 1991 State of North Carolina 11: 42 De t of Environment, Health, and Natural Resources it ti Division of Environmental Management 10*04 orth Salisbury Street - Raleigh, North Carolina 27611 James G. Martin, Governor George T. Everett, Ph. D. William W. cotseyJr., Secretary Director October 15, 1991 MELAQBMQUM To: Daniel C. Oakley From: George T. Everett Subject: Permit Adjudication Sandoz Chemical Corporation 91 EHR 0746 Permit No. NC9004375 Mecklenburg County On July 12, 1991, the DEM issued a renewal permit to Sandoz Chemical Corporation. As result of issuance of the permit, Sandoz adjudicated the permit base on the two following concerns: I . There was insufficient time to allow installation of control equipment to meet the limits for 2,4-Dinitrophenol and 4-Nitrophenol; and 2. The impossition of the limit for mercury. understanding of the issue with this item. Therefore, there will be no furthur idiscussio, item. After a second review of the permit file, the DEM will concur with chan(, mercury limit to monthly monitoring only for the duration of the permit to resolve the Due to the fact that mercury has been detected in the permit over the past five years, t feels that monitoring for duration of the permit is a fair resolution of the adjudication. monitoring is not a burden for a company the size of Sandoz. The DEM will wait fo guidance from you before preparing a final permit. If you have any questions, please contact Mr Date Overcash at (919) 733-50 Pollution Prevention Pays P.O. Box 29535, Raleigh, North Carolina 27626-0535 Telephone 919-733-7015 An Equal Opportunity Affirmative Action Employer t Permit No. NCO004375 STATE OF NORTH CAROL. NA DEPARTMENT OF ENVIRONMENT, HEALTH, AND NATURAL RESOURCES DIVISION OF ENVIRONMENTAL. MANAGEMENT PERMIT TO DISCHARGE WASTEWATER UNDER THE DISCHARGEI In compliance with the provision of North. Carolina General Statute 1 3- 1 .1, other lawful standards<and regulations promulgated and adopted by the North Carolina Environmental Management Commission, and the Federal Water PollutionControl Act, as amended, Sandoz Chemicals Corporation is hereby authorized to discharge wastewater from a fatality -located at Mt Holly Plant NC Highway 2 north of Charlotte Mecklenburg County to receiving waters designated as the Catawba River in the Catawba River Basin in accordance with effluent limitations, monitoring requirements, and other conditions set forth in Parts I, II, and III hereof. This permit shall become effective This permit and'the authorization to discharge shall expire at midnight on June 30, 199 Signed this day'. t �.� u n' George T. Everett, Director Division of Environmental Management By Authority of the Environmental Management Commission pppppp� Permit No. ' NCO004375 SUPPLEMENT TO PERMIT COVER SBEET Sandoz Chemicals Corporation is hereby authorized to: l . Continue to operate a 3.9 M ilk wastewater treatment facility ioutfall 00 l consisting of two basins for biological waste treatment, stormwater equalization basin for nonalkaline wastewater, to water equalization basins for alkaline wastewater, gravity secondary clarifiers, acid neu lion, tyy prim cl fxers, °stripper, sludge dewatering effluent dishing pond, staged discharge facility ilud rt effluent storage, d host aeration, d, treatherbicide an " w tewater `th discharge to the acid sewer d thence t+ the 1VlClD treatment pl t de der outfall t�}l outfall (1€? at a site located at Mt. holly Plant, N highway i, north of Charlotte, � , klenb Co ty {See of this Permit), and . After receiving an Authorization to Construct the Division' of Environmental Management, construct additional facilities necessary for the pretreated pesticide manufacturing wastewater discharge and, relocate outfail tail discharge point with no change in limitations required, and, 3. Discharge from said treatment works at the location specified on the attached map into the Catawba River which is classified Class WS-lll waters in the Catawba River Basin. I A. ( ). EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL Permit it No. NCO004375 During the period beginning on the effective date of the permit and lasting until expiration, the Permittee is authorized to discharge from outf ll(s) serial number 001. Such discharges shall be limited and monitored by the permittee as specified below: 1 Effluent harct+eristis 1211rhgtae Limitations i Units s eclfv) Measurement Sarnpl * am l ► - Man. Aver, Cam? _Max.Freauencv Lxple Locatipr� Flow 3.9 MGD Continuous Recorder !car OD, 5 Day, 20 OC***** 852.0 2236"0 Daily" Composite E,U,D Total Suspended Residue 976.0 2928.0Daily" Composite NH3 as N***** 651.0 977.0 Daily** Composite E,U,D Dissolved Oxygen Daily" grab E,U,D Fecal Coliform Monthly Crab Total Phosphorus Monthly Composite Total Nitrogen (NCB +NO3+TKN) Monthly Composite E OCD Monthly Composite MBAS Monthly Composite E Manganese Monthly Composite E: * Sample locations: E - Effluent, I - Influent, U - Upstream at NC" Highway 27, D - Downstream f" -85 Upstream and downstream samples for BOD5, NH3 as N, dissolved oxygen, temperature, conductivity, and pH shall be collected three times per week. during June, July, August, and September and Dance per week during the remaining months of the ;year. Daily is defined as every day except Saturday, Sunday, and legal holidays. * Chronic Toxicity (C eriodaphnia) P/E at 1 "S Mare, June, September, and December, See fart III, Condition D. * * See Part III, Condition E. * Staging Requirements (Applicable April 1- October 31) - See Part III, Condition F. + Weekly average limit The pH shall not be less than 6.0 standard units near greater than 9.0standard units and shall be monitored daily at the effluent, upstream, and downstream by grab sample. Theme shall be no discharge of floating solids or visible foam in ether than trace amounts. A. (). EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL Permit No. NC:O00437 During the period beginning on the effective date of the pertnit, and lasting until expiration, the Pertrrittee is authorized to discharge from outfall(s) serial number 001. (Continued) Effluent Characteristics Discharge Limitations Monitorina Reauirements LtiaLO@y Other Units (§pe21fyj Measurement i * a l an,__Ayg,, pgjjy__M" Mon. Ava. DAlly Max. lire ene T199AILOJI Iron Monthly Composite Chlorides Monthly Composite Sulfate Weekly Composite E Mercury .022+ 2.4 ucgil Weekly Composite E Conductivity Grab U,D Temperature Daily" Grab E,U,D Total Phenols 1.8 3.6 Weekly Grab Chronic Toxicity**" Quarterly Composite Pollutant Analysis`« Annually 4-chl aro-3- ethylphenol Quarterly Grab E -methylphenol Quarterly Grab E 4,6-dimethylphenol Quarterly Grab E Penthlorohenol Quarterly Grab E 2,4,-trichlcrophenol Quarterly Grab E A. (). EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL Permit No. NCO00 37 During the period beginning on the effective date of the permit and lasting until expiration, the Pe' °tree is authorized to discharge from outfall(s) serial number 002. Such discharges shall be limited and monitored by the permittee as specified below: Effluent Characteristics Discharge Limitations Monitorina U ita (AP.ORINI Measurement Sarnrtie *a Mo. An. PAlly—Ma Mon. Ava. pAlly Max. Freauencv fi e Lqglallgm Flow Hatch Recorder Total Suspended Residue 22.0 73.0 Weekly Composite" E OCD 108.0 1 6.O Weekly Composite" E SCC, 5 Clay, 20 "C 19.0 89.0 Weekly Composite" E *Sample locations: E - Effluent, I - Influent Composite samples may be done as grab samples if the discharge is on a batch basis. 'J 74 PAL 16 1991 State of North Carolina Department of Environment, Health and Natural Resour Division of Environmental Management 512 North Salisbury Street - Raleigh, North Carolina 27611 James G. Martin, Governor George T. Everett, Ph,D William W. Cobey, Jr., Secretary Director t' 4k Bill Archer P. 0. Box 669246 Charlotte, NC 28266 Dear Mr. Archer: In accordance with your at) July 12, 1991 Subject: Pen -nit No. NCO004375 Sandoz Chemicals Corporation Mecklenburg County ,and Resources, Coastal Area Management Act ortinyother Federal or Local governmental pen -nit fiat may be required, If you have any questions concerning this permit, please contact Ms. Rosanne Barona at elephone number 919/733-5083. Sincerely, Original Signed By Donald Safit for c: Mr. Jim Patrick EPA George T. Everett Aqi���fte Pollution Prevention Pays P.O. Box 29535, Raleigh, North Carolina 27626-0,535 Telephone 919-733-7015 An Equal Opporamity Affinnative Action Employer Permit No. NCO004 7 STATE OF NORTH CAROL_INA DEPARTMENT OF ENVIRONMENT, HEALTH, AND NATURAL RESOD CI�-S,�- �� DIVISION O F ENVIRONMENTAL MANAGEMENT � � � ,�> . 'Ifr LERMIT 6TC DISCHARGE WASTEWATER UNDER THE 1991 NAC to T A I I, xttt >i, uFfICE1.1 In compliance th the provision of North Carolina General Statute 14 - 1 .1, other lawful standards and regulations promulgated and adapted by the North Carolina Environmental Management Commission, and the Federal "water Pollution Control .Act, as amended Sandoz Chernicals Corporation is hereby authorized to discharge wastewater from a facility located at t. holly Plant NC Highway 2 north of Charlotte Mecklenburg County to receiving waters designated as the Catawba River in the Catawba liver Basin in accordance with effluent limitations, monitoring requirements, and ether conditions set forth in Parts I, 11, and III hereof. This permit shall become effective September 1, 1991 This permit and the authorization to discharge shall expire at midnight on August 31,1996 Signed this day July 12, 1991 orietnat signed 8Y t)onald Setrit tOr George T. Everett, Director .Division of Environmental Management By Authority of the Environmental Management Commission Permit No. NCOW4375 SUPPLEMENT To PERMIT COVER SHEET Sandoz Chemicals Corporation is hereby authorized to: 1. Continue to operate a 3.9 MGD wastewater treatment facility (outfall basins for biological 001) consisting of two waste treatment, stormwater equalization basin for nonalkaline wastewater, StOrmwater equalization basins for alkaline wastewater, gravity secondary clarif $ neutralization, gravity primary iers acid clarifiers, air stripper, sludge dewatering, effluent polishing pond, staged discharge facility including effluent storage, and post aeration, and, treat herbicide manufacturing wastewater, with discharge to the acid sewer and thence to the 3.9 MGD treatment plant described under outfall 001 (outfall 002), at a site lo aced at M Holly P1 t, NC ghway 2M 7, north of Charlotte, Mecklenburg County (See Part c L an FE of this Permit), and 2. After receiving an Authorization to Construct from the Division of Environmental Management� construct additional facilities necessary for the pretreated Pesticide manufacturing wastewater discharge and, relocate outfall 001 discharge point with no change in limitations required, and, 3. Discharge from said treatment work.-, at thp �"C"Wv'a j\jVuroasm. During the period beginning on the effective date of the permit and lasting until expiration, the Permittee is authorized to discharge from outfall(s) serial number 001. Such discharges shall be limited and monitored by the permittee as specified below. »� Effluent Characteristics Disehar e Limitations Monttorin f auirements , Lb/dater Units s ecifr} Measurement Sample *Sam - le Mon. Arc. l it Mix Mon. Auc�. C?oiier Max. requerrc�r � Location Flow ` 3.9 WD Continuous Recorder l or P BOD, 5 Day, 20 OC"'" 352.0 2236.0 Daily— Composite E,U,I Total Suspended Residue 976.0 2923.O D-a i l y * � Composite E NH3 as N*`*,. 6 1.O 977.E Daily— Composite E,U,C Dissolved Oxygen Daily— Crab E,U,D Fecal Coliform Monthly grab E Total Phosphorus Monthly Composite E Total Nitrogen (N( 2+NO3+TK ) Monthly Composite E COD Monthly Composite E MBAC Monthly Composite E Manganese Monthly Composite E * Sample locations: E - Effluent, I - Influent, U - Upstream at NC Highway 27, D - Downstream at I. 5 Upstream and downstream samples for BOD5, NH3 as N, dissolved oxygen, , temperature, conductivity, and pH shall be collected three times per week during ,Tune, July, August, and September and once per week during the remaining months of the year. Daily is defined as every day except Saturday, Sundry, and legal holidays. Chronic Toxicity (Ceriodaphnia) P/F at 1.8% March, June, September, and December-, See. Part III, Condition I . See Part II, Condition E, ***** Staging Requirements (Applicable April I - October 31) - See Part IfI, Condition F. + Weekly average limit The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units and shall be monitored daily at the effluent, upstream, and downstrearn by grab sample. There shall be no discharge of floating solids or visible foam in rather than trace amounts itmiURAX:OtherMeasurement Sample *Sample Mon. Avg. Daily Mon. Avg. Deily Max. A:- Max Frequency Ty-pe Location Iron Monthly Composite Chlorides Monthly Composite E Sulfate Weekly Composite E Mercury Monthly Composite E Conductivity Grab U,D Temperature Daily— Grab E,U,D Total Phenols 1 -8 3i-6 Weekly Grab E Chronic Toxicity— Quarterly Composite E Pollutant Analysis—* Annually E 4-chloro-3-methylphenol Quarterly Grab E 2-methylphenol Quarterly Grab E 4,6-dimethylpheriol Quarterly Grab E Pentachlorophenot Quarterly Grab E 2,4,5-trichlorophenol Quarterly Grab E ,uunng the period beginning can the ettecttve date of the permit and lasting until expiration, the Permittee is authorized to discharge from outf ll(s) serial number 002. Such discharges shall be limited and monitored by the permittee as specified below: " Effluent Characterlstics Mon1joring Requirements Lbs/dayUnits a eclfy) Measure ant sample *raample Mcsn., An. Man. Am palL, a. Frequency Type 29211 Flow Batch Recorder E Total Suspended Residue 22.0 733.0 Weekly Composite" E OCD 108.0 156.O Weekly Composite" E OCt 5 Day, 20 °C 19.0 89.0 Weekly Composite" E *Sample locations: ' E - Effluent, I - Influent * Composite samples may be done as grab samples if the discharge is on a batch basis. Y It X EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL Ni During the period beginning on the effective date of the permit and lasting until expiratioi Pearnittee is authorized to discharge frorn outfall serial number 001. (Continued) Such di Shall be limited and monitored by the perniittee as specified below. Effluent Characteristics Mon. Avg.; Daily Max, Measurement Sample *w lbs/day lbs/clay Frequency Type Li Ac:enaphthene** 0,39 0.50 Quarterly Grab E' Arylonitrile 1.69 430 Quarterly Grab E Benzene 0.75' 2.70' Quarterly Grab E Carbon Tetrachloride 0.32 0.67' Quarterly Grab E Chlorobe,nzene 0.31 0,57' Quarterly Grab E 1,2,4-Tr chlorobenzene 1.20` 2.46' Quarterly Crab E Hexachlorobenze,ne 0.26 0,49 Quarterly Grab E 1,2-Dichloroethane 1.20 3.71 Quarterly Grab E 1,1,1-Trick loroethane 0.37 0.95' Quarterly Crab E Hexachloroethane 039 0,95 Quarterly Grab E 1,1-Dichloroethane 0.39 1.04 Quarterly Grab E' 1, 1, 1 -TrIch loroethane 0.37 0,95 Quarterly Grab E Chloroethane 1.3 4.72 Quarterly Grab E Chloroform 0.37 0.81 Quarterly Grab E 2-Chlorophen l 0.62 1.95' Quarterly Grab E 1,-Dichlorobenzene 1.57 332 Quarterly Grab E 1,3-Dielllorobenzene 0.62 0.90 Quarterly Crab E IA-Dichlorobenzene °° 0.31 0,57 Quarterly Grab E 1, 1 -Dichloroethylene 0,28 0.44 Quarterly Grab E 1,2-trans-Dichloroethylene 0.37 0.95 Quarterly Grab E 2,4-Dichloroplienol 0.77 2.22 Quarterly Grab E 1,2-Dichloropropane 2.69` 4.05 Quarterly Grab E 1,3-D1chIoropropyletie 0.51 0.77 Quarterly Grab E 2,4-DIinethylphen o1 0.36 0.71 Quarterly Grab E 2,4-Dlnitrotoluene 1.99 5.03 Quarterly Grab E 2,6-Dinitrotoluene 4.40 11,28 Quarterly Grab E Eth lbenzene 0.65 2.20 Quarterly Grab E Fluoranthene OA7 1.20 Quarterly Grub E Methylene Chloride 0,70 1,57 Quarterly Grab E Methyl Chlori& 1,51 334 Quarterly Grab E 1lexachlorobutadiene 0,35 0,86 Quarterly Grub E Naphthalene** OA5 0.50 Quarterly Grab E Nitrobenzene 0.48 1.20 Quarterly Grab 2-Nitrohenol 1.3 108 Quarterly Grab E 4-Nitrophenol` 2,17 3,74 Quarterly Grab 24-Dintrophenol 2.15 3.71 Quarterly Grab E 4;6-Dinitro-o-cresol 1.55 5,50 Quarterly Grab E Phenol 1,6 2.70 Quarterly Grab E Bis(2-ethyIhexy1)phthaIate 1,81 4,91 Quarterly Grab E Di-n-butyl phthalate 0.4 1.00 Quarterly Grab E Diethyl phthalate 1.43 3.57 Quarterly Grab E L irnethyl phthalate 0,33 0.33 Quarterly Grab E B nzo(a)anthracene." 0.31 OJO Quarterly Grab ' E Benzo(a)pyrene*" 0.40 t1J0 Quarterly Grab' E ((7,ontinued) Effluent Characteristics Mon. Avg. Daily Max, Measurement Sample *S lbs/ciay lbs/day Frequency Type U, 3,4- Benzofluoranthene* OAO 0,50 Quarterly Grab E Benzo(k)fl uoranthene 0.39 UO Quarterly Grab E Chrysene" 0.39 UO Quarterly Grab < E Acenaphthylene** 0.39 UO Quarterly Grab E Anthracene" 039 0,50 Quarterly Grab E Fluorene" 039 0.50 Quarterly Grab E Phenanthrene" 039 0.50 Quarterly Grab E Pyrene** 0,44 0.50 Quarterly Grab E Tetrachloroethylene 0.39 0.99 Quarterly Grab E Toluene 0.53 L63 Quarterly Grab E Trichloroethylene 0.37 0.95 Quarterly Grab E Vinyl Chloride L82 4.70 Quarterly Grab E Total Cyanide 7.39 9,01 Quarterly Grab E *Sample Location: E-Effluent **These parameters are water -quality limited, t n B Scbgdule of Compliano P RT I accordance with the following schedule; Permittee shall comply with Final Efflux permit unless specified below. Urnitations specified for discharges in agitations by the effective date of the existing facilities at optimum _ efficiency. . No later than 14 calendar days following a date identified in the above schedule of compliance, the perinittee shall submit either a report of progress or, in the case of speciti actions being required by identified dates, a written notice of compliance or noncompliat In the latter case, the notice shall include the cause of noncompliance, any remedial actin taken, and the probability of meeting the next schedule requirements. Pant 11 Page I of 14 PART 11 STANDARD CONDITIONS ITIc N FOR NP E a PERMITS SECTION N A. UEFINfTIONS . Permit IssuingAutbority The Director of the Division of Environmental Management. . LEM, car Division Means the Division of Environmental Management, Department of Environment, Health and Natural Resources, 3. EC Used herein means the: North Carolina Environmental Management' Commission.. . Act or "the Act" The Federal Water Pollution; Control Act, also known as the Clean Water Act, as amended, 33 USC 1251, et. sett: 5. M ss/I7,ty Mettsuremen ,s a. The "monthly average discharge" is defined as the total mass; of all daily discharges sampled and/or measured during a calendar month on which daily{ discharges are xfaua, gLIIV a UUIIIa�; bmat tatvlam. it I" Inuictoi ,all ari mtmetrcl mean iounu oy' weights of the pollutant found each day of the month and then dividing, this: number of days the tests were reported. The limitation is identified as Average" in Part I of the permit b. The "weekly average discharge" is defined as the total mass of all daily r 'sampled and/or measured during; the calendar week (Sunday - Saturday) on discharges are sampled and tr easured, divided by the number of daily a sampled and/or measured during; such week. It is, therefore, an arithmetic n- by adding the weights of pollutants found each day of the week and then di sum by the number of days the tests were reported. This limitation is id "Weekly Average" in Pat I of the pen -nit. c. 'The '"maximum daily discharge" is the total mass (wei during; a calendar clay. If only one sample is taken durir of pollutant calculated from it is the "maximum daily i identified as "Daily Maximum," in Part I of the permit. Part 11 Page 2 of 14 d. The "average annual discharge" is defined ais the total mass of all daily discharges sampled and/or measured during the calendar year on which daily discharges are sampled and measured, divided by the number of daily discharges sampled and/or measured during such year. It is, therefore, an arithmetic mean found by adding the fl- number of days the tests were reported. This limitation is defined as "Annual Average" in Part I of the permit. 6. Concentration Measurement a. The "average monthly concentration," other than for fecal coliform bacteria, is the sum of the concentrations of all daily discharges sampled and/or measured during a calendar month on which daily discharges are sampled and measured, divided by the number of daily discharges sampled and/or measured during such month (arithmetic mean of the daily concentration values). The daily concentration value is equal to the concentration of a composite sample or in the case of grab samples is the arithmetic mean (weighted by flow value) of all the samples collected during that calendar day. The average monthly count for fecal coliforin bacteria is the geometric mean of the counts for samples collected during a calendar month. This limitation is identified as "Monthly Average" under "Other Units" in Part I of the permit. b. The "average weekly concentration," other than for fecal coliform bacteria, is the sum of the concentrations of all daily discharges sampled and/or measured during a calendar week (Sunday/Saturday) on which daily discharges are sampled and measured divided by the number of daily discharges sampled and/or measured during such week (arithmetic mean of the daily concentration values). The daily concentration value is equal to the concentration of a composite sample or in the case of grab samples is the arithmetic mean (weighted by flow value) of all the samples collected during that calendar day. The average weekly count for fecal coliform, bacteria is the geon-letric mean of the counts for samples collected during a calendar week. This limitation is identified as "Weekly Average" under "Other Units" in Pan I of the permit. c. The "maximum daily concentration" is the concentration of a pollutant discharge during zn a calendar day. If only one satriple is taken during any calendar day the concentration of pollutant calculated from it is the "Maximum Daily Concentration". It is identified as "Daily Maximum" under "Other [Jnits" in Part I of the pen -nit. d. The "average annual concentration," other than for fecal coliform bacteria, is the sum of the concentrations of all daily discharges sampled and/or measured during a calendar year on which daily discharges are sampled and measured divided by the number of daily discharges sampled and/or measured during such year (arithmetic mean of the daily concentration values). The daily concentration value is equal to the concentration of a composite sample or in the case of grab samples is the arithmetic mean (weighted by flow value) of all the samples collected during that calendar day . The average yearly count for fecal coliform bacteria is the geornetric mean of the counts for samples collected during a calendar year, e. The "daily average concentration" (for dissolved oxygen) is the minimum allowable amount of dissolved oxygen required to be available in the effluent prior to discharge averaged over a calendar day. If only one dissolved oxygen sample is taken over a calendar day, the sample is considered to be the "daily average concentration" for the discharge. It is identified as "daily average" in the text of Part 1. Fait 11 Page 3of14 f. The "quarterly average concentration" is the, average of all samples taken over a calendar quarter. It is identified as "Quarterly Average Limitation" in the text of Part I of the permit. g. A calendar quarter is defined as one of the following distinct periods. January through March, April through June, July through September, and October through December. }ther Measurements a. Flaw, (MGD). The flow limit expressed in this permit is the 24 hours average flaw, averaged monthly. it is determined as the arithmetic mean of the total daily flows recorded during the calendar month. b. An "instantaneous flow measurement" is a measure of flow taken at the time of sampling, when both the sarnple and flow will be representative of the total discharge. . A "continuous flow measurement" is a measure of discharge flow from the facility which occurs continually without interruption throughout the operating hours of the facility. Flaw shall be monitored continually except for the infrequent times when there may be no flaw or for infrequent maintenance activities oil the flow device. . Types, of Samples a. Composite Sample: A composite sample shall consist of: (1) a series of grab samples collected at equal time intervals over a 24 hour period o discharge and combined proportional to the rate of now measured at the time of individual sample collection, or () a series of grab samples of equal volume collected over a 24 hour period with the time intervals between samples determined by a preset number of gallons passing the sampling point. Flow measurement between sample intervals shall be determined by use of a flow recorder and totalizer, and the present gallon interval between:: sample collection fixed at no greater than 1/24 of the expected total daily flaw at the treatment system, or (3) a single, continuous sample collected over a 24 hour period proportional to the rate of flow. In accordance with (1) above, the time interval between influent grab samples shall be no greater than once per hour, and tine time interval between effluent grab samples shall be no greater than once per hour except at wastewater treatment systems having a detention time of greater than 24 hours. In such cases, effluent grab 'samples may be collected at time intervals evenly spaced over the 24 hour period which are equal i number of hours to the detention time of the system in number of days. However, in no case may the time interval between effluent grab samples be greater than six (o) hours nor the number of samples less than four (4) during a 24 Hour sampling period. b. Grab Sample: Grab samples are individual samples collected over a period of time not exceeding 15 minutes; the grab sample can be taken manually. . Calculation of Means a Arithmetic Mean: The arithmetic mean of any set of values is the Summation of the individual values divided by the number of individual valves. Part 11 Page 4 of 14 b. Geometric Mean, The geometric mean of any set of values is the Nth rot of the product of the individual values where N is equal to the number of individual values. The geometric mean is equivalent to the antilog of the arithmetic mean ofthe logarithms of the individual -values. For purposes of calculating the geometric mean, values of zero (0) shall be considered to be one (1). c. Weighted by Flog 'Value: Weighted by flow value means the summation of each concentration times its respective flow divided by the summation of the respective flown. 10. to lender Day calendar day is defused as the period from midnight of one day until midnight of the next days However, for purposes of this permit, any consecutive 24-Maur period that reasonably represents the calendar day may be used for sampling. 11. Hazardous Substance A hazardous substance means any substance designated under 40 CFR Part 116 pursuant to Section 311 of the Clean Water Act. 12. Toxic Pollutant' A toxic pollutant is any pollutant listed as toxic under Section 307(a)(1) of tlae Clear) Water Act. E Tl N B. GENERAL CONDITIONS I. Duty to C arrapl The permittee must comply with all conditions of this permit. Any permit noncompliance constitutes a violation of the Clean Water Act and is ,grounds for enforcement action, for permit termination, avocation and reissuan e, or modification; or denial of a permit renewal application. a. The permittee shall comply with effluent standards or prohibitions established under section 307(a) of the Mean Water Act for toxic pollutants and with standards for sewage sludge use or disposal established under section 40(d) of the Clean Water Act within the time provided in the regulations that establish these standards or prohibitions, even if the permit has not yet been modified to incorporate the requirement, b. The Clean Water Act provides than any parson who violates a permit condition is subject to a civil penalty not to exceed $2 ,000 per dray for each violation. Any person who negligently violates any hermit condition is subject to criminal penalties of $2,500 to $25,000 per clan= of violation, or imprisonment for not more than 1 year, or both. Any person who knowingly violates permit conditions is subject to crinrainal penalties of $5,00 to $50,000 per day of violation, or imprisonment for not more than 3 years, or both. Also, any person who violates a permit condition may be assessed an administrative penalty not to exceed $10,000 per violation with the maximum amount not to exceed $125,000. C Ref: Section 309 of the Federal Act 33 U.S.C. 1319 and 40 CFR 122.41 (aa)1 Part 11 Page 5 of 14 c. Understate law, a daily civil penalty of not more than ten thousand dollars ($10,000) per violation may be assessed against any person who violates or fails to act in accordance with the terms, conditions, or requirements of a permit. [Ref: North Carolina General Statutes § 143-215.6 (a)] 2. Duty to Mitigate The permittee shall take all reasonable steps to minimize or prevent any dischargc violation of this permit which has a reasonable likelihood of adversely affecting hurl health or the environment. 3. Civil and Criminal Liability y be temporarily suspended. to preclude the institution of any legal as fish kills, even though the responsibility for effective compliance may be temporarily suspended. 5. Pr �Qpertv Rights The issuance of this permit does not convey any property rights in either real or personal property, or any exclusive privileges, nor does it authorize any injury to private property or any invasion of personal rights, nor any infringernent of Federal, State or local laws or regulations, 6. Onshore or Offshore Conali �,tion This permit does not authorize or approve the construction of any onshore or offshore physical structures or facilities or the undertaking of any work in any navigable waters. 7. SLyerabilit, y The provisions of this permit are severable, and if any provision of this permit, or the application of any provision of this permit to any circumstances, is held invalid, the application of such provision to other circumstances, and the remainder of this permit, shall not be affected thereby. Part 11 Page fa of 1 . 12izty 1a2 Provide lnfo ation The pennittee shall furnish to the Permit Issuing Authority, within a reasonable time any information which the Permit Issuing Authority may request to determine whether cause exists for modifying, revoking and reissuing, or terminating this permit or to determine compliance with this permit. The permittee shall also furnish to the Permit Issuing Authority upon; request, copies of records; rewired to be kept by this permit. q. Duty to Rear a1 If the permittee wishes to continue an activity regulated by this permit after the expiration date of this permit, the permittee must apply for and obtain a new permit. 10. Expiration f Pgrmil The permittee is not authorized to discharge after the expiration date. In order to receive automatic: authorization to discharge beyond the expiration date, the permittee shall submit such information, forms, s, and fees as are required by the agency authorized to issue permits no later than 180 days prior to the expiration date. Any discharge that has not requested renewal at least 180 days prior to expiration, or any discharge that sloes not have a permit after the expiration and has not requested renewal at least 180 days prior to expiration, will subject the permittee to enforcement procedures as provided in iNCGS'143-215.6 and 33 USC 1251 et. seq. 11. Si tor, v Re ,u rement All applications, reports, or information submitted to the Permit Issuing Authority shall be signed and certified, a. All permit applications shall be signed as follows: (1) For a corporation. by a responsible corporate officer. For the purpose of this Section, a responsible corporate officer means: (a) a president, secretary, treasurer or vice president of the corporation in charge of a principal business function, or any other person who performs similar policy or decision making functions for the corporation, or (b) the manager of one or more manufacturing production or operating facilities employing more than 250 persons or having gross annual sales or expenditures exceeding 25 million (in second quarter 1980 dollars), if authority to sign documents has been assigned or delegated to the manager in accordance with corporate procedures. () For a partnership or sole proprietorship: by general partner or the proprietor, respectively, or (3) For a municipality, State, Federal, or other public agency: by either a principal executive officer or ranking elected official. b. All reports required by the permit and other information requested by the Permit Issuing Authority shall be signed by a person described above or by a duly authorized representative of that person. A person is a duly authorized representative only if: (1) The authorization is made in writing by a person described above. (2) The authorization specified either an individual or a position having responsibility for the overall operation of the regulated facility or activity, such as the position of plant manager, operator of a well or well field, superintendent, a position of Part 11 Page 7 of 14 uivalent responsibility, or an individual or position having overall responsibility I to the Permit Issuing Authority. iment under paragraphs a. or b. of this sei document and all attachments were pref • 13. P(mil ML)difigatim. Revocation and Reissuance, or Tern-nnation Subchapter iH .0100; and North 'Caroli na General Statute 143 - -215 , w I -- et. a]. 14-2r-eyiolis Permits All previous National Pollutant Discharge Elimination System Permits issued to this facility, whether for operation or discharge, are hereby revoked by issuance of this permit. The conditions, requirements, terms, and provisions of this permit authorizing discharge under the National Pollutant Discharge Elimination System govern discharges from this facility. SECTION C. OPERATION AND MAINTENANCE OF POLLUTION CONTROLS I . Certified Operator Pursuant to Chapter 90A-44 of North Carolina General Statutes, the permittee shall employ a certified wastewater treatment plant operator in responsible charge (ORC) of the wastewater treatment facilities. Such operator must hold a certification of the grade equivalent to or greater than the classification assigned to the wastewater treatment facilities. The permittee shall notify the Division's Operator Training and Certification Unit within thirty days of any change in the ORC status. % 1X . RLoj2er The perm: treatment permittee` Part 11 Page 8 of 1 Lion gnj €Vl intenancg similar systems which are installed by a permittee only when the operation is necessary achieve compliance with the conditions of the permit. . N=d o Halt gr &dggg not a Defense It shall not be a defense for a permittee in an enforcement action that it would have bt necessary to halt or reduce the permitted activity in order to maintain compliance with condition of this permit. 4 ftpijasin g of IreatmgnL Facilities a. Definitions (1) "Bypass" means the known diversion of waste streams from ally portion of treatment facility including the collection system,; which is not a designed established or operating mode for the facility. () "Severe property damage" means substantial physical damage to property, darn,, to the treatment facilities which causes them to become inoperable, or substan and permanent loss of natural resources which can reasonably be expected to oc in the absence of a bypass. Severe property damage does not mean economic b caused by delays in production. b. Bypass not exceeding limitations. The permittee may allow any bypass to occur which does not cause effluent limitatzc to be exceeded, but only if it also is for essential maintenance to assure effi6 operation, "These bypasses are not subject to the provisions of Paragraphs c. and d. this section c. Notice (1) Anticipated bypass, if the permmttee knows in advance of the need for a bypas, I I"Il a"ULIA It, Fi J.tll 11 t14.4,:RI FWal. IUA = Ut. 4V+U.%t tV1I #1U. y T:: UV uIV UIk CA%,V WI U.V L'.Y F:"Ol including an evaluation of the anticipated duality and affect of the bypass. () Unanticipated bypass, The pen°nittee shall submit notice of an unanticipated bypass as required in fart 11 E. 6. of this permit. (4-hour notice); d. Prohibition of Bypass (1) Bypass is prohibited and the Permit Issuing Authority may take enforcement actioi against a permittee for bypass, unless: (a) Bypass was unavoidable to prevent loss of life, personal injury or surer( property damage; Part II Page 9 of 14 (o) There were no feasible alternatives to the bypass, such as the use of auxiliary treatment facilities, retention of untreated wastes or maintenance during normal periods of equipment downtime. This condition is not satisfied if adequate backup equipment should have been installed in the exercise of reasonable engineering judgment to prevent a bypass which occurred during normal periods of equipment downtime or preventive maintenance; and c) The perntittee submitted notices as required under Paragraph c. of this section. () The Permit Issuing Authority may approve an anticipated bypass, after considering its adverse affects, if the Permit Issuing Authority determines that it will meet the three conditions listed above in Paragraph d. (l) of this section. . 112sets a. Definition. "Upset " means an exceptional incident in which there is unintentional and temporary noncompliance with technology based permit effluent limitations because of factors beyond the reasonable control of the permittee. An upset does not include noncompliance to the extent caused by operational error, improperly designed treatment facilities, inadequate treatment facilities, lack of preventive maintenance, or careless or improper operation. b. Effect of an upset. An upset constitutes an affirmative defense to an action brought for noncompliance with such technology based permit effluent limitations if the requirements of paragraph c. of this condition are met. No determination made during; administrative review of claims that noncompliance was caused by upset, and before an action for noncompliance, is final administrative action subject to judicial review. c. Conditions necessary fora demonstration of upset A perittee who wishes to establish the affirmative defense of upset shall demonstrate, through properly signed, contemporaneous operating logs, or other relevant evidence that: (a) An upset occurred and that the permittee can identify the cause(s) of the upset, (b) The pennittee facility was at the time being; properly operated, and () The permittee submitted notice of the upset as required in :Part lI E. 6� (b) (B) of this permit. (d) The permittee complied with any remedial measures required under Part 11, B. 2. of this permit d. Burdett of proof. In any enforcement proceeding the permittee seeking to establish the occuiTence of an upset has the burden of proof. Part 11 Page 10 of 14 6. Removed Substances Solids, sludges, filter backwash, or ether pollutants removed in the course of treatment or control of wastewaters shall be disposed of in accordance with NC IS 1 3-215.1 and in a 117 OWN II 1 1111111 or inadequately tr retention of inadequately treated effluent, ;E TION D. MQNITQRING A RECORDS 1. Reargjsentative Sarni ling Samples collected and measurements taken, as required herein, shall be characteristic of the volume and nature of the permitted discharge. Samples collected at a frequency less than Period which the sample represents. All samples shall be taken at the monitoring paints specified in this permit and, unless otherwise specified, before the effluent joins or is diluted by any other wastestream, body of water, or substance. Monitoring points shall not be changedwithout notification to and the approval of the Permit Issuing Authority, 2. Rgpgrtin Monitoring results obtained during the previous month(s) shall be summarized for each month and reported on a monthly Discharge Monitoring Report (DMR) Form (DEM No. MR 1,1.1 2, 3) or alternative forms approved by the Director, DEM, postmarked no later than the 30th day following the completed reporting period: The first DMR is due on the last day of the month following the issuance of the permit or in the case of a new facility, on the last day of the month following the commencement of discharge. Duplicate signed copies of these, and all other reports required herein, shall be submitted to the following address: Division of Environmental Management Water Quality Section ATTENTION: Central Files Post Office Box 27687 Raleigh, North Carolina 27611 Part 11 Page 11 of 14 . Flow Measurements Appropriate flaw measurement devices and methods consistent with accepted scientific practices shall be selected and used to ensure the accuracy and reliability of measurements of the volume of monitored discharges.` The devices shall be installed, calibrated and maintained to ensure that the accuracy of the measurements are consistent with the accepted capability of that type of device. Devices selected shall be capable of measuring flows with a maximum deviation of less than 10 from the true discharge rates throughout the range of expected discharge volumes. Once -through condenser cooling water flow which is monitored by pump lags, or pump hour meters as specified in Part I of this permit and based on the manufacturer's pump curves shall not be subject to this requirennent. . TI Prodtare Test procedures for the analysis of pollutants shall conform to the EMC regulations published: pursuant to NCGS 143-215.63 et. seq, the Water and Air Quality Reporting .Acts, and to regulations published pursuant to section 304(g), 33 USC 1314, of the Federal Water Pollution Control Act, as Amended, and Regulation 40 CFR 136. To meet the intent of the monitoring required by this permit, all test procedures must produce minimum detection and reporting levels that are below the permit discharge requirements and all data generated must be reported down to the minimum detection or lower reporting level of the procedure. If no approved methods are determined capable of achieving minimum detection and reporting levels below permit discharge requirements, then the most sensitive (method with the lowest possible detection and reporting level) approved' method must be used. 5. nal1i0 for Tampering ring The Clean Water .Act provides that any person who falsifies, tampers with, or knowingly renders inaccurate, any monitoring device or method required to be maintained under this permit shall, upon conviction, be punished by a fine of not more than $10,000 ; per violation or by imprisonment for not more than two years per violation, or by both. 6. Records Retention The permittee shall retain records of all monitoring information, including all calibration and maintenance records and all original strip chart recordings for continuous monitoring instrumentation, copies of all reports required by this permit, for a period of at least years from the date of the sample, measurement, report or application. This period may be extended by request of the Director at any time. . Recordina Results For each measurement or sample taken pursuant to the requirements of this permit the permittee shall record the following information; a. The date, exact place, and time of sampling or measurements; b The individual(s) who performed the sampling or measurements; c. The date(s) analyses were performed; d. The individual(s) who performed the analyses; e. The analytical techniques or methods used; and f. The results of such analyses. Part 11 Page 12 of 1 S. Ins` ecti n and Entry The permittee shall allow the Director, or an authorized representative,, upon the presentation of credentials and ether documents as may be required by law, to; a. Enter upon the pe ittee's premises where a regulated facility or activity is located or conducted, or where records must be kept under the conditions of this permit; b. Have access to and copy, at reasonable times, any records that must be kept under the conditions of this permit; c. Inspect at reasonable times any facilities, equipment (includingmonitoring and control equipment), practices, or operations regulated or required under this permit; and d. Sample or monitor at reasonable times, for the purposes of assuring permit compliance or as otherwise authorized by the Clean Water Act, any substances or parameters at any location. SE TIQN E. REPC)R'TINQ REQUIREMENTS' 1. han e in Discharge All discharges authorized herein shall be consistent with the terms and conditions of this permit. The discharge of any pollutant identified in this pennit more frequently than or at a level in excess of that authorized shall constitute a violation of the permit, 2. Planned Changes The permittee shall give notice to the Director as soon as passible of any planned physical a. The alteration or addition to a permitted facility may meet one of the criteria for determining whether a facility is a new source in 40 CFR fart 122.2(b); or b. The alteration or addition could significantly change the nature or increase the quantity of pollutants discharged. This notification applies to pollutants which are subject neither to effluent limitations in the permit; nor to notification requirements under 40 FR :Part 122.4 (a) (1). . Anticitaated NQngomnliance The pe nittee shall give advance notice to the Director of any planned changes in the perrnitted facility or activity which may result in noncompliance with permit requirements. . Transfers This permit is not transferable to any person except after notice to the Director. The Director may require modification or revocation and reissuan e of the permittee and incorporate such other requirements as may be necessary under the Clean Water Act. RQ—orts D. 2. of this permit). R. Part 11 Page 13 of 14 intervals specified elsewhere in this permit. Dn a Discharge Monitoring Report (DMR) (See arithmetic mean unless otherwise specifii 6. jwgmjy- a. The pt noncoi be pro circury the pe contait includ-I iire averaging of measurements shall u A by the Director in the permit. eliminate, and prevent reoccurrence of the noncompliance. under this paragraph. (A) Any unanticipated bypass which exceeds any effluent limitation in the permit. (B) Any upset which exceeds any effluent limitation in the permit. (C) Violation of a maximum daily discharge limitation for any of the pollutants listed by the Director in the permit to be reported within 24 hours. c. The Director may waive the written report on a case -by -case basis for reports under paragraph b. above of this condition if the oral report has been received within 24 hours. 7. -Qjher NoncQml2liangt, The permittee shall report all instances of noncompliance not reported tinder Part 11. E 5 and 6. of this permit at the time monitoring reports are submitted. The reports shall contain the information listed in Part 11, E 6. of this permit. 8. Other Lnformation Where the permittee becomes aware that it failed to submit any relevant facts in a permit application, or submitted incorrect information in a permit application or in any report to the Director, it shall promptly submit such facts or information, Part 11 Page 14 of 14 9. NoncomDliance Notification The permittee shall report by telephone to either the central office or the appropriate regional office of the Division as soon as i)ossible. but in no case more than 24 hours or on the next 111MIGNIMMIMMM! representation, or certification in any maintained under this permit, inclue noncompliance shall, upon convictioi violation, or by imprisonment for not PART III OTHER REQUIREMENTS A. Construction No construction of wastewater treatment facilities or additions to add to the plant's treatment capacity or to change the type of process utilized at the treatment plant shall be begun until Final Plans and Specifications have been submitted to the Division of Environmental Management and written approval and Authorization to Construct has been issued. R - Groundwater Monitoring T N/, 01 )erinittee shall, upon written notice from the Director of the Division of Environmental igemen t, conduct groundwater monitoring as may be required to detenni ne the compliance s NPDES pernlitted facility with the current groundwater standards. ges in Discharaes of Toxic Substances The permittee shall notify the Permit Issuing Authority as soon as it knows or has reason to believe: discharge will exceed the highest of the following "notification levels"; (1) One hundred micrograms per liter (100 ug/1); (2) Two hundred micrograms per liter (200 ug/l) for acrolein and acrylonit-rile; five hundred micrograms per liter (500 ug/1) for 2.4-dinitrophenol and for 2-methyl-4.6-dinitrophenol; and one milligram per liter (I mgA) for antimony; (3) Five (5) times the maximum concentration value reported for that pollutant in the permit application. non -routine or in -frequent basis, of a toxic pollutant which is not limited' ill the pe-rr'nit, if that discharge will exceed the highest of the following "notification levels"; (1) Five hundred micrograms per liter (500 ug/1); ()Cane milligani per liter (I mg/1) for antimony; (3) Ten (10) times the maximum concentration value reported for that pollutant in the pernlit application. Ol Part III Permit No. NCO004375 D. 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 of bioassay procedure (North Carolina Chronic Bicassay Procedure - Revised *September 1989) or subsequent versions. ft mental Sciences Branch arolima. Division of mental Management x, 27687 ,N.C. 27611 E. The permittee shall conduct a plant. The discharge shall be evali completed annually using EPA purgeables (i.e., volatile organic c (d) organochlorine pesticides and Annual Pollutant Analysis Mc accompanying memo, to be provi describes the sampling and anal pollutant analysis. This monitor Analysis Monitoring Requirement" IjIll III Oil: I! IF[ llii;lillillll ill nts and lists chemicals to be included is to be referred to as the "Annual Pollutant t i •• i • t t' Mugu-To • • t •- t t ... •- ___� staging requirements during the summer {April 2 - October 3 i} PAT IV ANNUAL ADMINJSTERI C AND COMPLIANCE FEE REQUIREMENTS A. The permlttee must pay the annual administering and compliance fee within 30 (thirty) stays after being billedby the Division. Failure to pay the fe.e an a timely manner in accordance with 1.5 NCAC 2H .0105(b)(4) may cause this Division to initiate Faction to revoke the permit. N. R GOV 1991 State of North Carolina W,24 MANASEQq Department of Environment, Health, and Natural ReSANWLE kdkiL affla Division of Environmental Management 512 North Salisbury Street - Raleigh, North Carolina 27611 James G. Martin, Governor George T. Everett, A.D. William W. Cobey, Jr., Secretary Director April 3, 1991 Mr. J. Paige Straley Sandoz Chemicals Corporation PO Box 669246 Charlotte, NC 28266 Subject: NPIDES Permit Application NPDES Permit No. NCO004375 Sandoz Chemicals Corporation Mecklenburg County Dear Mr. Straley: Reference is made to your letter of February 25, 1991 containing comments on the draft permit for NPDES permit application NC0004375. The Division of Environmental Management (ITEM) has reviewed the comments in this letter. The items are addressed in the following: (1) The word "north" refers to the plant location and is not a road direction. Also, the Department of Transportation considers odd -numbered roads as north -south roads. (2) The words "air stripper" have been added to the process description. The word "continue" has been deleted with reference to the herbicide wastewater. (3) The word "daily" has been defined on the effluent pages as every day except Saturday, Sunday, and legal holidays. 1 (4) Upstream and downstream monitoring for phenols has been dropped. (5) The total phenols limit will be left as 1.8 lb/day monthly average, 3.6 lb/day daily max. The Division's Planning Branch is presently evaluating the State phenol standard and has requested that monitoring for 4-chloro-3-methylphenol, 2-methylphenol, 4,6-dimethylphenol, pentachlorophenol, and 2,4,5-trichlorophenol using EPA method 604 be added to the pertnit. Monitoring should be done on a quarterly basis. (6) Limits for 2-chlorophenol, 2,4-dichlorophenol, 2-nitrophenol, 4-nitrophenol, 2,4-dinitrophenol, 4,6-dinitro-o-cresol, and phenol have been corrected to account for limits negotiated to include water from groundwater remediation. (7) The daily maximum for chloroform has been corrected to 0.81 lb/day. PolIntion Prevention Pays 1'. Box 27687, Raleigh, North Carolina 27611-7687 Telephone 919-733-7015 An Equal Opportunity Affirmative Action Employer (8) 'fhe mercury limit was included in the permit as an effluent sample collected on 7/24/89 indicated a concentration of 0-5 mg/l. However. the Division will reevaluate the mercury permits. r of effluent monitoring in which thi Toxicity questions may be dis andition D. (annual pollutant an �S permits. Sludge disposal is h point requested on March 27, 1991. Please contact Rosanne Barona or me at 919/733-5083 to discuss this letter. Sincerely, / it Overcas ", M. Supervisor, NPDES Permit's Cc: "Te"chnWical "Suppor"tBr"anch"W Ms. Carolyn McCaskill Pe File , y Pen -nit No. NCO004375 STATE OF NORTH CARCL.INA DIVISION OF ENVIRONMENTAL, MANAGEMENT Coll ' VTR AND PERMIT TO DISCHARGE WASTEWATER UNDER THE1991 URIJUL OFFICE h compliance wth the provision of North Carolina General Statute 143-: 15.1, imission, `w the Federal Water Pollution -Contt6l Act, as amended, Sandoz Chemicals Co Lion to discharge wastewater`a facility located at Mt Holly Plant NC Highway 27 north of Charlotte Mecklenburg County s designated as the Catawba River in the Catawba River Basin Darts 1, III and III hereof. This permit shall become effective This pennit and the authorization to discharge shall expire at midnight on Signed this day George T. Everett, Director Division of Environmental Management agement By Authority of the Environmental Management Commission SUPPLEMENT'' Sandoz Chet is hereby authorized to: 1. Continue to operate a 3.9 MGD wastewai P rtnit No. NCO004 75 WITC OVER SHEET Corporation River which is classified Class ?" -III waters in the Catawba River Basin. A. (). EFFLUENT LIMITATIONS AND MONITORING UI MENTS FINAL Permit No. NCO004375 During the period beginning on the effective date of the permit and lasting until expiration, the Permittee is authorized to discharge from outfall(s) serial number 001. Such discharges shall be limited and monitored by the permittee as specified below: Effluent Characteristics a Units ( QC Measurement Sara 12 *Samole` olL v p _MIXc a. a u8 aLly e ocat on Flow 3.9 MGD Continuous Recorder I or E OD, 5 Day, 20 652,0 2236.0 Daily** Composite E,U,D Total Suspended Residue 976.0 2926.0 gaily*" Composite E NH3 as * *** 651.0 977,0 Gaily" Composite E,U,D Dissolved Oxygen Cady*" Grab E,U,D Fecal Coliform Monthly Grab E Total Phosphorus Monthly Composite E Total Nitrogen (NO2+NO3+T N) Monthly Composite E OCD Monthly Composite E MBAS Monthly Composite E Manganese Monthly Composite E- * Sample locations: E w Effluent, I - Influent, U - Upstream at NC: Highway 27, D - Downs at I-85 Upstream and downstream samples for BOD5, N113 as N, dissolved oxygen, temperature, conductivity, and pH shall be collected three times per weep during ,Tune, July, August, and September and once per week during the remaining months of the year. ** Daily is defined as every clay except Saturday, Sunday, and legal holidays. *** Chronic Toxicity (Ceriodaphnia) P/F at 1.8%; March, June, September, and December-, See Part III, Condition D. * See Part 111, Condition E. *** Staging Requirements (Applicable April I - October 3 1) - See Part 111, Condition Fa The pH shall not be less than 6.0 standard units nor; greater than 9.0 standard units and shall be monitored daily at the effluent, upstream, and downstream by grab sample. There shall be no discharge of floating; solids or visible foam in other than trace amounts. I • A"I a: s,. % Dunn outfall(s) serial number 001. (Continued) Effluent Characteristics pischarae Llrrritations UaL ay Other UnIll (11g2gityl mdob urmenu Al i *Sample g paL a eauency oca ion Iron ; Monthly Composite E Chlorides Monthly Composite E Sulfate Weekly Composite E Mercury 0.022 2..4 u ll Weekly Composite E Conductivity Grab U,D Temperature Daily** Grab E,U,D Total Phenols 1.6 3.6 Weekly Grab E Chronic Toxicity** Quarterly Composite E Pollutant Analysis`** Annually E 4-chloro-3-methylphenoi Quarterly Grab E 2-methylphenoi Quarterly Grab E 4,6-dmethylphenol Quarterly Grab E Pentachlorophenol Quarterly Grab E 2,4,5-trichlurophenol Quarterly Grab E A. (), EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAL Permit No. N O0043 5 During the period beginning on the effective date of the perrnit and lasting until expiration, the Permittee is authorized to discharge from outfall(s) serial number 002. Such discharges shall be limited and monitored by the permittee as specified below: Effuent Characteristics12122haro 'Monitoring Requirements Lbs/day. Units -(12_e_cjW Measurement Sam e- * a m c l e M Avc, pAILy_MqX Mon. Ava. 12gily Max. Frenuencv iume Location Flaw Batch RecorderE Total Suspended Residue 22.3 7.0 Weekly Composite" E COD 108.0 158,Q Weekly Composite"* E BCD, 5 Day, 20 °C 19.0 89.0 Weekly Composite" E `Sample locations: E - Effluent, I - Influent ** Composite samples may be done as grab samples if the discharge is on a batch basis. EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS FINAI, NC(X)04375 During the period beginning on the effective date of the permit and lasting until expiration, the Pertnittee is authorized to discharge from outfall, serial number 001. (Continued) Such discharges shall be limited and monitored by the permittee as specified below: Effluent Characteristics Mon. Avg. Daily Max. Measurement Sample *Sample lbs/day lbs/day Frequency Type Location Acenaphthene" 0.39 0.50 Quarterly Grab E Acrylonitrile 1.69 430 Quarterly Grab E Benzene 0.75 2.70 Quarterly Grab E Carbon Tetrachloride 0.32 0.67 Quarterly Grab E Chlorobe' nzene 0.31 0.57 Quarterly i Grab E 1,2,4-Trichloroben zene 1.20 2.46 Quarterly Grab E Hexachlorobenzene 0.26 0.49 Quarterly Grab E 1,2-Dichloroethane 1.20 3.71 Quarterly Grab E 1,1,1-Trichloroethane 0.37 0.95 Quarterly Grab E Tie xachloroethane 0.39 0.95 < Quarterly Grab E 1,1-Dichloroediane 0.39 1.04 Quarterly Grab E 1,1,1-Trichloroethane 0.37 0.95 Quarterly Grab E Chloroethane 1.83 4.72 Quarterly Grab E Chloroform 0.37 0.81 Quarterly Grab E 2-Chlorophenol, 0.62 1.95 Quarterly Grab E 1,2-Dichlorobenzene 1.57 3.32 Quarterly Grab E 1,3-Dichloroben zene 0.62 0.90 Quarterly Grab E 1,4-Dichlorobenzene 0.31 0.57 Quarterly Grab E 1,1-Dichloroethylene 0.28 0.44 Quarterly Grab E 1,2-trans-Dichloroethylene 0.37 0.95 Quarterly Grab E 2,4-Dichlor-ophenol 0.77 2.22 Quarterly Grab E 1,2-Dichloropropane 2.69 4.05 Quarterly Grab E 1,3-Dichloropropylene 0.51 0,77 Quarterly Grab E 2,4-Dimethylphenol 0.36 0.71 Quarterly Grab E 2,4-Dint trotoluene 1.99 5.03 Quarterly Grab E 2.6-Vinttrotoluene 4.40 11.28 Quarterly Grab E Ethylbenzene 0.65 2.20 Quarterly Grab E Flu there 0.47 1.20 Quarterly Grab E Methylene Chloride 0.70 1,57 Quarterly Grab E Methyl Chloride 1.51 3.34 Quarterly Grab E Hexachlorabut adiene 0.35 0. 6 Quarterly Grab E Naphthalene** 0.45 0.50 Quarterly Grab E Nitrobenzene 0.48 1.20 Quarterly Grab E 2-Nitrophenol 1.23 2.08 Quarterly Grab E 4-Nitrophenol 2.17 3.74 Quarterly Grab E 2,4-Dinitrophenol 2.15 3.71 Quarterly Grab E 4,6-Dinitro-o-cresol 1.55 5.50 Quarterly Grab E Phenol 1.56 2.70 Quarterly Grab E Bis(2-ethylbexyl)phthalate 1.81 4.91 Quarterly Grab E Di-n-butyl phthalate 0.48 1.00 Quarterly Grab E Diethyl phthalate 1.43 3.57 Quarterly Grab E Dimethyl phthalate 0.33 0.83 Quarterly Grab E Benzo(a)anthracene** 0.31 0.50 Quarterly Grab E Benzo(a)pyrene** 0.40 0.50 Quarterly Grab E (Continued) Effluent Characteristics Mon. Avg. Daily Max. Measurement Sample *Sample lbs/day lbs/day Frequency Type Location 3,4-Benzofluoranthene** 0.40 0.50 Quarterly Grab E Benzo(k)fluoranthene** 0.39 0.50 Quarterly Grab E Chrysene** 0.39 0.50 Quarterly Grab E Acenaphthylene" 0.39 0.50 Quarterly Grab E Anthracene" 0.39 0.50 Quarterly Grab E Fluorene** 0.39 0.50 Quarterly Grab E Phenanthrene" 0.39 0.50 Quarterly Grab E PMne** 0.44 0.50 Quarterly Grab E Tetrachloroethylene 0.39 0.99 Quarterly Grab E Toluene . 0.53 1.63 Quarterly Grab E Trichloroethylene 0.37 0.95 Quarterly Grab E Vinyl Chloride 1.82 4.70 Quarterly Grab E Total Cyanide 7.39 9.01 Quarterly Grab E *Sample Location: E-Effluent "These parameters are water -quality limited. Part III Permit No. N(10004375 D. 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 them may be no observable inhibition of reproduction or significant mortality is 1.8% (defined as treatment two in the North Carolina procedure document). e permit holder shall perform quarterly monitoring using; this procedure to establish compliance with the permit condition. The first test will be performed after thirty days from issuance of this permit during the months of March, June, September, and December. Effluent sampling for this testing shall be performed at the N DES permitted final effluent discharge below all treatment processes. ditionaliy, ITEM Form AT- 1(original) is to be sent to the following address: iences Branch ion o anagement NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum control organism sival 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. E. The permittee shall conduct a test for pollutants annually at the effluent from the treatment plant. The discharge shall be evaluated as follows: i) A pollutant analysis of the effluent most be completed annually using IPA approved methods for the following analytic fractions: (a) purgeables; (i.e., volatile organic compounds); (b) acid extractables; (c) base/neutral e tractables; (d) organ " hlorine pesticides and PC13's ) herbicides, and (f) metals and other inorganics. The Annual Pollutant Analysis Monitoring (AAM) Requirement Reporting Form A and accompanying memo, to be provided to all discharges affected by this monitoring requirement, describes the sampling and analysis requirements and lists chemicals to be included in the pollutant analysis. This monitoring requirement is to be referred to as the "Annual Pollutant Analysis Monitoring Requirement" (APAM). 2) <Other significant levels of or ani+ For the purpose of implementing; this base/neutral extractable, and acid unidentified peaks occur) for cheni Reporting Form A should be identif Rennrtincr Form A in.sarnetiom. This 7 ,iernicals must be identified and approximately quantif e quirern nt, the largest 10 GC/MS peaks in the pur ,eab] ractable fractions (car fewer than 10, if less than 1 ds ether than those 'specified on the ` PA Recluireme. the "10 significant peaks rule"". F. Staging Requirements (Applicable April The operating day runs from 7:00 am to 7:0 clad nvt*rgai- etraa flnur ac rlptc-rmin&d htir if the ARAM' requirement is to be referred to a Aber 31) Each day, the permittee will calculate a running v' g formulas: 175 cfs: BOD5 + 0.54( 3-N) <= 5 staging requirements during the summer (April 1 - October 3 1 Additional DMR St7 EFFLU t ES Permit No. NCO004375 Discharge_ 2 7 8 10 11 12 1 14 15 16 17 18 19 20 21 2 23 24 25 26 27 8 29 0 31 for Sandoz Month Year Check if ORC has charred I certify that this report is accurate and and complete to the best of my knowledge. X River Allowable Actual AW °i ^ 'Ron- T414- AM4r gANW- RAn+ _ Satan- n Average Case 1: River Flow <= 175 Cfs BO 5 + 0.54N 3 <= 566.4 lb/ Case 2: 175 c a< 'ver Flow<= 250 cfs BOD5 = 0.54NH3 <= 1044 lb/ Case 3; Riv. Flow>250 cfa, BOD5<=852 lb/d (mo avc ), BOD5<=2236 lb/d (dly max) NF 3<=6 1 Ib/d (men avg) , N113<=977 1b/e (dly x) PT T-2 -I% i u rry i- ' use tc3 cc�'#`r Lj Ale 4 ' P•7 P' silo cto 4, ! .S- .fi r i filer°7-17 lK T—/ Pri I^ a ry o tP P5 L.h. � S ~� t tl�= , ;•earn , � -r� �!`sr,� Z- 313 P.S. d �.�. 73�— r s r^r car- r E-3 C! C.J 'µ . . i3ac PS Fire Or Spill or Ex lairs material Dial 228 to notify l Boiler Room/Suitchboard ; who tills Emergency Co - If passible ordin t r and if directed extinguish sounds emer enc whistle Stop and/or or contain contain spill fire without if possible risking ith ut personal risking safer Calls rescue squ d personal* or olice if neede safety. Leave area if danger of Mobilize Fir fames or Brigade Determine if ex lion emergency need to enact equipment. retell roc duce ' Call Fire Department Deploy if needed portable Determine pumps hazards sorbent and decide pillows,backhoe if evacuation = r neutralizing is needed. omp and and if so, Cell out Fire' how er awa Brigade if thence of;fire. r nee i for washdown nt 0 National Response Center if necessary tip ete c, eanup and replenish emergency supplies OVERVIEWOF ACTION FIGURE Page - Permit No. NCO004375 STATE OF NORTH CAROLINA OF DIVISION OF ENVIRONMENTAL. MANAGEMENT ` r, . C NATURALrS ANT) PERMIT WkM1" -r ' � "FLOP TO DISCHARGE WASTEWATER UNDER THE E NATIONAL POL T N I I N Y TEIF M,">g °'° ,tMAXAGENar In compliance with the provision of North Carolina General Statute 14-215.1, omisson, and the Federal Water Pollution Sandoz Chemicals Cori Mt, Holly Plant NC Highway 27 north of Charlotte Mecklenburg County by the North Carolina Environmental trot Act, as amended, lion :ed at in accordance with ettluent limitations, monitoring requirements, and other conditions set torttt in Parts I, II, and IH hereof. This pen -nit shall become effective This pen -nit and the authorization to discharge shall expire at midnight on Signed this day George T. Everett, Director Division of Environmental Management By Authority of the Environmental Management Co SUPPLEMENT TO Pi Sandoz Chemical ereby authorized to: Permit No. NCO004375 )VER SHEET ion !► # •'i ,. � ! , r . • #�iMtt�l M1L' i[lY�'fllNt la`!!i®t/tI!?YY.R[idt®EfIs! ou lI(s) serial number 001. Such discharges shall be limited and monitored by the permittee as specified below: Effluent Characteristics Discharge Urnitatirans Monitoriin€t Rauh Lbs/day., Units (soecif) Measurement Mon. Ava. Qally Max MoLi. Ava. Cfall,y Max. Fre ueney Flow 3. 9 MGD Continuous R BOD, 5 Day, 20 °C**** 852.0 2236.0 Daily C Total Suspended Residue 976.0 2928.0 Daily C NH3 as N**** 651.0 977.0 Daily , C Dissolved Oxygen Daily G Fecal Coliform Monthly G Total Phosphorus Monthly C Total Nitrogen (N0 +NO +TKN) Monthly CCD Monthly MBAS Monthly Manganese Monthly C Z=921=1 em-en ts am le *ample -Location acorder I or E amposite E,U,D amposite E amposite E,U,D rab E,U,D rab E * ample locations: E -Effluent, I - Influent, U - Upstream at NC I-1il hway 27, D - Downstream at 1-85 Upstream and downstream samples for BOD5, NH3 as N, dissolved oxygen, temperature, conductivity, and pH shall be collected three times per week during .Tune, July, August, and September and once per week during the remaining months of the year. Upstream and downstream samples for phenols shall collected monthly. ** Chronic Toxicity (Ceriodaphnia) '/r at 1.8%; March, June, Septetaiber, and December; see Part 111, Condition U. See Part 111, Condition E. * * Staging Requirements (Applicable April 1 - October 31) See Part 111, Condition E The pH shall not be less than 6.0 standard units nor greater than .0 standard units and shall be monitored daily at the effluent, upstream, and downstream by grab sample. There shall be no discharge of floating solids or visible foam in other than trace amounts. Effluent gheracterlstics M _0 Iron Chlorides Sulfate Mercury 0.022 2.4 ug/I Conductivity Temperature Total Phenols 1.8 Chronic Toxicity** Pollutant Analysis*** 1V1%;O*UFtP111Wt11 Frequency Monthly C Monthly C Weekly C Weekly C G Daily G Weekly G )uarterly C %nnually rents LpLe *mole P-0 Lo_q _atLo_n [posite E posite E posite E posite E U,D E,U,D E,U,D posite E E Organic Pesticide Chemicals 0.02 0.12 Weekly Composite E BOD, 5 Day, 20 °C M o 89.0 Weekly Composite E *Sample locations: E - Effluent, I - Influent The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units and shall be monitored weekly at the effluent by grab sample. There shall be no discharge of floating solids or visible foam in ether than trace amounts. EFFLUENT LIMITATIONS AND MONITORING REQ During the period beginning on the effective date of the pt Perrnittee is authorized to discharge from outfall serial nu shall be limited and monitored by the perittee as specific Effluent Characteristics Mon. Avg. >Daily Max. lbs/day lb/day ; Acenaphthene** 0.39 0.50 + Acrylonitrile 1.69 4.30 + Benzene 0.75 2.70 i Carbon Tetrachloride 0.32 0.67 , Chlorobenzene 0.31 0.7 + 1,2,4-Trichlorobenzene 1.20 2.46 Hexachlorobenzene 0.26 0.49 1,2-Dichloroethane 1.20 3.71 1,11-Trichloroethane 0.37 0.95 Hexachloroethane 0.39 0.95 1,1-Dichloroethane 0.39 1.04 1,11-Trichloroerhane 0.37 0.95 Chloroethane 1.83 4.72 Chloroform 0.37 0.21 2-Chlorophenol*** 0.55 1.7 1,2-Dmchlorobenzene 1.57 3.32 1,3-Dmchlorobenzene 0.62 0.90 1,4-Dichlorobenzene 0.31 0.57 1,1-Dmchloroethylene 0.28 0A4 1,2-trans-Dichloroethyene 0.37 0.95 2,4-Dichlorophenol*** 0.69 1.80 1,2-Dichloropropane 2.69 4.05 1,-Dmchloropropylene 0.51 0.77 2,4-Dimethylphenol*** 0.32 0.63 2,4-Dinitrotoluene 1.99 5.03 2,6-Dinitrotoluene 4.40 11.28 Ethlbenzene 0.65 2.20 Fluor there °0.47 1.20 i Methylene Chloride 0.70 1.7 Methyl Chloride 1.51 3.34 Hexachlorobutadiene 0.35 0.86 , Naphthalene** 0.45 0.50 Nitrobenzene 0.48 1.20 2-Nitrophenol*** 1.23 1.80 + 4-Nitrophenol*** 1.80 1.80 i 2,4-Dinitrophenol*** 1.80 1.80 + 4,6-Dinitro-o-cresol*** 1.37 1.80 + ]phenol** 1.56 1.80 i Bis(2-ethylhexylphthalate 1.81 4.91 + Di --butyl phthalate 0.48 1.00 + Diethyl phthalate 1.43 3.57 W Dimethyl phthalate 0.33 0.83 + Benzo(a) thracene** 0.31 0.50 + Benzo(a)pyrene** 0.40 0.50 + UIREMENTS FINAL NC00043 below: [eaurement Sample *Sample requency Type Location quarterly Grab quarterly Grab E �uarterly Grab E quarterly Grab �uarterly Grab E �uarterly Grab E quarterly Grab E �uarterly Grab E quarterly Grab E �uarterly Crab E quarterly Grab E quarterly Grab E �uarterly Grab E �uarterly Grab E quarterly Grab E quarterly Grab E quarterly Crab E quarterly Grab E quarterly Grab E uarterly Grab E quarterly Grab E quarterly Grab E quarterly Crab E quarterly Grab E �uarterly Grab E quarterly Grab E quarterly Grab E )uarterly Grab E quarterly Grab E quarterly Grab E quarterly Grab E �uarterly Grab quarterly Grab quarterly Grab E quarterly ' Grab E �uarterly Grab E quarterly Grab E quarterly Grab E quarterly Grab quarterly Grab E quarterly Grab E quarterly Grab E �uarterly Grab E quarterly Grab E (Continued) Effluent Characteristics Mon. Avg. Daily Max. Measurement Sample *Sample lbs/day lbs/day Frequency < Type Location 3,4-Benzofluoranthene** 0.40 0.50 Quarterly Grab E Benzo(k)fluoranthene** 0.39 0.50 Quarterly Grab E Chrysene** 0.39 0.50 Quarterly Grab E Acenaphthylene** 0.39 0.50 Quarterly Grab E Anthracene* 039 0.50 Quarterly Grab E Fluorene** 0.39 0.50 Quarterly Grab E Phenanthrene** 0.39 0.50 Quarterly Grab E Pyrene** 0.44 0.50 Quarterly Grab E Tetrachloroethylene 039 0.99 Quarterly Grab E Toluene 0.53 1.63 Quarterly Grab E Trichloroethylene 0.37 0.95 Quarterly Grab E Vinyl Chloride 1.82 4.70 Quarterly Grab E Total Cyanide 7.39 9.01 Quarterly Grab E 1.8 lbs)day (5-5.3 ug/l). ,K- Part III Permit No. NCO004375 D� 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 there may be no observable inhibition of reproduction or significant mortality is 1.8% (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 after thirty days from issuance of this permit during the months of March, June, September, and December, 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 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.C. 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 dose/response data. Total residual chlorine of the of 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 moniti rt Division of Environmental Managen permit may be reopened and modified NOTE: Failure to achieve test condi control organism survival and appror and will require immediate retesting (, suitable test results will constitute nom a include alternate monitoring requirements or limit E. The permittee shall conduct a test plant. The discharge shall be evaluated completed annually using EPA appro, purgeables (i.e., volatile organic compo (d) organochlorine pesticides and PCB's Annual Pollutant Analysis Monitoring (APAM) Requirement Reporting Form accompanying memo, to be provided to all discharges affected by this monitoring requ describes the sampling and analysis requirements and lists chemicals to be include pollutant analysis. This monitoring requirement is to be referred to as the "Annual F Analysis Monitoring Requirement" (APAM). • VVY75 Y MY V.-I fiance monitoring requirements. r pollutants annually at the effitien, r0mmth • 2) Other significant levels of synthetic organic chemicals must be identified and approximately quantified. For the purpose of implementing this requirement, the largest 10 CC/MS peaks in the purgeable, base/neutral extractable, and acid extractable fraction (err fewer than 10, if less than 10 unidentified peaks occur) for chemicals rather than those specified on the A A Requirement Reporting Form A should be identified and approximately quantified as stated in the APAM Reporting Form A instructions. This part (item 2) of the APAM requirement is to be referred to as the "1'0 significant peaks rule". F. Staging Requirements (Applicable April 1- October 31) The operating day runs from 7:00 am to 7:00 am. Each day, the permittee will calculate a running daily average stream flaw as determined by turbine operation at Mt. Island Dam, leakage at the clam (80 cfs), and. the 7QIO flow of Dutchman's Creek (15cfs). Effluent release is to be controlled such that projected release of B D and ammonia, using the most recent analytical values for these parameters, will not exceed the value given in the following formulas: (1) When the daily river flaw is calculated to be < or = 175 cfs: B D5 + 0.54( -N) <= 566.4 lb/day (2) When daily average river flow is calculated to be > 175 cfs but c or = 250 cfs: BOD5 + O? 54(NH3-N) <= 1044 lb/day The attached additional DMR sheet shall be used to monitor compliance with BOD and NH3 staging requirements during the summer (April 1 - October 31) Additional DMR Sheet for Sandoz EFFLUENT DES Permit No. NCO004375 Discharge Month Year Sandoz Class 4 Mecklenburg County Operator in Responsible Charge (ORC) Certified Laboratory: Person(s) Collecting Samples: Check if ORC has changed 1 certify that this report is accurate and and complete to the best of my knowledge. X River Allowable Actual QW Flow BOD5 NH3 BOO+. 54N i3 BOD+.54NH3 Comp?, Tim r f 1 1 1 a N 1 2 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 24 25 26 27 28 29 30 31 Average Case 1: River Flow <= 175 cfs BOD5 + 0.54NH3 <= 566.4 lb/d Case 2: 175 cfs<River Flow<= 250 cfs BOD5 = 0.54NH3 <= 1044 lb/d Case 3: Riv. Flaw>250 cfs, BOD5<=852 lb/d (mo avg), BOO <=2236 lb d (dly max) NH3<=651 lb/d-(mo vg), NH3<=977 lb/d (dly max) ,y Eil*�- 4 9 Fomisak Corporation MliW*m W Aftb*r, ii! Mt.Holly Plant Road Director, Environmentof Affairs )rtfa Carolina 28205P.O. 669246 8 Charlotte, NC 2 266 1063 March 15, 1990 rts ,,scan, Supervisor vices unit '.4' 2 19,9 a Department of Environment, Natural Resources urces Section iry St. 2'611 r s r � + � �- • r- � s • • • s • • '* ♦ - r • • s�.r * *. s � «- M� .e � � ` • • �' ••* -. • n t *. s •r- �� � � m® s ! l s ♦ • ' i r t • - residual toxicity at that time. In June 1989 we commissioned a study by Enwright Laboratories to perform chronic toxicil studies on six process wastesty eanis which we suspected of exhibiting chronic toxicity. These wastestreams had partly been identified through wastewater characterization studies performed previously. Two waste strearns did indeed show a potential effect. Verifying whether these are source of our residual chronic problems has been complicated by stored wastewater being rele&= We i occurrin� shows, r Our measure chronic toxicity quarterly, and it appears that some imp �11 uygl,auv.o LV major part of the treatability study. Working with the NC ITEM Biological Services Unit, we have already set up a chronic toxic lab here at Mt Holly. Our intent is to track down all suspect wastestreams and then to determin( combination of pretreatment and enhanced biological treatment will eliminate the toxicity. Our environmental engineering consultants will work with Sandoz professionals to form a Toxicity Reduction Team. The chronic toxicity lab is already at work and the consultant team should begi work in April. The time necessary to completely eliminate the problem is difficult to pin down for several reasons. We think the ultimate solution to both the toxicity Emit and other new limits will involN combination of waste minimization, waste pretreatment and possibly enhanced end -of -pipe treatn The specific modifications will depend on the final permit limits and on the results from our engineering treatability studies. If major modifications are indicated we anticipate that, as in 1911 and 1988, some process disruption will be inevitable. Thus it is unlikely that we can fully comp with all permit parameters, including toxicity, until the major portions of the upgrade are compl( Sandoz' record indicates a good faith effort to attack the problem of effluent toxicity. The f has been somewhat of a moving target --the change from acute toxicity to chronic toxicity testing example --but Sandoz remains committed to compliance with all applicable environmental regulat We are confident that our continued efforts will attain compliance with the chronic toxicity discl permit standards, 3 J.. Ij'kjj -- k4"a Y6..4iknL LYCLr.R V..+" . LaaL asa swa-.w..+.. —1 -- - -- - - a elp to you in any way, please do not hesitate to call me at 704 822 2701. Sincerely, J. Paige Straley, PE Environmental. Managej Mooresville Regional Office Dale Overcash W.M. Archer M. Teague M. J. Smith l- (7) VqI k a & Cwx EN V I R 0 N M E N T A L WOO CE RR I O D RH N PS. 'TUX 1 U JL `1 ' x Client: Sandoz Chemical Corp. Location: Charlotte, North Carolina County. Mecklenburg Identification: 1.8% Effluent Test Initiation: 0 /20 90 En right Environmental Consulting Laboratories. Inc. (25 Woods Lake Rd, 29 07) PO Box 17467 Greenville, S0 29606 803 23 .0707 I N,rEI This toxicity test W.= tpRErA-rION ou REsuE,rs - - - - z .4. - 1— ACULe JOXICILY. Ou -)1611,L Chronic Toxicity: Significant chronic toxicity by t Test. Final Result: Fail `I'E Sr S Y Sr E4; M Client: Sandoz Chemical Corp. Test Start Date: 02/20/90 Test Completion: 02/27/90 Test Type., 7 Day Chronic Toxicity - Pass/Fail Test Location: Enwright Environmental Consulting Laboratories (NC Certification #*. 010) Test Organism: Ceriodaphnia dubia Source: Enwright Age: <24 lirs Test Procedure: Short -Term Methods for Estimating the Chronic ToxicitY of Effluents and Receiving Waters to Freshwater Organisms. EPA 600/4-89/001 Method 1002 North Carolina Ceriodaphnia Chronic Effluent Bioassay Procedure. NC Dept of Nat. Res. and Comm. Dev., DEM, Water Quality Section, December 1985. Revised September 1989 Test vessels- 20 nil plastic beakers Amount Test Soln: 15 nil / replicate # Replicates/Concentration: 12 Test Organisms/Replicate: I Test Dilutions Used: 0 & 1.8% Effluent Test Solution Renewal: Day 2 & Day 5 Test Solution Treatment: None Food Source: 0.10 ml Selenastrum (3.0-3.5 X 107 cells/nil) and 0.05 nil YCT daily / test vessel Test Set By: Joel Stephens Biologist Test Results Checked By: Robert W. Kelley, Ph.D Biology Laboratory Manager SAMPEINCx I Two effluent samples were collected i cubita ners for use in this toxicity test. during shipping. Client: Sandoz 'Chemical Corp. DAte: 02/20tl Si # Lab B Type c+ Date sampled (Composite started) 2; Time sampled Days of use 1. Maximum hold time: 7 cei t° 4 CC A "T 13 stic liter -size ry. The samples were chilled Sample 2' Bio 409' to composite 2/22/'90 ,y 2 Day 72 hrs 4°C temperature upon re p a, Client: Sandoz Chemical Corp. Sample, Identification. 1.8 effluent Start Date: 0 /20/ 0 ACUTE TOXICITY (Effects can Survival) # organisms dead - control: 0 dead. 0.09 # dead producing young' 0 dead: 0 < 0 # organisms dead- effluent; 0 # 'dead producing young: 0 # males & # last - control: 0 males & # lost- effluent: 0 o significant acute toxicity by fisher's Exact 'Test. Client. Sandoz Chemical Corp. Sample Identification: 1.8% Effluent Start Date: 02/20/90 CHRONIC TOXICITY (Effects on Reproduction) Dailv, Reproduction Totals - Rep Day 4 Day 5 Dad* 6 Day 7 Total Control A 2 1 0 4 13 12 16 21 B ] C 1 4; 5 10 11 27 D 1 5 9 15 30 E 0 6 0 13 19 F 4 6; 1 10 21 G 2 0: 9 10 21 0 3 0 15 18 1 3 5 14 0 22 1 7 0 9 14 30 4 7 0 14 2 L 5 0 0 17 22 Av. young/;female: (including mortalities): 22.67 (excluding mortal -.ties): 22.67 %3rd broad: 75% 1.8% A 4 9 3 5 0` 0 0 0 Effluent' B 3 0 0 1 3 C 2. D 2 0 0 1 2 5 5 0 2 13 F" 5 0 0 1 6 C 4 1 0 0 H 4 0 0, 4 8 I5 1 0: 0 6 4 3 12 5 24 a1 K 11 1 0 5 17 L 9 2 9 0 20 Av. young/'female. (including mortalities): 9.92 (excluding mortalities): 9.92 /k °rA Client: Sandoz Chemical Corp. Sample Identification: 1.81 S Cart Date: 02/20/90 ACUTE TOXICITY Fisher's Exact Test is used to ana - ---, .c, u Wx than among the controls. The effluent caused no significant acute toxicity. CHRONIC TOXICITY Data analysis is dependent upon whether the data is normally distributed and the control and effluent treatments have equal variances. The data is normally distributed. (Chi Square Test) X2= 9.37 (P=0.01) The treatments have= equal variances. (F Test) F= 4.99 (P=0.01) Because the data meets the assumptions of a parametric test, the t Test is used. T Value: 4.06 Critical Value: 2.508 Because the calculated 't' value exceeds the critical value, the reduction in reproduction in the effluent treatment is significant, indicating chronic toxicity. (P=0.01) `t WA'rER C 1I 'rRY" ANL`kx I Client: Sandoz Chemical Corp. Sample Identification: 1.8 Effluent StartDate: 02 20/90 Dilution Water ID: MilliQ Ultra Pure' Water & 10% Perrier (10%` D W); Preparation. Aerated 24 Hours Hardness: 42 mg/L Conductivity. 63 umhos Effluent Conductivity (Sample 1): 4520 umhos Conductivity (Sample ): 3000 umhos Residual Chlorine: c0.05 m/L Test Solutions D.O. D.O. PH Temp (m /L) (% sat.) (C) CONTROL Initial 8.3' 105% 7.9 25.6 Day 2 (old) 7.9' 100% 7.6 257 Day 2 (new) 8.3 105% 7.5 25.7 :gay 5 (old) 7.9' 99% 7.1 25.0 Day 5 (new) 8.3' 104% 6.8 25.0 Final 7.1 89% 7.3 254 EFFLUENT 1.8% Initial 8.0 101% 7.5 25.6 Day 2 (old) 7.8 99%; 7.6 25.,7 Day 2 ( new) 8.3 105% 7.7 25.7 Day 5 (old) 7.9 9%' 7.1 25.0 Day 5 (new) 8.1 101% 7.1 25.0 Final 7.1- 89% 7.2 25.-4 Client: Sandoz Chemical Corp. Sample Identification: Start Date: 02/20/90 Culture Health: Sensitivity: Culture organisms reference toxican The 48 Hour LC5( The mean LC50 v as a toxicant is Therefore, the cc deviation units a sensitivity of the normal range. `luent re exposed to NaCl as a ,r this test was 2.43 g/L. atthislaboratory for NaCl 2.06 g/L. Std. Dev.= 0.29 nt LC50 -value is 1.28 standard e the mean. This suggests the ,.nisms produced a mean of 22.67 young over the 7 day test period. The mean number of young produced at this laboratory for in-house control tests is 19.93 Std Dev= 2.44 Reproduction levels during this test were 1.12 standard deviation units above the mean. Therefore, reproduction of the control organisms was within the normal range. Test Precision: Mean Significant Difference (MSD): The MSD for this test was 6.016 young. This is the least difference in the number of young produced by the control organisms vs. the number of young produced by any effluent treatment organisms which can be detected as statistically significant. The ratio of the MSD to the control mean (percent reduction) for this data is 26.54 percent. Water Analysis: Dissolved Oxygen: Some readings exceed recommended limits. (Limits: 50% to 105%) Temperature: All readings are within acceptable limits. (Limits:240C to 260C) PH: All readings are within acceptable limits. (Limits:6.5 to 8.0) (7) E N V I R 0 N M E N T A L MINI Cl-IRONIC PASS/PAII, C R. O D A P H N I A IOXICITY TEST Client: Sandoz Chemical Corporation Location: Charlotte, North Carolina County: Meckelenbur Identification: 1* Effluent Test Initiation. 0 /06/90 Enwright Environmental Consulting Laboratories, Inc. (25 Woods Lake. Rd, 29()07) PO Box 17467 Greenville, SC 20606 803 235-0707 1N'rERPRE'rA'r1ON OF RESULI'S This toxicity test was conducted to determine if the effluent at the given concentration (the in -stream waste concentration - IWC) causes death (acute toxicity) or reduction in the reproduction of the test organisms (chronic toxicity) during a seven day period. Acute toxicity is checked by statistically analyzing whether significantly more organisms died in the effluent treatment than in the control treatment. chronic toxicity is checked by statistically analyzing whether sigilificantly '* few,4-,r young were produced by test organisms exposed to the effluet i't Creatment. If either analysis indicates a significant difference, the Lest is considered a failure. Results are summarized as follows: Acute Toxicity: No significant acute toxicity by Fisher's Exact Test. Chronic Toxicity: No significant. chronic toxicity by t Test. Final Result: Pass NOTE: On the test initiation day a small ethanol spill caused _kun of fumes from the drain into the incubator room. do ever resutrs Q0 jnUj(,aLjU a Jt!ZJZ!jk:Lj-ttj6 kJL --IAALAXt. as compared to the previous quarter. Ir E S Ir Client: Sandoz Chemical Corporatil Test Start Date: 02/06/90 Test Completion: 02/13/90 Test Type: 7 Day Chronic Toxicity Test Location: Enwright Environme (NC Certification Test Organism: Ceriodaphnia du Test Procedure: Short-Terni Metho, of Effluents and Recei EPA 600/4-89/001 Met North Carolina Cerioda Procedure. NC Dept of Quality Section. Decem tss/Fail Consulting Laboratories Source: Enwright Age: <24 hrs 1AIJIUMIL If'-,'5L ZIQUI iu ini / repucaLe # Replicates/Concentration: 12 Test Orgariisnis/Replicate: 1 Test Dilutions Used: 0 & 1.8% Effluent Test Solution Renewal: Day 2 & Day 5 Test Solution Treatment: None Food Source: 0.10 nil Selenastrum (3.0-3.5 x 107 cells/ml) and 0.05 ml YCT daily / test vessel Test Set By: Joel Stephens - Biologist U Test Results Checked By: Robert W. Kelley, Ph.D Biology Laboratory Manager SAMPEING INFORMA'rION Two effluent saniples were collected in plastic liter -size cubitainers for use in this toxicity test. The effluent stunples were hv nPr-,nnnPI and shiDt.>ed to Enwright Environniental Burin g shipping. Client: Sandoz Chemical Corporation Date: 02/06/90 Sample Sample #2 Lab # Ilia 387 Bio 390 Type composite composite Date sampled (Composite started) 2/5/90 2/8/90 Time sampled 0700 0700 Days of use Init,Day 2 Day 5 Maximum hold time: 72 hrs 72 hrs Temperature upon receipt: 1°C 40C w x� .e _1�3 rr :..,.] Client: Sandoz Chemical Cat,poration Sample Identification: 1.8% Effluent Start Irate: 0 /06,/9 ACUTE TOXICITY (Effects on Survival) organisms dead - control: 1 deed: 8.31 # dead producing young: I organisms dead- effluent: 1 dead: 8.3 # dead pt•odkcing young: I males & # lost - control: p # males & # lost-- effluent: 0 No significant acute toxicity by Fisher's P arf Ta d +. IA A'TER CIIEMISrRY ANAEYSIS Client: Sandoz Chemical Corporation Sample' Identification 1.8% Effluent Start Date.; 02/06/90 [iilution Water ID: MilliQ Ultra Pure Water & 10 Ferrier (10% DMW) Preparation: Aerated 24 hours Hardness: 45 mg/ Conductivity°. 88 umhos Effluent Conductivity (Sample 1): 4910 umhos Conductivity (Sample 2): 6520 umhos Residual Chlorine: <0.05 mg/L Test Solutions D.O. I.O. pit Temp (m /L) (% sat.) ( ) CONTROL Initial 8.3 1 6% 7.4 26.0 Day 2 (old) 7.5 8 7.2 25.9 Day 2 (new) 7.8 99% 7.3 25.9 Day 5 (old) 7.1 90% 7.1 25.8 Day 5 (new) 7.6 96% 7.3 2.8 Final EFFLUENT 1.8% Initial 8.3 104% 7.3 25.2 Day 2 (old) 7.3 92% 7.2 2.9 Day 2 (new) 8.2 104% 7.2 25.9 Day 5 (old) 7.4 94% 7.0 25.8 Day 5 (new) 8.1' 103% 7.0 25.8 Final (.Iietit: Sandoz Chemical CorporatiOT Culture Health* Sensitivity: Culture organisins reference toxican The 48 flour LC5( The mean LC50 v as a toxicant is Therefore, the ct� deviation units a sensitivity of the normal range. number of you' in-house contrc Reproduction IE Therefore, rept outside the noi The MSD for this test This is the least differ produced by the contr, young produced by an which can be detected The ratio of the MSD t 3Lnisms was within th of the control organis= e. Water Anrtlysis: ed recommended limits Dissolved Oxygen: Some readings exce Temperatu re: All readings are within acceptable limit-,. PH: Some readings exceed recommended limit.s. Stag of North Carolina Department of Natural Resources and Community Development Division of Environmental Management 512 North Salisbury Street Raleigh, North Carolina 27611 James G. Martin, Governor R. Pa William W. Cobey, Jr., Secretary December 1989 William Archer Sandoz Chemical Corporation PC) Box 669246 Charlotte, NC 28266 Subject: NPDES Permit No. NC004N Sandoz Chemical Corporation Mecklenburg County Dear Mr. Archer Please find enclosed a copy of the Draft NPDES Permit No. NCO040690 for Sandoz C Corporation. I would appreciate a response by January 10, 1989. If the subject p+ favorable with your company, the Division of Environmental Management °ll publish of to issue this permit. Sincerely, . C. tire. or 1-tES aUt CES AJ:,J N tTF D1':V I Lula M. Harris DECO Environmental Engineer I i N OF EENVIRORIg ,q Enclosure cc' Permit File Mooresville Regional Office Pollution Prevention Pays P.O. Box 27687, Raleigh, North Carolina 27611-7687 Telephone 91-733-7t115 An Equal Opportunity Affirmative Action Employer STJ DIVISION OF ENVI TO DISCHARGE Permit No. NCO004375 -INA D NATURAL RESOURCES WAGEMENT �ER THE fianec with the vrovision of North rAmlina ripnornl Rf*hito I A 2-1) 1 AZ 1 Sandoz 0 NC Highwt north of Cha Mecklenburg ition aed at - a, tb 1, u, anct in nereot. This permit shall become effective Ihis permit and the authorization to discharge shall expire at midnight on Signed this day R. Paul Wilms, Director Division of Environmental Management By Authority of the Environmental Management Corr SUPPLEMENT TO PEn Sande Chernicals C is hereby authorized to: Effluent C'hsraot�rl l ®Ischarae t Imi+�tlan� iP,rMit r% l it- AI-YC '# • 0 . e ;w. r.t tlnita sae Iv► Meaisurerme�n# Sam 0 le Flow {April 1 - October 31 } Freauencv Flow (November 1 -March 31) ' Continuous Recorder I or .6 BOO, ©ay, 0 °C 85, .0 ; 36i O Continuous Recorder I or Suspended Residue Total Su' 96.0 2928.0 Dail y Composite E,U,Q NFl3 N 434.0 651.0 Daily Composite E Dissolved Oxygen Dail y Composite E U,D F Daily grab E,U,D Total Residual "Chlorine Monthly Grab E; Total Phosphorus Monthly' Grab EMonthl Total Nitrogen (+NO3+TKN) y composite E CCD Monthly Composite E Monthly Composite E le 1 ations: "; -fluent, - In l'l nt, IT -Ups at NC Highway U • s at I-85 Lips t do s ples f B{)�S, as N, dissolved oxygen, temperature, conductivity, week d g e, July, August, ci September d once week during the remaining months of the all be collected three times Upstream samAles f phenols sh collected rattily. year. d downstream **Chronic Toxicity (Ceriodap ia) P/F at 1.8 ; March, June, September, and December, See Part III, Condition G. ***See Part III, Condition H . Ile pH shall :not be'less than 6.0 standard units nor 'greater than 9.0 standard units and shall be monitored daily at the effluent, downstream. upstream,' d There shall be no discharge of floating solids or visible foam in other than trace amounts. (Continued) ,�fftuent Chr�aoterietiL� �isehara� t im�tatl+�n� Mcrnite�ring„ t3taer Uni+� tQ» �ilv't a • rem+�nt; MS MIM—AmV "'LqUlWn Manganese Monthly Composite E Monthly y Composite Chlorides Monthly Composite E Sulfate Monthly Composite E Mercury 13,900 mgil Weekly Composite Conductivity.....B 0.28 ugll Weekly Composite Temperature Grab U,D Total Phenols Daily 1.8 rJ°.�.1} Grab B,U,p Chronic Toxicity —Quarterly ugtl Weekly Crab lvetJ, 4i Pollutant Analysis —Annually Composite B S Nix REQUIREMENTS FINAL NCOOC During the period beginning on the eff( Permittee is authorized to discharge frc shall be limited and monitored by the p, Effluent Characteristics Mon. Avj lb/day Acenaphthene** 0.39 Acrylonitrile 1.69 Benzene 0.75 Carbon Tetrachloride 0.32 Chloroben zene 0.31 1 ' ) A-TT4r-hl,% ZI V =- Hexachlorobutadiene 0.35 0.8E Quarterly Grab E Naphthalene** Nitroben zene, 0.45 0.48 0.50 erly Grab E 2-Nitrophenol*** 1.23 1.20 1.80 Quarterly Quarterly Grab Grab E E 4-NitrophenoI 2,4-Dinitrophenol's ** 1.80 1.80 1.80 1.80 Quarterly Quarterly Grab Grab, E E 4,6-Dinitro-o-cresol*** 1.37 1.80 Quarterly Grab E Phenol*** Bis(2-ethylhexyl)phthalate 1.56 1.81 1.80 4.91 Quarterly Quarterly Grab Grab E E Di-n-butyl phthalate Diethyl phthalate 0.48 1.43 1.00 Quarterly Grab E Dimethyl phthalate 0.33 3.57 0.83 Quarterly Quarterly Grab Grab E E Benzo(a)anthracene** 0.31 0.50 Quarterly Grab E Ben zo(a)pyrene** 0.40 0.50 Quarterly Grab E 4f (Continued) Measurement Sample *Sa Frequency Type Loe quarterly Grata E vuwtvlly `afau A. (.. EFFLUENT LIMITATIONS AND M Q G REOUIREMENTS FINAL Ds —.+ XT— 'Mt- A11-'T . —4—a w i, acstrat ulp x-vamucc is autrionzea to QiScnarge trom ou s al number 00 . Such discharges shall be limited and monitored by the pennittee as specified below: ffif�luent C'�aracterlett91 1111 ae Lt;»ttmtjr,4 Manitc�rt egg ! ment Units to 191 t .utement Sar»Rle !2AMAIA Doi v _Mse . E eauencv L Flow Continuous Recorder E Total Suspended Residue 22.0 73.0 Weekly Composite E 000 10.0 1.0 Weekly Composite E;' Organic Pesticide Chemicals 0.02 0.12 Weekly Composite B©D, 5 Day, 20 OC 19.0 89.0 Weekly Composite E *Sample locations: E - Effluent, I - Influent The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units and shall be monitored weekly at the effluent by grab sample. 'There shall be no discharge of floating lids or visible foam in rather than awe amounts. Discharges are to be released in accordance with the following: Stain, ecruiremets If at 'lease one turbine at Mt. Island Dam is operating at the beginning of each discharge day, BOD5 and 'NH3- released in accordance with Equation No. 1; until 7:00 p.m. If no turbines are in operation at 7:00 a.m., BODS doan be 3 N can be released in accordance with Equation No. 2, as defined below, until turbine operation begins. When at least one turbine at Mt. Island Dam begins operating, BOD5 and 3-N can be released in accordance with Equation No. 1 until 7:00 p.m. If at lease one turbine begins operation after 7:00 a.m., BOD5 d 3- released in accordance with Equation 1. At 7:00 p.m. the "total daily stream flow during the 7:00 P.M. period 24-hour average discharge rate will be calculated which will include theminimuminstantaneousw dflow quantity nt t follows. A lus 1CFS 7Q10 from DutchmanCreek (i.e., if 30 x EE /360 ft3 was released by one. turbine from 7:00 a.m. to 7:00 p.m. Ithe 24-hour average would be [30 x EE6/3600 x 24 + 80 + 151 = 4.). If the 4-hour average flaw rate is greater than or equal to 329 CFS, BOD5 and NH3-N can be discharged from 7:00 p.m. to 7.00 a.m. in accordancewith Equation.. No. 1. If the 24-hour average flow rate is less than 329 CPS, BOD5 and 3-N can be discharged from 7:0 Equation NO. 2. If a lease one turbine begins operation after 7:00 p.m., BOD5 and NH3 - m. oc g00e relessedcinrac accdance ordance ce with Equation 1. EQUATION NO. 1 S er l Winter 2' BOD5 + 0.4 ( 3-N) 111.1 Ibs/hr. avg. BOD5 + 0.5 (NH3-N)< 197.9 lbs/hr. avg. (333.3 lbs/ r max.) (593.7 lbs/ r. max.) EQUATION NO. 2 BOD5 0.54( -N).� (a) lb/hr. BOD5 + 0.31 ( -N) (B) lbs/hr. BOD5 BOD5 discharge rate, Ibs/hr. 3-N = 3-N discharge rate, Ibs/hr. Discharge Day begins at 7:00 A.M. A and B are; defined below e hourly rates will be calculated dividing daily discharge by 24) A,_ lb hrl Ib hr Flow: CFS Av Av 95 to 175 23.6 47.2 54.2 108.4 75 to 250 4.587.0 99.8 199.6 250 50 329 84.5 169.0 150.3 300.6 NCO0043 `5 Fart III Continued F. This permit shall be 'modified, or revoked and reissued to incorporate toxicity limitations and monitoring requirements in the event toxicity testing or other studies conducted can the effluent or receiving stream indicate that detrimental effects may be expected in the receiving stream as a result of this discharge. G. The effluent discharge shall at no time exhibit chronic toxicity in any two consecutive toxicity tests, using test procedures outlined In: ,.,,� • .,�,. �.�.A - A,c eae ea %;,upeaill i aecse) or suosequenr versions. &;atvw all a eaernenr processes. 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 hemieallpt measurements performed In association with the toxicity tests, as well as all do eire data. Total residual chlorine of the effluent toxicity sample must be measured and reps chlorine Is employed for disinfection of the waste stream. Should any single quarterly monitoring indicate a failure to meet specified limits, then monitoring will begin immediately until such time that a single test is passed. Upon p this monthly test requirement will revert to quarterly in the months specified above.' - NOTE: Failure to achieve test conditiont control organism survival and appropria test and will require Immediate retesting to submit suitable test results will consfi, plant. The discharge shall be evaluated as follows: requirement is to be referred to as the "10 significant peaks rule*. ALLOCATION Modeler Date Rec. �# h CJ � c4E " tutArrd Drainage Area ( ;1L _ Avg, Streainflo\v (cfs). _ 'a e7QIO (cfs)�n 7Q10 (cfs) 30Q2 (cfs) i� Toxicity Limits: IWC 1. Acute .hrcEc Instream Monitoring: Parameters Upstream Location Downstream Location Industrial (% of Flaw): q 8'010 Euent ointnent : Characteristics 1�MAY RECEIVING STREANI., SO_ Class: c Sub-Bas i t : Reference USES Quad: , (please attach) JJ U01111tY. c : Re-ional Office. Requested by: Date: Prepared by: r' mate. W113 Reviewed by: T ate:Comments: 7hL_dbh � �. fP Ted. t t -T> , Request No :1 3` e ------------------- WASTELOAD ALLOCATItN APPROVAL FORM - _---- - -4*-- " Facility Name: Sandoz MARS NPDES No. NCO004375 Type ofIndustrial Status • Existing a.•t t . Receiving Stream: Catawba River � Classification: WSIII Subbasin 030834 Drainage ar as2011 County: Mecelburg Summer 10 32 (R) Regional Office:Winter 71 Requestor Har(orig.) Average flow: 3016 Date of Request: 0Q. Quad: F14SE' RECOMMENDED EFFLUENT LIMITS - - - --~--- ~~ Mo ; Idly � - cv•� - - (� Avg Max `�� Wasteflow (mgd) 3. (Year Round) .� `' . NH3N (lb/d) 651 77`P $ Mercury (lb/d) 0.0 and. .4 ug/l Phenols (lb/d) and no concentration limit Sulfate (lb/d) 4,100nd no concentration limit .._ .,— Specific phenolic compound limits will be the B and NSPS limits in Federal Register. Phenolic compounds include:`'-Chlorophenol, Mercury concentration limit may be increased to 5.3 ug/l if diffuse installed. Recommend inclusion of the attached staging requirement. Recommend use of an additional DMR page similar to one attached: to monitor compliance with BOD and NH3staging requirements during summer. The statement that Natal polynuclear hydrocarbons shall not exceed 0.50 lb/day (15.5 ug/1) shall be deleted from the permit. ------------------------------------------------------------------------ Reco ended by: {4u J Date: Reviewed by Tech Support Supervisor`; 14Date* 514io Regional Supervisor 4 -"- .. Date Permits & Engineering.Qyts:�.2—UDate: ,1, RETURN TO TECHNICAL SERVICES BY: Al f 0 ti l 1 - October 31) i am to 7:00 am. Each day, parameters, will not exceed the value given in the following foi mulas: When daily; average river flow is calculated to be <= 175 c BO 5 + .54(NH -N) <= 566.4 lb/d When daily average river flow is calculated to be > 175 cf. but <= 250 cfs BOD5 + 0.5 (NH -N) <= 1044:lb d l Additional DMR Sheet for Sandoz EFFLUENT NPD S Permit No. N O004375 Discharge Month Year Sandoz Class 4 Mecklenburg County Operator in Responsible Charge (ORC) Certified Laboratory: Person(s) Collecting Samples: Check if ORC has changed 1 certify that this report ; is accurate and and complete to the best of my knowledge. River Allowable Actual w Flow BOD5 NH3 BOO+, 54NH3 BOO+.54NH Comp? 1 3 4; 5 6 7 8' 9' 10 11 12 13 14 15 16 17' 18 19 20 21 22 23 24 25 6, 27 28 29 30 31` Average Case 1 t ; River Flow <= 175 cfs BOD5 + 0.54NH3 <= 566.4 lb/d Case 2: 175 ofs<River Flow< 250 cfs BOD5 = 0. 4NH3 <- 1044 lb d Case 3: Riv.' `low 2 0 efs, BODS<=852 l /d (me av ), BOD5<=2236 lb/d (diy max) NH3<=651 lb/d (mo avg), NH <=977 lb/d (dly max) DIVISION OF ENVIRONMENTAL MANAGEMENT March 8, 1990 kffiMQ_NQ9_M_ TO: Sandoz WLA File FROM: Ruth Swanek SUBJECT: Sandoz Draft Permit Changes NPDES No. NCO004375 Catawba River (030834) Mecklenburg County On February 9, 1990 representatives of Sandoz met with DEM to discuss the draft permit for the facility. The permit was modified to include a flow limit of 3.9 mgd year round. This new flow was then used to develop a BPS' limit for ammonia assuming a concentra- tion of 20 mg/l. The resulting monthly average limit was 651 lb/d. A factor of 1.5 was used to develop the daily maximum limit of 977 lb/d. Since the new BODS and NH3 limits were more stringent than in that the stream flow was equivalent to the minimum daily release. Since the flow of the Catawba River is usually much higher, the phenols in the effluent should not cause taste and odor problems when only the mass limit is assigned`. Therefore, the concentration limit was dropped. The sulfate limit was dropped for the same rea- son since the company had initially expressed concern;, about this limit. The company also revealed that it would prefer to meet the specific phenolic compounds limits given in the Federal Register although compliance with some of the effluent` guidelines would' result in noncompliance with the total phenols limit. However, this action makes the company noncompliant with only one parameter rather than two, and this request was granted. Sandoz provided us with information (attached) which indicates that the North Carolina standard for polynuclear aromatic hydrocar- bons (P s) is based on individual concentrations rather than total concentrations. The information was reviewed by a TENT chemist and it was determined that the company was correct. Therefore;, the statement that total PAHts could not exceed 0.50 lbld (15.5 ug l) was deleted from the permit.' Finally, the company reported that fifteen substances have been remanded from the C CPS ' list. ERA, has told us that only one substance has been. remanded. This issue is currently being resolved. c es - 5) ' poi 1 f l- November %. t3G i A 4 s o t`s A cl,! `I}� € t5.a t1 ' w. -, �, •-C,.:i .ice,. } tip, ad ii �.. ,. �# 3 11 .t§,. `k r the cl ss V 1 �fi .s t t " 3 , i C" t.t 2 .1..' C'"r .C' Y a t '1'# ` :� 6) wei C _ a c ='c3 ' C, eF ,a re L Vlr�. iJ S�.cns S ^ al- l' a_r ac t t.., tic a u 'i.i _ : ,0 d..m , rcd `.3w?,1.5 al azly `rse +';i2t.se'ri _,. .. } ;i `. clf`' 23i Pid KC} 11J t L ...i ., .+.i t' oast be t veloped on a coo oo..d- }° r 3c7-'::['t`. to sue"a si thepossibility of t:a r agile # GC".iTpiai3 Ttd la'a$i:. health effects. : # *tG p iC7 r"#n tissue It 'Should �f moored that the sLx .�r,>_ i_ Close i-xsta s y�h e level to .., .' y t r �� #r't C 6Y n t'-6 �L` 4.'_-' -. . a, va.t' t st ., � 4 iIlaul;toe, tiles cv CLi. Cc t ica. s u 3..+ n :,011� -. �.* of ea-' a „; a to a°:^GuT1t:f peGleS following statement is tt? be .�r.cieOUaie taAi thin o -.ides � More variability. Consequently, the mg1 appropriately inserted: a TOup pro coulpound� �� s o�F F other to o i er ion t surface area/day conversion factor is gat data are not available for reasonable basis for exuar onit1i1i serve class than Minimal not used in the der; a at;on of toa roil} Sufic to derive e a ley'ei which it ool ciernicals of w o e c.. rni^al nr a few chemicals bas�ad r,terion. protect a„ainst L.,. p_ :ea l toxicity of #his c'ata an v ifh n the p ,rp ,r� C. ,:S_-rxlJ?ep!ic �+:",",'`eatio GiJ�1Ti{�tlnc : 'i S rnila S 12 tiI'w nature t7- t?7? ' to Cher icals it L"e cars t ' ,; c. ""i.�.i "y'.,G criteria GF itiie �y t�+ /'+{ !1, .+iFi' I`JQ yro r Cho :1cal Classes �por'~ i(i}.IGe`�i �3C�7" support ft7F cl'i�' �`i"�x t..tIOA p c cr=al 5 Of A a4,erialS vvhiGlr al class is broadly ee�:nod as tx r .Sa .o other; nlernbers of the concentrations g??p 6rE 1 ridVsirable taste aril or iadCli iCi C11erA any ratap of Ghe ..zc l C1 SpCLL dS yt"f loll 2t A r class, ± ay be s3 ilc:. Irr Co if;aSt. to here the water. I dey'elopit.g and utfl3 tn; s'ach reviewed in a sz rgie r.s4 e �e vent h olc Lk:cat respo^se has been shown to diifcr criteria ty��a facto.s must be appreciated: are ieiit. in criterion derivation. Y ti Ma ltedl:'S on a GLSx3likct24'P and iS�:aA$#.a.,ye : rile lrTi"r1#ratiL3nS r'y2:;?St organoleptic data GrQ!;ii? isomers should be -egai ded as a Part of t. Lsi5 for Gl' xe'.oi" _all within a ciass.: the to other members and the human health significance of a chernical class rather than'as a srrigle extrapolation, of a criterion of ;hat class is riot appropriate. organoleptic properties. + compound. class c:_tenon is an 4• Additional sulaprart for the validity of The publications;whfch report taste ni„l a her to of r:s3c%sa ety r'P ofa cr=ieritr, to other vie nbers and odor thresholds are, with few estimate than one rriefnlaer of a class. It extrapolatic;s class could be provided by evidence of exceptions, crypticintneii descriptions more involves the use of available data on of a � ,�,Ftsroc attoaie and pharraacd l:netic data of test methodologies, number of one or more chemicals of a class to forSome m nbers of the class, si:b;s"Wts tested, connerib-atioc. response derive criteria for otsier compounds of r tkm nbCy"e CC1nsSderations. it re? 1cnships, and sensory the same class in the event tliett t'aeae B e Ct be ,,,,;'fable in some cases to } characteristfes a' specific: izty threshold. h�s. c"e;i' insufficient data available tc} +.:eri�'*e ma-,- r diviCIe a cheoiical Gass into various conceentratiOns above cc+ ound-specific criteria, tclass kisses. �cich diy:siorrs could be the csualit}° a3 orb arcte r;ic data s often ,� c; ierion us al.y` applies to c zrl ' biclogical endpoints (e.g„ sig~iifrcantlye less than that of to .. ologic �. +t- - ,; than F:3'.l: merr ber of a class at:. e kin to l se , sti *"5 :1o2`i-Ga:c3Tkloge^5. , poti.:rrCi'. L data used rfr @u: #alrex3. S other G.S eau. the vilTri of the CC} o rnds Nvithin xihe cars-.-,n�,. rut 1 3' 1Ct" of data (erg.. a Consequen .y, a critical eva1u ,tat*: sat be ,� � aI hazards of MISS. �`� t` potential id#'dr l for socle ;oe _ 2r,xerS SJ.f 3. C.taSS the available orp;,anotcptic data musx. .+.axe i l.apFe :oa:smart exposure a not t, l a d.ikelion ..For, for o*kars)-1t �:le no a r tat?e ar<.tl t e se=eC,ion of he most r ,.x. axe ed a criterion b, c f tics^, but � a rid fslsced ran t`ie extent crabs app op x to d :ta Base for the trite. on ry r, 5+t Cf3x ""`.t i+ s tr✓i in indi � t al each r:7t".at be based yips sound scientific m� t made far Exceptionsy. fi lryr tCs.k .:.at Linn o [^ be explick OY -. luw>g r �rx. va Lad ,aria ,.a poz.iX-i. .. —mixtures Iti cn are p ld d Cx P subc �., tli4 tfon 9'arst k F 3 eR +' { riot ri+ic c=t are not M a no t P r C an .r ei teLJeds ancr t''Z )uful C 1x .;7 s. 3 La z o3 l { if l,il s tic derived ail a o ttaiJctG tv potential earl e?'Sf ( ni}xti res e- ., toxa ent :; o ems)- ( g � r r %a f � r lit C ' Is+it1e u y .dt _ 1.}"'sC d'�rrct re t •>sr,S za j` f ict3 "..k health i sUch exceptions, 5 SOr" r } e,1 r"t s �i W+w x ¢ 4 (} 1.0 q e"..t KMS r xxlka numen iA y^ t s"i 1'i: to s se- 0 17auli i'"'� 3�}t~ 'wi3 ry t to ,e+yI�Lu$ tip.e e cteu or t` vti. 1 t 3, - •'�. t�'� k 1 G x .t Lai C Cl co C s. f,' L. {. 'v .:.k '�} L tt.«3 -t ( �Knd. salt i i� R..,at � t» .. L.. i1 V"y t i }C [t : i"CYt XS # G+?G"" { k,, n a a a i f olio s.rasikcs oa to r #r intake� yx 1 # S`i �. e .' o a 1 t. ^spur{ nod „a. r `l}e: 1i n, t Sri if:.o' t ere ions enors ri" :. i.uid .tt`il ° 0 + ..'�Si S ety L` i c;rad_iS7a on ell£' 1 e1' ltc C} .... } fee t .a O: i3ic' °ire^+, }� on 1 Lti ,Flat s t ofAl s ;Liu l i e , 2NO cle � . d in asse.cse an a a op art tar} c m ant has a Ci:: C i'sl tit k nce 1.._,a y she ;Ct .. k-st, ?,. E,1G, "i". CT ... ',+,S rlty. €t7 *.� "ctif Y .7 t y tie iwx!r fi .: : L, !Ca are kd C iP E'.Ct. t C' Gl �J:i ,it (,.r}tk "`l1 if is ;,y dta b:e#.. t a .. ... i S.. ik,B i, a n .c:: e * i S a class '3f co Ci..i.,...s Lae E ."ti c L } ik i 0 #CA and scienilfic reaa3o fin g. y�i Lr L r".lk G i tfrx } C.e .. k'u'.J # M 1' t" .. i"G. ". C`i t?"t e("i 4.. �J a3i i �3t.fr " on l S t i" # rytt of sufficient data on f 3e C - Cr k ..Ia it r x. t es ,._. a. uali.:es da-1 are a ,l 1?S a c.al aGiWI ttie rev u. t T t' 1N °aa ere; Si7 ,1. in physical, chemical, C stL Sr should t inmirr.r.ed h r l z,^ #iC, C7i tCiXIGC1J3G t.rr on It ri e .n bu i,al.h s�, r en# toxicoitsgrc data are a.'a,isfile 1' `ti ` s to i ast f� a class criterion s o a c a .3:1t i-> # Gn c t. ,e pica yvitha 2 class, a S.;t c i )• _. d t,.j `. r't is G:llt `vrA the ec. rC L.s 4e ,,-5 ,'„? c { A C C L be aJ:r-'nCt .c .f"�...�, uPE xkC t 3L t 1S C t. "a 1 x }.,,an k c � ".,4.i.11 and the i s l oft.. r.A e iY F D C S etil i fl vex} e i + for J r ,� t { G,, a „. �} r .:r. t� ic'#�. e;4 r"AeSI ( 1».et C ry lift , ..:io .d _h #i: - '¢.#.Vitt tii tE. classes, sciert...t`it' =ci + ant may S ° Est Consequently, IS &iT_pere�t:�"e tllr�.t t.i"iG' In G Y e.::c c,� .s. _ '..*e.. '.,? f..' .a's is �, +"�' sufficient. de-ree of SI?' ilc' ti• ``3E�'."1Vr"EtlC7T1 SeCtIUTi or eaf„13. t y't'le" S o.' d ,a, ,?t�'.,...ky Gh4rniGGkJ °x ill thin classto fi.,.u;lly f�i CI`16eriC7'"I i °icl class c raterit i is rased. � class or,# = o ipp,f able to s >,.v car all d ar e a' tv i a �r =d c l'}te"Iti ciG'.Ir LS iii:Gtl of � - f y7 S tar C Gi sue« „L s, C al; t L+ .'t""' S fix sc i *tile - 4' t i t w e e' � 4 k AITT l + r ij DailMax Mg Avg, B lbld) : 0.50 (W) 0.40 (BAT,NS b/d): 0.50 (WQ) 0.39 (BAT, NS 0.50 (W) 0.9 (BA.T, NS 0.50 (WQ) 0.39 (BAT,N 0.50 (WQ) 0.9 (BA, NS 0.50 (WQ) 0.9 (BAT, S 0.5i (WQ) 0.9 (BAT, N 0.50 (WQ) 0. (BAT, NS ld) : 0.99 0.9 B 1.63 0.53 B 0.95 0.37 BA;T, NSP 4.70 1.52 9.01 (WQ) 7.39 (BAT, N 277 ar. is compounds include: 2 Chlorophenol, ; 2, -Diehloropheno m th 1phenol, 2-Ni roph nol, 4 Nitrophenol, nitroph nol, 4, 6-Dintro-o-care ,cal, Phenol. nie Permit C R NSC TCt 1ClTY TESTING REQUIREMENT ( t t discharge shill at no time exhibit chronic toxicity ifa tuay two r cedures outlined in - at arccesses. , testing results required as of t hhis permit condi.ion will be entered i1� onitorirag Forma (MR-1) for the month in which it was performed, Iasi R Additionally, DEM Forma AT-1 (original) is tobe sent to the follov Attention. Environmental Sciences Branch North Carolina Division of Environmental Manaaenient P.O. Box 27687 Raleigh, N.C. 27611 nt tonicity sample must be measured and reported if ite stream. arterly monitoring indicate a failure to meet specified i immediately until such time that a single test is pas; 'ironmental Management indicate potentVial'imp;,cts to the receiving .e#opened and modified to include alternate monitoring ret uirenaew to achieve test conditions as specified in the ci-,ed document, such -n survival and appropriate environmental controls, shall constitute immediate retesting(within 30 days of initial monitoring g evert). l tilts will constitute noncompliance with monitoring requirements. --3. CMGD Recommended bv isin 7 ;late icity (Cericacl4aphnia) P/F at 1, °r, , See Part � + r Type of ProductProduced Lbs/Day Produced Effluent Guideline Reference t eata Request No.: 5314 WASTELOAD ALLOCATION APPROVAL FORM Facility Name: Sandoz Chemicals Corp. NPDE`S No.: NC O004375 Pipe 002 Type of Waste: 100 Industrial Status: Existing eiving Stream: Catawba River las i'ication: WSI11 Subbasin: 030834 Drainage area; 2011 sq m County: Mec l nburg Summer 7Q10 329.00 :: s Reg gional Office: C? Winter 7Q10 :s Requester: Lula Harris Average low: 3016 c s US ,s to of Request: /14 09 30Q2 c s e6v. Quad: F14SE Recommended Mta Avg Dly Max BOD5 (lb/d) : 19 89 B T TSS (;lb/d) : 22 73 BT pH (su) : -- 69 B'T, WQ' COD (lb/d) : 108 156 BP de ahem (lb/d) z 0.02 0.12 BPT Testing Req.: None MONITORING (Y/N) : N Location: (Y/) : N Location COMMENTS tually discharged through out all 001. Waoteload inclu at being discharged. eco ended w. Date: rt Supervisor: Sete: °al Supervisor: Date: Engineering: Bute: JRN TO TECHNICAL SERVICES BY: oL' the Pe ittee is period beginning on the authorized to discharge effective date of the from€sutfall(s) Permit and lasting . expiration the limited and monitored by the Pe, ittee serial n ber(s) 001. as specifiedbelow: Such discharges shall ient actetistics Pisch e h° itatio itor" R :�` is s dad DailyAvg. Daily H her Un,its (peifl H+ t l l Iaail A fail re e Location Su r (April 1 - O toia r 31) 3.4 MGD Winter (November 1 - March 31) 2.6 MGD 714.0 1940.0 Continuous Recording I or Suspended Solids" 681:0 2189.0 Daily Composite E .s Nt tived Oxygen 20.0 g/I 20.0 mg/1 Daily Weekly. Composite Composite E E Coliform 5.0 m /l 3.0 mg/l Daily Grab E Residual Chlorine 1000.0%100 ml 2000.0/100 ml Weekly Composite E Phosphorus Monthly Composite E Nitrogen ( _ + NO2 + NO3) Monthly Cbmposite E 7 10.0 Monthly Composite E �.c Pesticides 0.0 01 0.079 Weekly Composite E nese 90.3 90.3 Weekly Composite E 273,0 273.0 Weekly Composite E rotors Weekly Composite E to 898.0 898.0 Daily Grab E ry 0.11 0.11 Weekly Composite E Is i is 45.0 ug/I 78.0 ug/I Weekly Weekly Weekly Composite Grab E itv Pollutants �` Monthly Composite E wally E monitored daily. EffluCharacto-ristics L,M f-- Measux le Upstre East Bank Sample Locations e I-85 Approx. I mile downstream t or Immediately above BOD5 Near l- 5 Belmont Intake as N Weekly Composite + + Dissolved oxygen Weekly Composite + + + p Weekl y Gral, + + + + Conductivity Weekly Grab + + + Temperature Weekl y Grab + + �' + '+ Phenols Weekly Grab + + + Weekly Grab + + + Denotes monitoring required at specified locations. fiat ly above nont Intake Dissolved Oxygen oon�.nly Composite + %mi7ntti Grab + + + + p Conductivity + 2/month Grab + + + � + + "temperature �t/ tatC821'�h r3�i ++/month + Phenols Grab - + + + Weekly Grab + + + Denotes monitoring required at specified locations. * r, •r .s t: •s e expiration the taxges shall be �icenap ne 22 59 Acrvlonitrile 6 242 Monthly Grab E Benzene 37 136 Monthly Grab E Carbon Tetrachloride 18 38 Monthly Grab E Chlorobenzene 1, 2, 4 15 28 Monthly, Grab E Trichlorobenzene 68 140 Monthly Grab E Hexachlorobenene 15 28 Monthly Grab 1, 2 Dichloroethane 68 2`11 Monthly Grab E 1, 1, 1 Trichloroethane 21 54 Monthly Grab E Hexachloroethane 21 54 Monthly Grab 1, 2 Dichloroethane 22 59 Monthly Grab 1, 1,, 1 Trichloroethane 21 54 Monthly Grab E Chloroethane, 104 268 Monthly Grab E Chloroform 21 46 Monthly Grab E 2 Chlorophencl 31 68 Monthly Grab E 1, 2 Dichlorobenzene 77 163 Monthly Grab E 1, 3 Dichlorobenzene 31 44 Monthly Grub E 1, 4 Dichlorobenzene 15 28 Monthly Grab E 1, 1 Dichloroethylene 16 25 Monthly Grab E 1, 2 TransDichloroethylene 21 54 Monthly Grab E 2, 4 Dichlorophenol 3 2 Monthly Grab E 1, p Dichloro ro e 153 20 Monthly Grab E 1, 3 Dichloropropylene 29 44 Monthly Grab E 2, 4 Dimethylphenol, 18 Monthly Grab E , 4 Dinitrotoluene 113 285 Monthly Grab E 6Dintrotc�lun 255 1 Monthly Grab E Ethylbenene 32 108 Monthly Grab E Fluor there 25 68 Monthly Grab E Bis (2-Chloroi opropyl) ether 301 757 Monthly Grab E Methylene Chloride 40 89 Monthly Grab E Methyl Chloride 86 190 Monthly Grab E Hexa hlorobutadiene 20 49 Monthly Grab E naphthalene 2 59 Monthly Grab E atrbenzne Monthly Grab asA..9.SS 1L8A�5.i [IUMIU1%,1V REQUIREMENTS Final During the period beginning on the effective date (!� /� PT�BS �Ci. j�.�f.Y f� �IC000435 Pe ittee is authorizedto limited d monitored by of the discharge fromo tfall(s) serial Permit and lasting n er(s) 001, Such discharges io the the Pe fttee as specified-bel ges shall be Effluent cterist is yy �a p49py yy j y h �..4s Vl$ 'G .L$ Y. .Ltat.LV � p iA:&.tYJr yq R y yn l axlY g T3s lv M Other x.ts (Spec. )[e a l �V *. TI "lv t le leq -Nitrophenol H82 $�a �ro C +0.. cy ype t S.fl 4- itrophenol 41 72 9 124 Monthly Grab B 2, 4-Dinztrophenol 71 123 Monthly Grab 4, 6-Dinitro-o-cresol 78 277 Monthly Grab E Bis (2-ethylhexyl) Phthalate 103 279 Monthly Grab Di®n-butyl phthalate 27 7 Monthly Grab E Diethyl phthalate 81 203 Monthly Grab B Dimethyl phthalate 19 47 Monthly Grab E Benzo(a)anthracene 22 59 Monthly Grab B Benzo(a)pyrene 23 61 Monthly Crab 3, 4 Benzofluoranthene 23 61 Monthly Grab E Be o(k);fluoranthene 22 59 Monthly* Grab B Chrsene 2 59 Monthly Grab Acenaphy�thylne 22 59 Monthly Grab thracene 22 9 Monthly Grab Florene 2 59 Monthly Grab B Phenanthrene 22 59 Monthly Grab , E Pyrne 25 7 Monthly Grab Tetrachloroethylene 22 56 Monthly Grab Toluene 26 60 Monthly Grab Triehloroethylene 21 54 Monthly Grab Vinyl Chloride 14 268 Monthly Grab E Total Cyanide 1200 420 Monthly Grab Monthly Grab B M3 If at lease one turbine at Mt. Island Dam is operating at the beginning of each discharge da- r:�lease.d in accordance with Equation No. 1 urzt�%1' 7 � 3i2 P.m. If c� turbinesare in o?aeratcan at i : (�#� BOD5 e d �" c e c be released in accordance with Equation No. s , BOD5 and 3-N � x defined below,; �aa�ta? turbine 'operation begins. When at least one turbine at Mt. Island begins 'operating, BOD5 and �-N c b released in ' accordance with Equation `I >. M. at lease one turbine begins operation afire ; . t p.m.,' m. , BBOD5'a ci 3 N c be released in until 7:0o I Equation 1. At 7:00 .m. the total daily stream flow during the 7:00 m, accordance with 24�-hour average discharge rate will be calculated wb-ich will include thetrain urriin taneouus low determined as 'follows: tA S 7Q10 from DutchmanCreek (i.e., if 30 6/3600 ft3 way; released by one turbine from `:00 a,m to quantity talus 15 Cl"S average would be tl x E6/ F Cl 4 80 15 44 r). C P.m., the 4-hour If the 4-hour average' flow rate is rester than or , CPS, BOD5 d -%' discharged from i : �7ti �:. t�� ;': g� equal to ,�9 average flow rate 'i less than 3 FS, BOD5 and N,1H3-.N c.an be discharged from d7:00 o,w.. toith - No. if the -hour Equation NO, 2. If at lease one turbine begins operation after 7: 0 ; a.m. in accordance with with Equation 1. p.m., BOD5 aiad NIH3-te can be released in accordance EQUATION NO. 1 er JQ Winter 3, BOD5 + 3.4.5 ( - ) < 111.1 lbs/hr, avg. BOD5 + 0.5 (NH3-N)< 197.9 'lbsf Ibr. avg. (333.3 lb / r ) (593.7 lbs/ r. max.., EQUATION 'vt5.2 BOD5 + .54( 3-N)< (a) lbs/hr. BOD5 + 0.31 (NH3-N) < (B) lbs/hr. BOD5 = ;BOD5 discharge rate, l bs/hr. 3-N = 3--N discharge .true, lbs/hr. Discharge Day begins at 7:00 A. M A and B are defined below Me hourly rates will be calculat«-d dividing daily discharge by 24) A 1 her (b hr3 Flaw= s Max, A 5 to 175 23.6 47.2 54.2 1C8, 175 to 250 43.5 87.0 99,6 � 6 250 50 329 84.3 169.0 150. 3 300. F. Toxicity Reopener This permit shall be modified, or revc Permit No. NCO004375 ed and reissued to incorporate toxicity studies conducted on the effluent or receiving st7:eamV indicate that d( effects may be expected in the receiving stream as a -(,suit of this dl G. Chronic Toxicity Testing Requirement The effluent discharge shallat no time exhibit chronic toxicity using procedures outlined in: 0. The North Carolina Cerigd4phi1ja chronic effluent bioassay procedu Carolina Chronic Bioassny Procedure - Revised *Februnry 1987) or version. The effluent concentration at which there may be no observable inhibit reproduction or significant mortality is _6% (defined as treatment tw in the North Carolina procedure document). The permit holder shall pe monthly monitoring using this procedure to establish compliance with t permit condition. The first test will be performed after thirty days issuance of this permit. Effluent sampling for this testing shall be performed at the ND ES permitted final effluent discharge below all treatment processes. All toxicity testing results required as part of this permit condition 110 Anf.v-14 -- 4-1— ",! - -1 - - ,. <. - I--- - III k I fix - J ) I UT- Lue mon'Un j,n i ,formed, using the parameter code TGP313. Additionally, DEM (original) is to be sent to the following adcir(-.,;s: Attention: Technical Servicns BrnTir.h North Carolina Division of Environmental Management P.O. Box 27687 Raleigh, N.C. 27611 shall be complete and accurate and Include all supporting Ilysical measurements performed in association with the toxicity test all dose/response data. Total residual chlorine of the effluent 9mple must be measured and reported if chlorine is employed for )n of the waste stream. test data from this monitoring requirement or tests performed by th Lina Division of Environmental Management indicate potential impacts Ing stream, this permit may be reopened and modified to include ionitoring requirements or limits. .ure to achieve test conditions as specified in the cited document', control organism survival and appropriate environmental controls, s an invalid test and will require immediate retesting (within 30 day itoring event). Failure to submit su.itaf)le test results will a failure of permit condition. Permit No. NCO0043 IT, Priority Pollutants The permittee shall conduct a test for priority pollutants annually after combination Of all waste streams in the main discharge pipe. The discharge sbaY be evaluated for all volatile fractions, acid fractions, base/neutral fractions, and pesticide fractions listed in Table 11 of Appendix D. of 40 CFR Part 122 and all metals, cyanide, and phenols listed in Table TIT of Appendix D. of 40 CFR Pal 122. The permittee shall test the effluent for any pollutants listed in Tables I and V of Appendix D. of 40 CFR Part 122, if ' -a specific pollutant is believed to I present in the discharge. In addition to the above testing requirements, other significant levels of synthetic organic chemicKs must be identified. For the purpose of implementing this requirement, the largest 10 percent of the GC/MS peaks other than the priority pollutants shall be identified. All tests shall be performed in accordance with the EPA Reference Methods listed in 40 CPR part 13& No process wastewater from log debarking processes shall be discharged from this facility. No processes shall be discharged from this facility. No process wastewater from the wasbdown of veneer dryers shall be discharged from this facility. No wastewater containing plywood glues, wasbwnter containing glue wastes, washwater from machine clean-up operations, or other process wastewater from Plywood manufacturing processes shall be discharged from this facility. The phosphorus limitation contained in this Permit may require the construction of additional facilities for phosphorus removal at the wastewater treatment plant. The Division of Environmental Management will reevaluate the rating of th, wastewater treatment plant at the time an Authorizntion to Construct is requested. If the facility is determined to be a class ITT or TV plant, the monitoring will be adjusted accordingly, resulting in d&JY monitoring for most Parameters listed in the permit. 4 \ A S STATE OF ,NORTH CAROLINPi DEPARTMENT OF NATURAL RESOURCES AND COMMUNITY Y DEVELOPMENT DIVISION OF ENVIRONMENTAL MANAGEMENT 'ERM i To DiSCMARGP WASTEWATER UNDER THE NAT I NA1 _PPMTANTNATPA AGE ELIMINATION SYSTEM In cOmPliance with the provisions of North Carolina Worn! Statute 143•215.1,' b r la,,,ul st:xanclnrds and rcgulnt:fOns promulgated and <tdolded by the Igor%} Carolina vironnont;al Orrs;gement Commission, and the {'ederal WOOL Pol Ju io" Control Act, ns ended, Sandoz Chemicals als Corpcarst oD hereby nothorize4 to discharge wastewater i't`om a V,ar. i l it.y ;or:nt d on N.C. Highway 27 North rroceivinj{; 1Vtt"Ftors }`eN1 n.�.e.7 q Or r T,�r r i it r°4 n r1-WoY R sir .. � too �.Ci. rtk+ i`.`i t ittq = accoloplan with fft""nt h.x_xit.aLions, rtl'.:.t.inns not tQr"Lh ito :Caitsr.1tf., a7.`}( .t.i[ 1r•-��:.k1 s permit YOU become effective s pa?3"r6it: nI'd isttr3: authorization to rtigd;har.ge N°-1%i.. :r t E°xpirn t`3t. r'1,l.dCI1SLt oti "ad this day R. Paul Kim DMAOI- D. ivr.:i7r,.`n a Fpr°.!Y"d".C.CientV t 3aYPnljihmenf By. Authority t"t{ th" +',avir9i:C'3;•eSt.rY t#tlilag*F:m'`n: t:r;tTTttidi..`isjoa SUPPIXMFNT Sandra is hereby authorized to: Permit. No. NCO004 ' CO PERMIT COVER SUET Chemicals Corporation CD Oastewat er treatment facil i.t ins for acid neutralization, f Ong, biological treatment, thiosul __ _ __ , ,s, uvxky c. �e�:_ t z this, Pn aajt chlorination, and post aeration located on N.C. Highway 27, N< Charlotte; in Mecklenburg County (Sep* Part TTI of this Permit), and Discharge from said treatment works into they Citnwba River wi classified Class "WS-TTI" waters in the Catawbii River Basin. ate monitored by the Pe ittee uuG...a_.Lks) serial number(s) 01. specified bed. " L-ne Such di hes shall be Juent Character­--s Uis �L" tatio 'tear" Rewnj 4_s Dail Avg. I?aily ri her its ai1� Avg. CSc i } hail Me t' l 1 Summer (April 1 - October 31) M Fr c e Location Winter (November 1 - March. 31) .9 MGD 5 al Suspended Solids 538.0 681.0 1462,0 2.6 MGD Continuous Daily Recording I or E as 2189.0 Composite E Salved Oxygen �0.0 mg/1 20.0 mg/l Bail Weekly Composite Composite E l Colafarm 11 Residual Chlorine 5.0 1000.0/1001m1 2000.0/1005.0 mg/Im1 Daily Weill Grab Composite E „ E 11 Phosphorus y Monthly Composite E E it Nitrogen ( + NO2 + NO3) Monthly Composite E 73„0 104.0 Monthly Composite E Lnic :Pesticides 0.014 0.079 Weekly Composite E ;anise 90.3 90.3' Weekly Composite E 273.0 273.0 Weekly Composite E ,erasure Weekly Composite E ate 898.0 898.0 Daily Grab E ury 0.11 0.11 Weekly Composite E ols 18 1.8 Weekly Composite E nic "Toxicity Weekly Grab E city PollutantsMonths y Composite E Annually E * Sample Locations: I _; Influent, E -Effluent See Part III, Condition No. G. Chrnn4 - r^- 4 7 — —� t-,Iltt,;c--Lve gate Permittee shall monitored the river as specified below: of the Permit and lasting until expiration the Effluent Characteristics 4on Sample Locations SMeas ement ."ur §9TP—Ie Upstream East Bank Approx. I mile At FjacRe-ucy I)pt� 1-85 d2n§tEtLIE_ or Immediately above Near 1-85 Belmont Intake BOD5 NH3 as N Weekly Composite + + Dissolved Oxygen Weekly Weekly Composite + + + + pH lonductivity Weekly Grab Grab + + + + + + remperature Weekly Weekly Grab Grab 4 + + + + Phenols Weekly Grab + + + + + + 13 + Denotes monitoring required at specified locations. During the I>eriod beginning on the effective date Permittee shall monitored the river as Specified below: of the Permit and I _.. until expiration the Effluent Characteristics Maxtiar Sample Locations Measurement Fr §ap!ple upstream East B' k Approx. 1 mile At or Immediately above e 5-85 downstream Near 1-85 Belmont Intake BOD5 3 as ITT Monthly Composite + + + Dissolved Oxygen Monthly; Composite + + + + + PH /mon'th Grab + Conductivity 2/month 2/month Grab + + + + Temperature /month Grab + Grab + + + Phenols Weekly Grab + + + + + + + + Denotes monitoring i; 1«J. required at specified locations. r No. NCO004375 Permittee is authorized �UtZ to discharge. gate of the from outfall(s) serial Permit and lasting until expiration the limited and monitored by the Permittee as specified below: number(s) 001. Such discharges shall be Effluent a--- istics l Disch ar e ' itatio nitor. is her its ( Daily Avg. Daily Max.]wily ci Avg, T3sil M' M t Pr c S l e Location Acnaphtene 22 59 Acrylonitrile 96 Monthly~ Grab E Benzene 3 136 Monthly- Grab Carbon Tetrachloride 18 38 Monthly Grab E Chloroben,zene 1, 2, 4 15 28 Monthly Grab Trichlorobenzene 68 140 Monthly Grab B Hexachlorobenzene 15 28 Monthly Grab E 1, : Dichloroethane 68 211 Monthly Grab E 1 1, 1 Trichloroethane 21 54 Monthly Grab E Hexachloroethane 21 54 Monthly Grab E 1, 2 Dichloroethane 22 59 Monthly Grab E 1, 1, 1 Trichloroethane 21 54 Monthly Grab E Chloroethane 104 268 Monthly Grab E Chloroform 21 46 Monthly Grab E 2 Chlorcphenol 31 98 Monthly Grab E 1, 2 Dichlorobenene 77 163 Monthly Grab E 1, 3 Dichlorobenzene 31 44 Monthly Grab 1, 4 Dich.lorobenne 15 28 Monthly Grab E 1, 1 Dichloroethylene 16 25 Monthly Grab E 1,, 2 TransDichloroethylene 21 54 Monthly Grab E , 4 Dichlorophenol 39 112 Monthly Grab E 1, 2 Dichloropropane 153 230 Monthly Grab E 1, 3 Dichloropropylene 29 44 Monthly Grab E , 4 Dimethylphenol 18 6 Monthly Grab E 2, 4 Dinitrotcluene 113 285 Monthly Grab E 2, 6 Dintrotcilune 255 641 Monthly Grab E Ethyrlbenene 3 168 Monthly Grab E Fluorttaene 25 fi8 Monthly Grab E Bis (2'Ghloroisopropyl) ether 0 757 Monthly Grab E Methylene Chloride 40 Monthly Grab E Methyl Chloride 190 Monthly Grab E Hexachlorobutadiene 20 4 Monthly Grab E NaphthaleneMonthly 22 9 Grab E Nitrobenzene 27 68 Monthly Grab E onthl r*, l� A . EFFLUENT LIMITATIONS AND MONITORING REQU,pXMNTSFinal Duringthe period be -ginning can the P ittee is authorized effective date of the NPD S No. Permit and last ing NCO004375 limited ci monitored by to discharge the Pe it fromoutf ll(s) serial number(s)O�11. until expiration the discharges hell be €te as specified ;bet Effluent ._ a teristi s ...._._ Lisc ge L' itiltia ns l Avg. llaily N her Units S cif j Dail y M t SIiaiiy .l le Lr Location �'-Nitrophenol 41 69 4-Nitrophenol 72 124 Monthly Grab E 2, 4-Dinitrophenol 71 123 Monthly Grab E 4, 6-Dinstro-o-cresol 78 277 Monthly Grab E Bis (2-ethyl e yl) Phthalate 103 279 Monthly Grab B Di-`-baatyl phthalate; 7 57;' Monthly Grab � Diethyl phthalate 81 203 Monthly Grata Dimethyi phthalate 19 47 Monthly Giab Benzo(a)anthracene 22 59 Monthly Grab E Bent (a)pyrene 23 61 Monthly Grab 3, 4 Bellzofluoranthene 23 61 Monthly Grab Bea; o(k)fluora.nthene 22 59 Monthly Grab B Chrysene 2 59 Monthly Grab c.enaphythylene 22 59 Monthly Grab E Authracene 22 59 Monthly Grab Flourene 22 59 Monthly Grab E Phenanthrene 22 59 Monthly Grab B Py rene 25 7 Monthly Grab Tetrachloroethylene 22 S Monthly Grab Toluene ZEa 00 Monthly Grab Tri hloroethylene 21 4 Monthly Grab Vinyl Chloride 104 268 Monthly Grab Total Cyanide 1200 420 monthly Grata Monthly drab E 143 at the beginning of each dischar M. If no turbines are in o'oeratic ge day, BOD5 and -N can be at 7c00 a.m., BODE and -N turbine at Mt. Island D begins operating, BOD5 �and 4 -t iAc eoreleased in a cordpec twith ion bEquation 'Nan It It until on .m. If at lease one turbine begins operation after 7:00 pm., BOD5 and. -N can be released in accordance with Equation 1. At 7:00 p.m, the total daily stream flag during the 7:00 p.m. period will be determined as follows: 24-hour average discharge rate will be calculated which will include the minimum instaneous flow quantity plus 15 CPS 7Q10 from Dutchman Creek. (i.e., if 30 x EE6/3600 ft3 was released by one turbine from 7:00 a.m. to 7.00 average would: be f30 EE6/300 24 + 80 +'1 -= 44'� p.m., the 4-hour. CPS;, BOD5 d 3-N c be discharged from 7:00 p.m. to 7:00 2a.m uina accogrd f ce ith Equation No. low rate is greater t1. If han or equal to 329 hour average flow rate is less than329 CPS, BOD5 and 3-N can be discharged from 7:00 p.m. to 7:00 a.m. in accordance �with Equation NO. 2. If at lease one turbine begins operation after 7:00 p.m , BOD5 d 3be released in accordance with Equation 1. -N EQUATION NO. 1 S er Ci) RODS + 0.45 3-Winter (2) ( ' ) c ... 111. 1 lbs/hr. avg. BOD5 + 0.5 ( 3=N)c 197.9 lbs 2 r. avg. (33.3 lbs/hr max.) (593.7 lbsf1hr. ) EQUATION NO. 2 BOD5 + 0.54( 3-N).� (a) lbs/hr. BOD5 + 0.31 ( 3-Iv7) < (B) is/hr. BOD5 = BOD5 discharge rate, lbs/ r. 3-N = -N discharge rate, lbs/hr. Discharge Day begins at 7:00 A.M. A and B are defined below (The hourly rates will be calculated dividing daily discharge by 24) A lb hr B lb hr) Flaw: CPS AyA. Max. Ay . M 95 to 175 23.6 47.2 54.2 108. 175 to 250 43.5 87.0 99.8 199.6 250 50 329 84.5 16.0 150.3 300.6 TOxicity Geot ener This permit Anil be modified, or revoked i imi.t nt ions nod monitoring to a z.rem ant, i, Q expected in the rereivi A ty Testing Requirement discharge shall-- at no tim ztlined in; isle stream :a.cadicatce thAt e ream as as rosrrlt of this d;` fr& chronic toxicity usin; as unroxaac tiloassay Procedure _ Revised *Febr"nr 19;r or conc.entrnt i.on at which there :may be ;no obsorvab 6e ,inhibit!' to Carolina procedure document i ttoring using this procedure it;ion, i°he first: test will bs this permit. Effluent sampl: t the NPDES ormitted final e rocesses . y testing results required as ish compl.+ ,n A after ti As testing art of t;i; s permit condit thin tori:1g tC'+-m tUR- t i For the month in which rfurtr'ed, using the P€ rameter coda Ttxt`IN. 1°i"iCtfLt0VW t y, DRN ([ 3 tgin-sl") is to be snnto the f,j it7Aa j, nddres¢ At°:tent fon: Technical Services Branch North Carolina Division of Environmental Managenmont P.O. Pox 27687 Raleigh, N.C. 27611 shall be complete and accurate and include all supporting 1hysical measurements performed in association with the toxicity tests, a all<dose/response data. Total resid n chlorine of the eEfivant` xamPle must be measured and reported if ohlor ne is employed f r Corn of the waste stream. r test data from time monitoring requirement or resin performed by the alma Division of Environmental Management indicate potential impacts to ,ing stream, this permit may be reopened and modified to include monitoring requirements or limits. lure to achieve test, conditions as specified in the cited doc umenk such control organism survival rand appropriate environmental ironment;;al nont:`tols,` shall On invanl i_ a test and will require iimtudia , rp osting (within 30 days of na tor_ing ev'ant) . �' ij ur4,+.' to submit t o t nu l to st P't>si. l is will as failure of Permit condition. Permit No. NCO004375 H. Priority Pollutants The permittee shall conduct a test for priority pollutants annually after combination of all waste streams in the main discharge pipe. The discharge shall be evaluated for all volatile fractions, acid fractions, base/neutral fractions, and Pesticide fractions listed in Table 11 of Appendix D. of 40 CPR Part 122 and all metals, cyanide, and phenols listed in Table ITT of Appendix D. of 40 CFR Part 122. The permfttee shall test the effluent for any Pollutants listed in Tables IV and V of Appendix D. of 40 CPR Part 122, if a specific pollutant Is believed to be present in the discharge. In addition to the above testing requirements, other significant levels of synthetic organic chemicals must be identified. For the purpose of Implementing this requirement, the largest 10 percent of the GC/MS peaks other than the priority pollutants shall be identified. All tests shall be performed in accordance with the EPA Reference Methods listed fn 40 CPR part 136. No process wastewater from log debarking processes shall be discharged from this facility. No processes shall be discharged from this facility, No process wastewater from the washdown of veneer dryers shall be discharged from this facility. No wastewater containing plywood iglues, wnshwater containing glue wastes, washwater from machine clean-up operations, or other process wastewater from Plywood manufacturing processes shall be discharged from this facility. The phosphorus limitation contained in this permit may require the construction of additional facilities for phosphorus removal at the wastewater treatment plant. The Division of Environmental Management will renvnl"ate the rating of the wastewater treatment plant at the time an Authorization to Construct is requested. Tf the facility is determined to be a Class ITT or TV plant, the monitoring will be adjusted accordingly, rnsulting in daily monitoring for most parameters listed in the permit, Tp application documents. d. Pretreatment Program (POTWs only): N/A Production Rates (industrial discharges only) in Pow a. Highest month in the last 12 months. SIC 285 11, 579, SIC 2879 -- 225,000 b. Highest year in last 5 years: SIC 2865 �- 110,91 SIC 2879 - 1,9 7,000 Description oIndustrial Process (for industries on Applicable CFR Part and Subpart: a. CFR Part 414.83' b. CFP. Part, 455.2 Three =ring facilities. WS sed rating. ode (s): 2865 494' awater Code(s): 3' bring reque toxicity. - - - - - - A , - ,-% v i c +- i n rY I - 02 16 21 66 TION *,t is recomme Additional effluent limits requests: Toxicity limits should be based on minimum instantaneous release (95 cfs Other: None T N. C. DEPT. OF NATURAL RESOURCES 1l COMMUNITY DEV. Foa Aoas�cw ar t ENVIRONMENTAL MANAGEMENT COMMISSION NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM APPLICATION FOR PERMIT TO D ISCHARGE WASTEWATER STANDARD FORM C — MANUFACTURING AND COMMERQW, SECTION I. APPLICANT AND FACILITY DESCRIPTION Unless otherwise specified can this form all items are to be completed. If art Item Is not applicable indicate 'NA.' ADDITIONAL INSTRUCTIONS FOR SELECTED ITEMS APPEAR IN SEPARATE INSTRUCTION BOOIKLET AS INEI "its. . REJW^ TO BOOKLET BEFORE FILLING OUT THESE ITEMS. Please Prim or Type t. Legal Name of Applicant:: Sandoz Chemicals Corporation (see instructions) .,, Mailing Address of Applicant (see Instructions) P.O Box 669246 SEP 10 1,987 Number &'Street < Charlotte City North Carolina I State tlg. 2866 Zip Coded 3. AppifCant's Authorized Agent (see Instruction$) Mr, Gilliam M. Archer, III Name and Title t Environmental Manager P. O. Boas 669246 Number & Street Address i{?r�i`.:' City Charlotte State North Carolina 1d"�d 28266 Zip Code $d1rr 704 827-9651 Telephone :# Area Number 4. Previous Application .; Code It a previous application for National or Federal discharge per- mit has been made, give the date 78 12 1. of application. Use numeric designation for date. k YR MO OAY° I certify that I am familiar with the information Contained In this application and that to the best of my knowledge and belief such Information Is true, complete, and accurate. Ray H. An ers Vice President, C.nerations Printed Name of Person .Signing Title 7 09 09 YR MO DAY r Se temer 9 1987 gnatu f Applicant or Authorized Agent slate Application Stoned North Carolina General statute 143--21 .6 Cb (2) provides that- AnT person who knowinglymakes a=y false statement representation, or certi±ication in any application, record, report, plan, or other document files or required to be maintained under Article , or regulations of the Environmental a ement Commission implementing that Article, or who falsifies, tatmers with, or lcnowl y renders inaccurate any recording or monitoring device or method required . to be operated or maintained under Article 21 or regulations of he E Vi.r0 en.tal Management Commission lem en that Article, shall, be guilty of a misde anon " .. ishable by a fine not to exceed, 10,000 or by I=prisonment not to teed fix months, or by both.. (IS U.S.C. Section 1001 pro 4e�, a punishment ent' by A' fine of not more than 16,000 or imprisonment not pore than s years, or -bot , for a similar offense. fay AC NCY USE athrity, ( Instructions) ame, ownership, and "tion of the plant or ^ating facility whoro d's- 3046 or all ur, Sandoz Chemicals Corporation Mount holly Plant hip (Public, Private or tblic and Private) opus M PAV Capp suck If Federal Facility: FEO s GSA inventory Control 1' r � rn Highway 27 West & Number uz Charlotte Mecklenburg ty North Carolina Manufacture and Processing of eyes and Organic Chemicals f Business State the f the business conducted ant or operating facility. ' AGENCY USE Ev Intake Water ( lnstrut- ,rdicate water intake volume by sources. Estimate volume par day in thousand wr day. 2220 .ipal or private water system th ss ii s y thousarld gallons Pat day :0 water CC (Con amiaed water for treat- sdater ` thousand gallons r y men On y 200 i 1t < thousand mil : r y f109 2720 thousand gallons par day item is intake water from Stormwater runnff specify the source. t8 Water Use Estimate volume per day in thousand per day for the fallowing I water usage at the facility. tructions) j()} :ontact cooling water 1 a ' th gallons per day 100 r feed water thousand gallons por day rsswater (Including tar t i6t3 {include csundwater and no water) t thousandgall" s day StC3rmwa 6} ary water thound gallons par day r* 00 thouaggod gallons pot day i Item a } 2720 t erd 9MIons per day to Water treatment filter backwash v ere�eischar specify. e is nitary' aster use, 91VO 00 mber of people served . A11 Facility 04rh4rgts and *that FOR AGENCY USE i t$ssts: Numaatr •"d OfschiOnt (sea instructions) Vdtumt Specify the number of discharge Points and the volume of water discharged Of last from the facility according to the categories betbw. Estimate Number of Total Volume Used. average volume per day in thousand Discharge or Discharged, gallons per day. points Thousand :Gal/Day Surface water 101fa1 109ta2 Sanitary wastewater tran$Port 102#1 1 �2 system Storm water transport system # C1 1 Combined sanitary and storm 389d water transport system IMdI Surface impoundment with no 10lt2 ..):effluent: 100*1 Underground percolation 109f1 tb9f2 Weft injection 10Sg1 to Waste acceptance firm #02tf1 loft" r 200 Evaporation 109t1 10012 Consumption 34911 10912 G C)ther* 10k1 1 Facility discharges and volume 2720 Total item 9. 1110911 10112 • if there are discharges to'other,' specify. 1 agent r 10. Permits,. Licenses and Applications List all existing, pending or denied permits, licenses and applications related to discharges from this facility (tee instruction$). gate Lute Gate Expiration Type of permit Issuing Agency For Agency Use lit Number or License Filed issued Denied hate YR/MO/DA YR/M0/0A YR/MCi/OA YR/MO/DA 310 (a {tS (a (di #11 t tail 1. COW 3i 11, Maps and Drawings Attach all required maps and drawings to the back of this application,(see Instructions) 12. Additional information" 112 Item Number information 9 Values representpotential annual flow quantities for 1988. We request continuation of 3.9 MGD discharge rate during summer months (April I - October 31) to allow discharge of stored effluent, and 2.6 MGD discharge rate during winter months (Nov. I - March 31). I3 SECTION U. BASIC DISI it, each discharge indicated in Section I, item 9, FOR AGENCY USE ZING AND COMMERCIAL DESCRIPTION DITIONAL INSTRUCTIONS FOR SELECTED ITEMS'APPEAR IN SEPARATE INSTRUCTION BOOKLET AS INDICATEC BOOKLET BEFORE f- It LING OUT THESE ITEMS. Discharge Serial No. and Name 001 a. Discharge Serial No. (see instructions) Treated Wastevater b. Discharge Name 201 b Give name of discharge, it any. (see instructions) c. Previous Discharge Serial No. If previous permit application 001 was made for this discharge (see 2014 Item 4, Section 1), provide previ- ous discharge serial number. Discharge Operating Cates a, Discharge Began Date if the discharge described below is in 76 06 operation, give the date (within 2021 best estimate) the discharge YR MO began, M Discharge to Segin Date If the OiSCharjp has never occurred but is planned for some future date, 102b give the date (within best esti- YR MO mate) the discharge will begin. c. Discharge to End Date If dts- charge is scheduled to be dtscon- N/A timed within the next 5 years, 202C give the date (within best esti- YR MO mate) the discharge will end. Engineering Report Available Check,if an engineering report is available to reviewing agency upon 203 request. (see instructions) Discharge Location Name the political boundaries within which the point of discharge is IoCatel:L NOrth Caxolina State 204a A-_Ckl 'q County 204b —4-4-� uld be repre- s" REFER (d acituicable) City or Towne 104t 204# 5. Discharge Point Description Discharge is into (Check one), (see instructions) Stream (includes ditches, arroyos, and other intermittent watercourses) 2060 f0STR Lake [3LKE Ocean C30CE Municipal Sanitary Wastewater Transport System OMTS Municipal Combined Sanitary and Storm Transoort System CIMCS This section contaii,I6 9 eta gfS. DISCHARGE SERIAL NUMBER 001 Municipal Storm Waiter Transport FOR ACENCY USE System [3 ST S Well (injection) C1 WEL Other C30TH If 'othvr' is checked, specify 1011111; fi, Discharge Point — Lat/Long Give the precise location of the point of Discharge to the nearest second. 16 Latitude 20192 --25- DEG MIN _5SEC M N Longitude 204b ___9_1DEG t ___LSEC 7, Discharge Receiving Water Name Name the waterway at the point 1 207# Catawba RiVer of discharge,(see instructions) For Agency Use For Agency Use If the discharge is through an out, fall that extends beyond the shore- 2070, Major Minor Sub 207C 303e fine or is below the mean low water fine, complete Item 8. III. Offshore Discharge a. Discharge Distance from Shore 201111A feet b. Discharge Depth Below Water N/A Surface 20*b feet 9, Discharge Type and Occurrence a. Type of Discharge Check whether the discharge is con- 20114 (con) Continuous tinuous or intelsirritterit. (see instructions) (int) Intermittent b, Discharge Occurrence Days per 7 week Enter the average num- 101110, —days per week ber of days per week (during Pertods of discharge) this dis- Charge occurs. cDischarge Occurrence —Months If this discharge normally 20*4 RIJ A N X]FEB EMAR ZJAPR operates feather intermittently, I I or continuously) on less than MAY JSJUN JgJUL IS AUG a year -around basis (excluding shutdowns for routine mainte- ESEP WOCT X]NOV MOEC mince), check the months dur- ing the year when the discharge is operating. (see, instructions) :Omplete Items 10 and I I if "inter. littent­ is checked in Item 9,a, )therwise, proceed to Item 12. 0. Intermittent Discharge Quantity State the average voiurne per dis- 11je —ELL—thousand gallons per discharge occurrence. charge occurrence in thousands of gallons. It. Intermittent Discharge Duration and Frequency a, Intermittent Discharge Duration Per Day State the average 2110 A/24tours per day number of noun Der day the discharge is operating. b, Intermittent Discharge Frequency State the average 21111s -N-LAischarge occurrences per day number Of discharge occur, fences per day during days when asscriarging, 12, Maximum Flow Period Give the N/A time period in which the maximum 212 From to flow of thtS OwSCMarge occurs, month month a DISCHARGE SERIAL. NUMBER 001, FOR AGENCY USE 13. Activity 00SC60601% Give Manufacturing and processing of dyes and organic narrative description of activity producing thisdischarge4see 2t x chemicals, and manufacture of an agricultural herbicide. Instructions) 14. Activity Causing Discharge For each SIC Code which describes the activity causing this discharge," supply the type and maximum amount of either the raw material consumed (Item 14a) or the product produced (Item 4b) in the units speccified in Table I of the Instruc- tion Booklet. For SIC Codes not listed in Table 1, use raw material or production units normally used for measuring production„(See instructions) a. Raw Materials Maximum Unit" Shared Discharges SIC Code Name Amount/Day (See Table;i) (Serial Number) 14s b. Products Maximum Unit Shared Discharges SIC Code Name Amount/Day (See Table 1) (Serial Number) 140 286 Org. 400 1000 lbs 001 les.anl emca s 2879 Ag. Herbicide 8 1000 lbs 001 DISCHARGE SERIAL NUMBER 001 FqR AGENCY USA 15, Waste Abatement Acidic and non -acidic wastewaters and stormwater are a, Waste Abatement Practices I the waste abatement The acidic wastewater is neutralized 1trjk ttr,, ,,Va f,j, this distbar,10 collected separately. wtpi,j I met nArrAtivu. (See and combined with non -acidic wastewater for settling and equalization. The combined wastewater is treated in an extended aeration activated sludge system with sludge recycle from secondary clarifiers. Discharge quantity is controlled automatically depending on the minimum river flow by pumping excess effluent to a 300 million gallon storage facility. Stored effluent must return through the activated sludge system prior to discharge. ESEPAR (2) ESEGRE (3) ECOUNT Waste Abatement Codes Usillg the codes listed in Table 215b (1) (4)R.ECOVE, (5) OMO(r,) NIT it ei the tnstrottion Booklet, describe the waste abatellicnt (7)P1aUAL_ -2-SEDIZ—, --- 2ACZLV-- pr(,Cesscs J()t this citschArot'M the order ill which ttIVY (WLIlt (10) BPOLIS _jLAGOO MPOSTA (13) (14) (16) (17) (19) (20) (21) (22) (23) (24) (25) 11-4 * * DISCHARGE SERIAL NUMBER 001 c►sa Arkcv css' i � �. ' wastawater char��teri�ti This determinatlan Is to be basedon actual analYSls Check the boy beside each eorestituent which is present in the effluent (discharge water]. or best estithate.(seeinstructions) Parameter Parameter a, Color Copper X 01042 00080 Ammonia Iron X X 01045 00610 Organic nitrogen Lead 01051 00605 Nitrate ' Magnesium X X 00927 00620 Nitrite Manganese 01055 00615 Phosphorus Mercury X 71900 00665 Sulfate Molybdenum X 01062 00945 X Sulfide Nickel 01067 00745 Sulfite Selenium OI147 00740 Bromide Silver 01077 71870 Chloride Potassium 7 00940 Cyanide Sodium X 00929 00720 Fluoride Thallium X 0109 00951 Aluminum Titanium X 0II2 01105 Antimony Tin 01102 01097 Arsenic Zinc 01092 01002 Beryllium Algicides* 74051 01012 Barium Chlorinated organic compounds* X 01007 74052 Boron Pesticides* 0102 7403 Cadmium Oil and grew 00550 01027 X Calcium Phenols, X X 32730 00916 Cobalt Surfactants X 38260 01037 Chromium Chlorine 50060 01034 Fecal coliform bacteria' Radioactivity* X 74050 74055 *Specify substances, compounds and/or elements to Item 26. Pesticides (insecticides, fungicides, and rodenti ides) must be reported in terms of the acceptable common names specified in Acceptable Common Names and Chemical Names or the Ingredient Staterrient On Washington, D.C. 20250, June 1972, as Pesticide Labels, 2nd Edition, Environmental Protection Agency, required by Subsection 162.7(b) of the Regulations for the Enforcement of the Federal Intieide, Fungicide, and Rodenticide Act. 11- foa Aca►cw�c7se Equalized Feed I .+� i i# i i• i i f m Chromium, Copper, N system influent. Controls Check It the fol. tg Piant controls are available its discharge. mate Power source for major Ping faciltty^ n of emergency Procedure for r or equipment failure slete ltern 29 if discharge is cooling and/or steam water ationsand water treatment ives, are used. Treatment Addit➢ves. if the irge is treated with any con- ef, inhibitor, Or algicide, r theCfollowing; me Of Material(s) I me and address of manu- turer and Zinc may be present in trace quantities in ® RPS ALM POI.Ymer as a clarification aid various antity (Pourios added per !#lam Icon gallons of water treated), II- icke" its I 2t9a 211b DISCHARGE SERIAL NUMBER 001 i�o ac�Ncr tls Primarily Cationic Polymerete d. Chemical composition at m�1 additives (see instructions). Complete items 20-25 If there Is a thermal discharge (e.g., associated with a steam and/or power generation plant, steel mill, petroleum refinery, or any other manufacturing process) and the total discharge flow is 10 million gallons per day or more. (see instructions) 20. Thermal Discharge Source Check /A the appropriate items) indicating the source of the discharge, (see instructions) Boiler Slowdown 0 BLSD- Bolter Chemical Cleaning 0SCCL Ash Pond Overflow QAPOF Boiler Water Treatment '— Evapora- [ EPBD for slowdown Oil or Coai Fired Plants — Effluent C} OCFP from Air Pollution Control Devices Condense Coaling water 0 COND Cooling Tower Slowdown [D CTBD Manufacturing Process a MFPR Other 0 DTHR 21. Discharge/Receiving Water Temper- N/A ature Difference Give the maximum temperature difference between the discharge and receiving waters for summer " and winter operating conditions. Summer (see Instructions) s to OF. Winter t21'b OF. 22. Discharge Temperature, Rate of '. OF./hour Change Per Hour %22 Give the maximum possible rate of temperature change per hour of: discharge under operating can• ditlons, r (see instructions) 23, Water Temperature, Percentile %] Report (Frequency of Occurrence) In the table below, enter the temperature which Is exceeded 10% Of the year, 5% of the year, 1% of the year and not at all (maximum yearly temperature). (see instructions) Frequency of occurrence a. Intake water Temperature 2 (Subject to natural changes) b. Discharge Water Temperature 2=23t' 24. :Water Intake Velocity 4 �` � feet/sec. (see instructions) 25. Retention Time Give the length of 4211 /A minutes time, in minutes,'from start of water temperature rise to discharge of cooling water: (see instructions) oiSCHARGE SERIAL NUMBER -- Fii ACsEN�CY 41SE 001 26. Additivnai 1nf0rm*tJ00 8 item intcarr»ation 3 Modification of the wastewater treatment facility is re aired under RCRA. A 'Basis of Design Report for these modifications de elo e b�* Engineering -Science of Atlanta is available from William M. Archer, Environmental Manager, Sandoz Chemicals Corp., Mount holly Plant, P.O. Box 669246, Charlotte, N.C. '28266. Drawings and specifications will be submitted in the near future for a permit to construct from DEM. 15 S. _based on the minimgm daily averse river flew of '329 cfs as is the cu rgnt Rermit. lfi No chlorinated or— c riorit ollutants�caew e. de e -th analysis (see attached results). Test results preceded bless than 00 symbol represent parameter detection limit. Low p b levels of o-dichloroben ene have been detected in past sampling. C_ STANDARD FORM C — MANUFACTURING AND COMMERCIAL SECTION M. WASTE ABATEMENT REQUIREMENTS & IMPLEMENTATION (CONSTRUCTION) SCHEDULE This section requires information on any uncompleted Implementation schedule which may have boon Imposed for constructionof waste abatas ment facilities. Such requirements and implementation schedules may have n established by local. State, or Federal agencies ;or by court action. In addition to completing the following items, a copy of an official implementation schedule should be attached to this application. IF YOU ARE SUBJECT TO SEVERAL DIFFERENT IMPLEMENTATION SCHEDULES. EITHER BECAUSE OF DIFFERENT LEVELS OF AUTHORITY IMPOSING DIFFERENT SCHEDULES (item Ia.) AND/Oil: STAGED CONSTRUCTION OF SEPARATE OPERATION UNITS (item lc), SUBMIT A SEPARATE SECTION tit FOR EACH ONE. _ FOR AGENCY USE t. Improvements 30is ' a. Discharge Serial Number B k7 Affected List the discharge 7fr?ta serial numbers. assigned In Section It. that are covered by this implementation schedule, b. Authority imposing Require- ments; Check the appropriate Item Indicating the authority for implementation sctiedule. It the Identical Implementation schedule has been ordered by more than one authority, check the appropriate Items. iaiss Instructions) Locally developed plan 1b (BLOC Areawide Plan CARE Basic Plan OBAS State approved Iptemanta- tion`schedule s]QS Federal approved water quality standards impteenta Lion' plan. (QS Federal enforcement proced- ure or action: IENF Stag court order QCRT Federal court order C PEO c. Facility Requirement. Specify the 3-character: cede of those .S-character listed below that best describes : (general) In general terms the require- ment of the Implementation schedule and the applicable six - character aoatement CT>de(s) .. from Table II of the Instruction, booklet. If more than One 6-character schedule applies to the facility : '. (specific). because of a staged construction ` (see Table il) schedule, state the stage of con- struction being described here with the appropriate general action code. Submit a separate .Section III for each stage of construction planned. Now Facility NEW Modification (no Increase In capacity or treatmentp moo Increase In Capacity INC Increase In Treatment Level TNT Both Increase In Treatment Level and Capacity ICT Process Change PRO Eiirnination of Discharge ELi This s t,. :crigin, y C+akes.; amantat on xci+edu►e and 3, Actua► Conti fat►on Ost POR ACENCY 415E f stion for implementation stops ►►sted below. implementation Steps 2. Schedule (Yr4MO. /Day) 3. Actua► Completion (Yr. o./ ay) a. Preliminary plan complete . Fna► plan submission l —/ C. Final p►an comp►etc d. Financing complete & contract awarded o« Site acquired —�—/ f. 6egin action (e.g., construction) / g. End action (e.g., construction) h. Discharge Sagan i. operational ►eve► attained ..„.: .....s,.�...: e 111-2 GPO Os<,742 GENERAL ENGINEERING LABORATORIES 1313 Ashley River Road P.O. Box 30712 Charleston, S.C. 29407 leston, S.C. 29417 Engineering Consulting ne (03) 5 6- 17I- hemical Analysis !� Laboratory Certification Number 10120 � i CLIENT: SANDOZ CHEMICALS CORPORATION PO BOX 669246 GATE: 08/25/87 CHARLOTTE , NC 2826 CONTACT. MR. E. J. ECCLES RELEASED BY: ,�c.GEORGE C. GREENE PE PHO CC/FC. SNDE/PP1 PAGE NO.: -------------------------------------------------------------------------------- SAI^IPI F ID FINAL EFFLUENT 07/30/87 LAB ID 87071336 PARAMETER DATE ;RECEIVED: 07/31/87 ----------------------------------------------------------------------------- CYANIDE <0.1 ppm ANTIMONY <0.01 ppm ARSENIC <0.005 ppm BERYLLIUM <0.01 ppm CADMIUM 0.010 pp CHROMIUM <0.05 ppm COPPER <0.05 ppm LEAD <0.005 ppm MERCURY 0.0017 pp NICKEL <0.05 pp SELENIUM <0.005 ppm SILVER <0.05 ppm THALLIUM <0.005 ppm ZINC <0.05 pp DIGESTION FOR MERCURY ANALYSIS YES ACID DIGESTION YES ACROLFIN <10 ppb ACRYL NITR LE <10 ppb BENZENE <5 ppb ROhMOEORPM <10 ppb CARBON TETRACHLORIDE <10 ppb CHLOROBENZENE <10 ppb' CHLORODIBROMOfMETHANE <10 ppb CHLOROETHANE <10 ppb 2-CHLOROETHYL VINYL ETHER <10 pp CHLOROFORM (10 pp DI HLOROBENZENE (1,2 A., 1,4) <10 ppb ICHLCROBEIZENE (115) <10 ppb DICHLOROBROMOMETHANE <10 pp }ICHLORODIFLUOR JPMETH NE <10 ppb CI CHLOROETHANE (1 ,1) <10 ppb iICHL1ROETHANE (1,2) <10 ppb )ICHLOROETHYLENC (111) <10 ppb ICHL ROETHYLEN (1, -T) <10 pp ICHLOROPR PANE 0,2) <1`0 ppb DICHLOROPROPYLEINE (1,2) <10 pp pr GENERAL ENGINEERING LABORATORIES 1 13>Ashley River Read P.O. Box 30712 Charleston, S.C. 29407 Charleston, S.C. 29417 Engineering Consulting Phone (803) 55 i-81'71 Chemical Analysis Laboratory Certification Number 10120 CLIENT: SANL)02 CHEMICALS CORPORATION PO BOX 669246 DATE: 08/2 87 CHARLOTTE , C 20266 CONTACT: MR. E. J. ECCLES CCiFC : SNDE 'PP 1 PACE NO.: -------------------------------------------------------------------------------- SAMPLE ILA : FINAL EFFLUENT 07/30/87 LAB ICJ : 8707133 PARAMETER TER DATE RECEIVED: ----------------------------------------------------------------------------- 07/31/87 ICHLOROPR PYLENE (113) <10 ppb ETHYLBENZENE E <10 ppb METHYL BROMIDE <10 ppb METHYL CHLORIDE <10 ppb METHYLENE CHLORIDE <10 pp TETRACHLOROETHANE (1,112,2) <10 ppb TETRACHLOROETHYLENE <10 ppb TOLUENE <10 ppb TRICHLOROET'HANE <1,1,1) <10 ppb `fRICHLOROETHANE (1,12) <10 ppb `L'RICHLOROETHYLENE <10 ppb , TRICHLOROFLUOROMETHANE <10 ppb VINYL 'CHLORIDE <10 ppb CHLORLPHENOL <2) <10 ppb DICHLCROPHENOL <2, ) <10 ppb DINITRO- O-RE O <4, ) <10 ppb DINITROPHENL_<2-METHYL-4,6) <30 ppb DIMETHYLPHENOL <;2, ) <10 ppb 6INITROPHENOL <2,4) <45 pp NITROPHENOL (2) <10 ppb NITROPHENOL (4} <10 ppb P-CHLORO-M -CRESOL <10 ppb PENTACHLOROPHENOL <10 ppb PHENOL <10 ppb TRICHL:.OROPHEIIOL (2,4, ) <10 ppb CENAPHTHENE <10 ppb BEN?IDINE <10 ppb BIS (CHLORLIMETH'YL) ETHER <10 ppb BIS <2-CHLOROETHGXY) METHANE" <10 ppb IS <2-CHLOROETHYL) ETHER <10 ppb BIS (2-CHLOROISL`PROPYL) ETHER <10 ppb BROLOPHENYL PHENYL ETHER <10 ppb CHLOROETHYL VINYL ETHER <10 pp CHLOROPHEN°YL PHENYL ETHER <10 pp CHLORONAPHTHALENE (2) <10 ppb DICHLOROBENZIDINE (3,31) <10 ppb GENERAL ENGINEERING LABORATORIES 1313 Ashley River Road P.O. Box 30712 Charleston,_S.C. 29407 Charleston, S.C. 29417 Engineering Consulting Phone (803) 556-8171 Chemical Analysis Laboratory Certification Number 10120 CLIENT: SANDOZ :CHEMICALS CORPORATION PO BOX 669246 DATE. 8/2 /S CHARLOTTE NC 28266 CONTACT: MR. E.'J. ECCLES CC/FC SNE./PP1 PACE NO.: ------------------------------ SAMP"LE I) FINAL EFFLUENT ./ 0/87 LAB ID : B70 1336 PARAMETER DATE `RECEIVED: 7,/31/87 ----------------------------------------------------------------------------- DINITROTOLIIENE 2,4) <10 ppb DINITROTOLUENE (2,6) <10 ppb OIPHENYLHYRAZINE (1,2) <10 ppb FLUORrANTHENE <10 ppb HEXACHLORO ENZENE <10 ppb" HE: ACHLORO UTALIIENE <10 ppb HEXACHLOROCYCLOPENTADIENE <10 ppb HEXACHLOROETHANE <10 ppb ISOPHORONE <10 ppb NAPHTHALENE <10 ppb NITROBENZENE <10 ppb N-NITROSOLIMETHYLAMINE <10 ppb N-NITROSODIPHENYLAMINE <10 ppb, N-NITROSO-LEI-N--PROPYLAMINE <10 ppb TRICHLOROBENZENE (1 2,4) <10 ppb; SIS t2-ETW(LHEXYL) PHTHALATE <10 ppb' BUTYL BENZYL PHTHALATE <10 ppb' bIETW(L PHTHALATE <10 ppb DIMETRYL PHTHALATE <10 ppb DI-N-BUT`CL PHTHALATE <10 ppb l)1-N--0CTYL PHTHALATE <10 ppb ACENAPHTHYLENE<10 ppb ANTHRACENE <1,0 ppb BENZO W ANTHRACENE <10 ppb BENZO (B) FLUO ANTHENE <10 ppb BENZO (K) FLLIORANTHNE <0 ppb BENZO OHI) PEfYLENE <10 ppb BENZO (A) PYRENE <10 ppb BENZOFLUO ANTHENE (314) <10 ppb CHRYOENE <10 ppb DIBENZO <A,H) ANTHRACENE` <10 ppb FLUORENE <10 ppb INDENO (1,2,3-CD) PYRENE <10 ppb PHENANTHRENE <10 ppb PYRENE <10 ppb ALDRIN <10 ppb I Cqnsul4q rtwix (803) 556-8171 :rnza naiysis Laboratory certification Number 1O120 CL I ENT . SANDOZ CHEMICALS CORPORATION PO BOAC i6`�246 DATE: '08�25r'8 CHARLOTTE , NC 28266 CONTACT: MR. E . J . EC LES CC FC: SNDE/PP1 PAGE NO.: 4 _-__ SAMPLE ID . FINAL EFFLUENT 0 70/8? LAB ID 8701336 PARAMETER DATE RECEIVED: 0 31f87 DIELDRIN <10 ppb CHLORDANE (TECHNICAL) <10 ppb ACHLORDANE <10 ppb G-CHLORDANE <10 ppb O,P'-DDE <10 ppb O,P'-DDD <10 ppb G,P°-CDT <10 ppb P,P'-DDE <10 ppb ,P'-DDD <10 ppb P,P'-DDT <10 ppb NDOSULF I (10 ppb ENDOSULFAN'i II <10 ppb ENDOSULFAN SULFATE <10 ppb ENDRI I <10 ppb ENDRIN ALDEHYDE <10 ppb HEPTACHLOR <10 ppb HEPTACHLOR EPDXIDE <10 ppb A - HC <1,0 ppb 8--8H <10 ppb LINDANE <10 ppb D-BHC <10 ppb TOXAPHENE <10 ppb AROCLOR 1016 <150 ppb AROCLOR 121 <150 ppb AROCLOR 1232 <150 ppb AROCLOR 1242 <150 ppb AROCLOR 1248 <10 ppb AROCLOR 1254 <150 ppb AROCLOR 1260 <150 ppb AROCLOR 1262 <150 ppb E` TR CT I M4 & CONCENTRATION `1E CHAS.T.MAIN, INC. TWO FAIRVIEW PLAZA, 5950 FAIRVIEW AD_ P,O BOX 240236, CHARLOTTE, N,C, 28224, TEL 7041554 1 100 MAIN` Sample Number 3027 7 1000 Jots : MAIN ANALYTICAL LABORATORY RESULTS OF ANALYTICAL TESTING Date: 8/27/87 CLIENT:' io Chemicals wrp 1 Address: P*O* Box 66 246 Charlotte, NC 28266- 2 6 P.O. # Sample No. Gate Taken Sample Description 871189 8/1112/87 Final Effluent Gate Samples Recd.: Shipped By., _ J. n Rec'd/Logged By: Invoice bate: By Parameter Unit Concentration 87-.318 Bromid/l 14 JL for units 520 _Xjwride nall 0.56 SR_1 .3C Nitrite/l 0.02 el Ni /1 4.48 Pho/1 0,20 ' Sulfate 1 3360. LjLA i 1 2.0 Remarks: Test results preceded by less <) sl l represent paraMter detectiOn limit. page 1 of ° 2 MAIN Analytical Lab PAGE, O `r o 1 1e JOB : _- -JM DATE: _ 93 27 87 NTS. MAIN Sample Number 87-1189 By Parameter Unit PM Sulfide /1 JL V ,/l Concentration e .4 1.88 Tin-,/l 0. 9 JL Titanium 0.7 JL Altvdnum mg/l 0.6 JL Barium /l " q.4 JL Boron /l {4.8 JL Cobalt 1 < 0. 05 JL Iron 1 1.52 JL Magnesium jl 12.0 1 1 0.1 JL Manganesejl 0.48 OR LIIVA7nN WASTEWATER ANALY,SIS FINAL WASTEWATER + WASH SOUS 87,000 g/l TOC 32,600 mg/l COD 5,300 mg/l ISOPROPANOL - 5% NO U ;SON 36 mg/l Agra w t Y t s t y it t. is t x SELECTIVE HERBICIDE ,G WITH A SPECIFIC SPECTRUM DE ACTION4 Y " AGAINST GRASSES AND BROAD -LEAF WEEDS TES COTTON CROPS AND FRUIT PLANTATIONS June 1979 z s � 6 [i s y AGRO OOPE-4358 Introduction ZORIALIDs a- selective herbicide based on a joydazincne of low toxicity, which was discovered and developed in the Laboratories of SANDOZ Ltd., in Basle (Switzerland), t is available - as a wettable powder containing 0% (weight by weight) of the active ingredient n rfZura on - as granules containing % (weight by weight) of norflura. on or will be available as a wettable dispersible concentratecontaining The information contained in this document is based on our worldwide experience up to date. EFFECTIVENESS ZORIALOis a relatively long-lasting soil pre -emergence herbicide with little ;cost -emergence activity. Primarily ZORIAL' is an annual' grass killer but shows also good control of annual broadleaf weeds. At higher rates, good activity against Cyperus species has been shown, and activity against some Carex and Juncus species has also been evident. In favourable cases, some perennial grasses are controlled too. x AGRO DOK E- 3 -3 CROP TOLERANCE AND POTENTIAL FIELD APPLICATION According to our present knowledge, practical crop tolerance has been found so far with cotton and perennial crops such, as cran- berries, established alfalfa,; citrus, some deciduous fruit trees, nut gees, bananas and sugar cane. The suppression of noxious weeds, or their destruction (mainly grasses), it the present problem in many cotton and fruit tree growing countries. These are the places where ncr.�. Zu.tazon can be successfully included in the rotation of normally used herbicides, either on`its own, or in mixture with other suitable products.' DRIAL® is not a common broad-spectrum acting product to be used to solve general weed problems, but is a speciality designed to solve specific weed problems which have _ in many places - been created by interference through new crop husbandry methods. fg5 i # f AGRO OOK E-43 PropertiesChemical and Physical Nox6Zutazon, a fluorinated pyridazin ne herbicide of low toxicity o the user, is the active ingredient of our formulated commercial products known as: ZORIAL EVITALO (USA) SOLICAM& (USA) ACTIVEINGREDIENT hon �?unaon common name � ch,e.m.icaZ name.-chloro-5-(mothylamino)- - (cx,a,x-trifluoro--tolyl)- (2H pyrid'ainone stxu.ctnaZ �o,%muZa C F 3 N N H 0 Cl em'p.ix caZ AoxmuZa C sz Hs Cl F 3 N 3 0 mo .ecu aA we.i.g h 303 i 7 appearance crystalline solid ` cozoux white odour odourless meeting point- ___ 177 IC t 3 ° C AGRO GO, _E-4358 va.pou . prce64ute at 20°C 2° 0 x 10-1 Torrm 50°C 2-°5 x 10` Torr. f 1200C 5,. 2 x 10`4 Torr* zotubitity in ware.. { 28 ppm at 23 ° 4o. ubiZity ,n �sotvent4 ethyl alcohol 14- 2 g/100 ml at 250C acetone 5.0 g/100 ml at'25°C xylene 0-25 /100 ml at 250 y y quite'stable in aqueous solution } (5.5 ppm) at pH 3, 7 and ; o significant breakdown was observed within 7 days at 50oC, the loss E r amounted to less than 8% after ;'.4 days. thexmo-ztabiZity Stable, no degradation upon storage at 50C for 4 weeks and 700C for 1 C .4 AGRO OOK E-4358 FORMULATIONS (typical' data) WETTABLE POWDERS code numbetz SAN 9789, SAN 52.143 H, SAN 9789 H I .eg.istexed Tnadematkz : ZO IALO SOLICAMO_ (USA) COMP0,6ition 80 of not4tunazon (active ingredient) ( eight1weight) 20 of adjuvants and inert materials phy icat Janm fine powder coou grey -beige odour practically odourless 1 butk denzity 240-295 g/ (depending on milling process) zuzen ibitity min. 80% for concentrations of from (CIFAC method MT 15.1) 0.5 to 5% at -300C in water of hardness 20 to 500 ppm cold ztabitity excellent' heaaby stable at 50o for 21 weeks in accelerated stability study 4het6 ti6e min."4 years when kept in unopened original container at 20oC approx. GRANULAR FORMULATION } t 1 od number SAN 9789 H 5 G registered Trademark FVITAL� (USA) composition 5 of not6t nazo (active ingredient) (we ghtl weight) 95 f adjuvants and inert material physical form free flowing granules particle size mainly between 315 and 1000 mi rons bulk density 1,4 kg/l ` stability stable shelf Life min. 2 years when kept in unopened original containers at temperatures lower than 300C. FLOWABLF FORMULATION ode number X SAN 9789 N 600 WC registered Trademark ZORIAL FL j f ' composition 600 g/l of noAt tutazon. (active ingredient) 650 g/l of adjuvants and inert material physical farm liquid suspension concentrate c otour beige -white [t density (200C) approx. 1250 9/1 i i suspensibiLity min. 80` for concentrations of from (CIPA method MT 15a1) 0.5 to 10.E at 00in water of E hardness 20 to 500 ppm cold stability heat stability shelf i fe stable at temperatures dow -20C, the product s approx. 04oC, but wh 10 to 20C,exhibits L original physical prc stable at 400C for 2 accelerated stabi 1 i tJ hen ke rties aeks in to y _� 'Int r, �"V-Mv min. years w p- in unopened original containers. AU U UUt4 Analytical e Determinations of nox una c n n technical and orm alat d pr du t The active ingredient is separated from by-products and formulation additives by slim layer chromatography, extracted from the silicagel layer and quantitated by pectrophotometric assay. i ^- I Please consult: AGRO DOK CBK 187/71 and 1158/73 "Quantitative UV spectrometric determin pesticides in technical and formulated Noy . utca.zon" . . DeterminatioE_2±_12jjj.una.zon residues in soil The residues; of not6 a azon and its metabolite are extra acetonitrile-water, cleaned -up by alumina column chromat determined by gas chromatography. Please consult: Report CVH 8/70e "GLC de ermi'nation of residues of nog. in soil". Determination of nrnutczon residues in cro s Two methods are available for the determination of resid berries and in soybeans, peanuts and cotton seed. Both ff based on soxhlet extraction, clean-up by liquid -liquid followed by alumina column chromatography, and quantitt chromatography. Please consult: AGRO DOK CBK 2008/75 "Analyss'of cranberries for residues c and its desmethyl metabolite". AGRO DOK CBK 1163/73 "Analytical method for residues of nog. its desmethyl metabolite in sybans, jcotton seed" ToxicQ1091cal and environmentalaspects x nfrousstudies carried out with no,%6Zutazon and its metabolites Iftowthat this SANDOZ speciality is practically a non -toxic herbicide, W f n does not present any marked hazards, either to humans `or to wild life* ~. TOXICITY LDso in rig peg. kg oj body weight e,cies technical no�LJZukazon 2CRIAL'V rl rat 9`3 1.0 a 2tl .000 rz� 1 rabbit no skin irritation lye irritation rabbit no irritation ltion rat 200 mg per litre of air Ino adverse effect x a ACUTE TOXICITY 'ceding tests (90 days) • n rats 50 mg/kg 250 Mg/kg with technical grade material / daily; daily. no effect slight liver and kidney weight`` increase, minimal thyroid stimulation on dogs 15 mg/kg / daily: no effect Higher doses were unacceptable from a palatability viewpoint. -. Dermal test On rabbits, no local or systemic effect was observed when ZDRIAL was applied daily during a 21days 'period at the rate of 1'000 me/kg. i "c . Inhalation tests On rats, no toxic symptoms were observed with tests conducted r rrrrsrnr ��- �h� during a 14 days'period, for one hour daily, with j rate of 10 mg per litre of air. TOXICITY TO WILD LIFE 4 No marked hazards are to ;be expected for birds" and fi o investigate this, tests were conducted with ZQRIAL t 1..cute oral toxicity to birds ' Mallard duck LD125 mg/kg; Bobwhite quail LD50.>1250 mg/kg 2. Fish toxicity Catfish L C s 0 200 pp Goldfish fingerlings LC0 20 pp'm Rainbow trout LCso 6 ppm A. IN SOIL The dissipation of noA4twtazon from soils depends largely on the type of soil, soil moisture, temperature, solar radiation, air movement, and Mode of application. By checking dissipation rates at different locations within the USA and Switzerland, and under good agricultural practice conditions, the influence of relatively different conditions was tested. Results indicate enhanced dissipation occuring;in lighter soils at higher moisture levels, with surface application. Soil carry-over may be expected to be longer in cooler or drier areas. Leaching, at depths ranging from 0 10.cm to 10 -'20 can, occurred to a very small extent. B. IN CROPS 1. Cotton Non-dlintd cotton seeds from Alabama, Arkansas, Louisiana, Mississipi and Tennessee trials have been analysed for ntta.zo and its desmethyl metabolite at harvest,'1 4 to 218 days after, application. The minimum detection levels were 0.03 ppm for norf'Z crazon and 0.02 ppm for desmethyl nor Zura No residues were detected above these limits. 0 2s Cranberries No residues of not Zu:azvn or its desmethyl metabolite were detected in cranberries, grown in various soils in Massaehussets, Washington and Wisconsin, and harvested between 136 and 161 days'; after the ',application of the product., . Fruits Apricots, peaches, grapefruits,lemons-and oranges from various places in USA have been analyzed for no&6Zu,,Lazcn and its desmethyl metabolite. No residues have been detected at harvest. 4. Nuts No residues have been detected in almonds and nuts at harvest. 5. Secondary crops Soybeans and peanuts were grown in soil: which has been treated j with ZOIRIAL in the preceding year. At the time of harvest, no or only very small' residues of no&6Zuxa. on and its desmethyl metabolite 0.1 ppm) could be detected in the foliage. C) ;Milk and poultry Cows were fed feed containing 0, 0. 5, 1.5 and 5.0 ppm no&6 utazon ' daily for 4 weeks. The highest residue of notiZutazon in whole milk was 0.05 ppm. The residues in the milk solids did not exceed 0.04 ppm. esm'ethyl-nox6tu azon residues were simi 1 ar to those of not4tutcdzon. The total residues in fat and kidney did not exceed 0.05 ppm, those' { in muscle and liver 0.03 ppm. Hens were fed diet with the same doses for 4 weeks'. The residues of not6 unazon and its desmethyl metabolite was always below 0.01 ppm. I The total residues did not exceed 0.03 ppm, 0.05 ppm and 0.03 ppm in the fat, muscle and liver, respectively. I f i I a Metabolism 1 In plants Metabolism studies in cotton plants (tolerant crop) and corn (sensitive crop) have shown that no. Zu�Lazon is absorbed fast from the soil or nutrient` solution. Translocation into the foliage is slow in cotton, but fast in corn. Furthermore,' cotton seedlings appear to metabolize F not6ta .a.zon moreslowly than corn. N-demethylation is the major degradation pathway leading to significant quantities of desmethyl-not4tuxLa.zon Additional small quantities are recovered as water soluble, probably con- jugated, metabolites and as bound material. CF3 F I — N N � NH 0 C1 0 C1 non una on desmethyl-not6Zutca.zon . In soil Degradation of rotruxzon in various soil types leads almost quantitatively to the formation of d smethyl-not 6Zuta.zon. Only very small amounts of polar material is found; soil bound residues are present in quantities of less than 10%. AGRQ DOK E-4358 - 1 - i . 1n animals I Rat. No btu anon'given as a single dose of 50 mg/kg, is absorbed at'a minimum extent of Q. The blood and tissue 'levels reach peak concentration after 2 hours, and then rapidly decrease. Excretion is almost complete within 96 hours, 8` and 20% being excreted in the faeces and the urine, respectively. Three major pathway seem to be operative in the detoxifi- cation of no, Zunazon: d methylation yields desmethyl- ox4Zu.a on, hydroxylation processes involving the replacement of chlorine in the heterocyclic ring leads to 4-hydr°oxy non .2u4azon and its conjugates, and elimination of'chlorine and conjugation through a i ° sulfur atom. i I .. i i - i i 1 E r i { 1 N N ,.._. CND R-N NH 0 l 0 cl nox6Zutazon desmethy -non . u :azon i N — N (H R—P� R— N NH2 0 cl 4 ON 0 -don a intermediate hydroxy-non.uxazon Sconjugates N -- N NH 0 0-c nj , O-conjucdate R Suggested pa"Chways of detoxification of no Zuxazon an the rat. n µ � Fish: The fish are likely to accumulate.ndt more than 13 times the concentration of no 6 u .a.zon in the .surrounding medium. In herbicide -free water, the fish eliminated 91 9`5` of the absorbed compound within 10 days. The metabolism of the absorbed no btu. Lazo t leads to desmethyl not6 u..zon, as well as to polar and conjugated metabolites and to small quantities of unextractable material probably j} bound to the tissue. I DISSIPATION Photo -degradation In a model experiment, sunlight exposure of not6 u�La.zon in aqueous solution caused rapid decomposition. Within 140 hours of exposure, approximately 90% of nox6Zutazon was -decomposed. t. Besides various polymerization product,, dezc . o u-no 6Zu . zon and desmethyZ-not4Zutazon were identified. no& Zu ta.z o>n C3 ,C 3 N N 0 C1 h*v 'v CF3 CF RCN 3 0 Cl 0 AGRO [its E- 3 d 17 Volatilization Laboratory studies have indicated that notituxazon volatilizes from the soil; in a typical experiment, l of the applied' no)tjZuAazon had ,volatilized from the treated soil in seven weeks. Leaching The leaching behaviour of not6tuxazon was investigated in soil column tests in comparison with other herbicides;the results indicated that there was only slight movement in the sail. order of decreasing mobility ' try. f Zura Z ne norfLurazon diuron fZuometuron Results of field experiments have confirmed the findings of model experiments. Thus, there will be no ride because of groundwater contamination. Adsorption The amounts of nox4 u:tazon adsorbed by various types of soil are relatively small; they range from 0.003 to 0.16 mlcromoles per 9 of soil, at a concentration of 25 micromoles per litre of water. Conclusion PUnder field .conditions, the dissipation of noA6IZu,ta on from the soil seems to be brought about mainly by volatilization and photochemical degradation. 6 Biological Action Biological i ZRIALO (as well as all formulations containing no.tu�La.on as active ingredient) is a pre -emergence surface -applied herbicide, activated by moisture. It has little post -emergence activity. The action on weeds is selective,and it controls a number of mon,ocoyledonous- as well as dicotyledonous -weeds. The active ingredient is taken up by the roots, and is immediately distributed within the emerging plant, where ZORIAL causes a loss of chlorophyll in the susceptible plants, which become whiten This chlorophyll removal is an indirect result of an interruption of carat n id synthesis. The carotene pigments act as protector against photooxydation of the chlorophyll. Susceptible weeds, germinating and growing, in ZRIAL- heated soils, will therefore change, sometimes with some intermediate red discoloration, to a white colour. This sympton and the subsequent necrosis of the young plants, are the result of a successful application of ZOR'I L.' Notitu,%a on has rather a long residual action in the soil, which may vary according to soil conditions, such as composition, structure and moisture, and also according to sun radiation and to temperature. Depending on the crops to be treated, the rates of application are variable. In perennial crops such as cranberries, fruit trees, nut trees, citrus, etc..., the rates of application can be increased to a curtain level, without endangering the crop itself, and where the efficacy is also good on some perennial noxious weeds such as ` ru spp., C n don spp., Carex spp., Juncus spp., etc.a. In favourable cases, some of these weeds have even been destroyed. Permit No. NCO000437_ SUPPLEMENT TO PERMIT COVER SHEET Sodyeco, Inc. hereby authorized to: post chlorination facilities, Tpolishing Rponds, post aer facilities, and sludge lagoon located at Sodeco, Inc. I Mecklenburg County (Note fart III, Condition -Nos. B & C' Permit) , and 2. Discharge from said treatment works into the Catawba Ri is classified Class A -II. ou"I U i 4.Iluf Effluent Characteristics Kg/day (lbs/day) Other Units (Specify) ***Measurement Sample Sample Daily Avg. Daily Max. D��iiyAy�g, gaily I �Yma x�. quency Fr—e -1y:�p:e:— Location Flow 3.9 MGD Daily Continuous I or E BOD + .45 (NH 11 (2667) (8/001) Daily Composite *****I,E,U,D 3-N) 5 BOD + .45 (NH (21 (4749) (14,247) Daily Composite *****I,E,U,D 3-14) 5 TSS 443(976) 1,329 (2,928) Daily Composite I,E Phenols 0.8(1.8) 1.6(3.6) Monthly Grab E Fecal Col, form 1000/100 ml 2000/100 ml Monthly Grab E,U,D Temj,.)era.ture Daily Grab E,U,D Dissolved Oxygen (minimum) 5 mg/l Daily Grab E,U,D COD Weekly Composite E Total Residue Weekly Composite I'E Settleable Matter Daily Grab E *Saniple Locations. I - Influent, E Effluent, U - Upstream, D - Downstream **All stream samples shall be grab samples. July, August, anc _. <:., k" czWQ"L-UU0C -w c LU-nc.,, UO t:L"" t<« tic: 1; period wi 11 has determined as follows: A 4-hour aver minimum instantaneous flow quantity plus 15 C FS 7 1 t1 nne Whine from 7:00 A.M. to 7:00 P.m,, the --hour hour ave <aqp flow rate is greater than or equ= 7:00 A.M. in accordance with Equation No, 1 N113--N r,"°aan he discharged from 7:00 P.m. to 7:0( begins operation after 7:00 P0., I+t)D5 and NH, EQUATION NO 1 Summer [ 1. ) (333.3 1h/hr max.) BOD5i ROD5 di chaar< Discharge Day begin; ige would he (30 x 106 + 00 + 1 5 )' = 442) . _ W;11 3FiC}C7. x... anca ranY' P.M. clude the sed by the 2-- ~pan he released in accordance} with Equation 1. W nt.er[2) ,1 lhsfhr. avg. t3C7D5 0.5 (NH3-- )l 197.9 lEas/hr. avg. (593.7 lbs/hr. max.) lhs/hr. 13ODs + 0.31 (NH3-N)-< (B) bs/hr. ite, lbs,/hr. A and It are defined het o (`i"Y dividing daily discharge by 2 A (lb/hr) F low: CFS AVq c3 to 175 2 3.E 47.2 5 175 to 250 43.5 87.0 aa a hourly rates will ho calculated 3 (]lb/hr ) re�a � t^tax, 1.2 108.4 n8 199.6 V I WA C Part I Permit No. NC B. SCHEDULE OF; COMPLIANCE 1. The permittee shall achieve compliance with 't 1 is himitation specified for discharges in accordance t NOT APPLICABLE . No later than 14 calendar days following a'date deeit erdantifiein the aof W schedule ofcompliance,�t c r perm ttee ssubmitfinns bein required by identii case, 1,11 jjv;'I � ­ , ---- actions taken, and the probability of meeting the next 4&I4' PART Permit No. NC Act used hereinens the Federal Water Pollution Control Act, As amended. DEM used herein means the Division of Environmental Management oft e Department of Natural Resources n Community evelopmen "E C" used hereinBans the North Carolina Environmental Management Commission. C. MONITORING AND REPORTING 1. Representative Sampling Samples and measurements taken as required herein shall be representative of the volume and nature of the monitored discharge. 2. Reporting Monitoring results obtained during the previous month(s) shall be summarized for each month and reported on a Monthly Monitoring Report Form (DEM No. MR 1. 0, 1.15 and 1.4) postmarked no 1 ater than the 45th day following the completed reporting period. The first report is due on The DEM nay`require reporting of additional monitoring rsu then daily discharges by weight divided by the number of days sampled during the calendar monthwhen the measurements were made. e "daily maximum" discharge means the total discharge by weight during any calendar day. est Procedures st procedures for the analysis of pollutants shall conform to The EMC c ations published pursuant to N. Cm G. S. 143-215.63 et seg.. The ater and Air Quality Reporting Act, Section 304(g), 13 dSC 1314, of the ederal Water Pollution Control Act, As Amended, and Regulation 40 CFR 136. ecording, euts or each measurement or sample talon pursuant to the requirements of his permit, the pe mitt e shall record the following information: PART Permit No. NC a. The axed place, date, and time of sampling; b. The dates the analyses were performed; e. The persons who performed the analyses; d. The analytical techniques or methods used; and e.The results of all required analyses. Additional Monitoring by Pere tte i It s Retention Environmental Protection `A en y. PART I Permi t No. NC A. MANAGEMENT REQUIREMENTS 1. Change in ischarg ,91& Fol® ing uoh nn+ira thp nerme_ y be modified to specify and licit any pollutants not previously limited. 2. Non compliance Notification If, for any reason, the permittee does not comply with or will be unable to comply with any effluent limitation specified in this permit, the p r itto shall provide the Division of Environmental Management with the followinginformation, in writing, within five (5) days of becoming aware of such condition. a. A description of the discharge and cause of noncompliance; and b. The period of noncompliance, including exact dates and tiros; or, if not corrected; the anticipated time the noncompliance is expected to continue, and sups being taken to reduce, 'eliminate and prevent recurrence of the noncomplying ischarg 3. Facilities Operation The permittee shall at all tires maintain in good working order and orate as efficiently as possibleall treatment or control facilities or systems installed or used by the permittee to achieve compliance h the terns and conditions of this permit. 4. Adverse Impact The permittee shall take all reasonable sups to minimize any adverse impact to navigable abl tees resulting from once pl anc h any effluent limitations specified in this permit, including such o0 lrat or additional monitoring as necessary to determine nature n impact of the noncomplying discharge. . 5. Bypassing Any diversion from or bypass of facilities necessary to maintain cl'i o with the terns and conditions of this permit is prohibited,except (i)'where 1 PART II Permit No. NC unavoidable to prevent loss of life or severe property damage, or ii) where excessive storm drainage or 'runoff would damage`any facilities necessary for compliance with the effluent limitations and prohibitions of this permit. The permittee shall promptly notify the Water Quality Section of DEM in writing of each such diversion or bypass. 6. Removed Substances Solids, sludges, filter backwash, or other pollutants removed in the course of treatment or control of wastewaters shall be disposed of in a manner such as to prevent any pollutant from such materials from entering waters of the State or navigable waters of the UnitedStates. i. Power Failures In order to maintain compliance with the effluent limitations and prohibitions of this permit the permittee shall either: a. In accordance with the Schedule of Compliance contained in Part I$ provide an alternative power source sufficient to ;operate the waste- water control facilities; or,if such alternative power source is not in existence, and no' ate for its implementation appears in Part I, b. Halt, reduce or otherwise control production an /or all discharges from wastewater control facilities upon the reduction, loss, or failure of the primary source of power to said astewater control' facilities. . Onshore or Offshore Construction This permit does not authorize or approve the construction of any onshore' or offshore physical structures or facilities or the undertaking of any work in any navigable waters. 1 PART II Permit No. NC B. RESPONSIBILITIES 1. Right of Entry The permittee shall allow the Director of the Division of Environmental Management, the Regioral Administrator, and/or their authorized represen- tatives, upon the presentations of credentials.* a. The enter upon the permittee's premises where an effluent source it located or in which any records are required to be kept under the terms and conditions of this permit; and b. At reasonable times to have access to and copy any records required to be;kept under the terms and conditions of this permit; to inspect any mpnitcring equipment or monitoring method required in this permit; and to sample cry discharge of pollutants. 2. Transfer of Ownership or Control This permit is not trans fern ble. In the event of any change in control or ownership of _fa,.ilitips from which the authorized discharge emanates or is contempTated, the permittee shall notify the prospective owner or controller by letter oil the existence of this permit and of the need to obtain a emit it the name of the prospective owner. A copy of the letter shall beforwarded to the Division of Environmental Management. 3. Availability of Reports Except for data determined to be confidential under N. C. G. S. 143-215. 3(a)(2) or Section 11008 of the Federal Act, 33 USC 1318, all reports prepared in accordance with the terms shall be available for public inspection at the offices of the Division of Environmental Management. As required by the Act, effluent data shall not be considered confidential. Knowingly making any falqp tfafamont nn amen citeh rannrt mAv roctilt in tho imnncifinn of rrit inal penalties as provided for in N. C. G. S. 143-215.6(b)(2) or in Section 309 of the Federal Act. 4. Permit Modification After notice and opportunity for hearing pursuant to N. C. G. S. 143- 215.1.G (b)(2) and .-S. 143-215.1(e) respectively, this permit may be modified, suspended, or revoked in whole or in part during its to for cause including, tut r:jt limited to, the following: a. Violation of any terris or conditions of this permit; b. Obtainirg th's pemit by isrepresentation or failure to disclose 4 ,ully reievarril, facts; or c. A change in any condilk-ion that requires either a temporary or permanent reduction or elimination of the authorized discharge. M 10 & 1 9 PART II Permit No. NC 5. Toxic Pollutants Notwithstanding Part II, B-4 above, if a toxic effluent standard r prohibition (including any schedule of compliancespecified in such effluent standard or prohibition) is established under'Section 3 7 of the Act for a toxic pollutant which is present in the dischargeand such standard or prohibition is more stringent than any limitation for such pollutant in this permit, this permit shall be revisedr modified in accordance with the toxic ' effluent standard or prohibition and the permittee so notified. 6. Civil and Criminal Liability Except as provided in permit conditions' on "Bypassing" (Part II -5 an "PowerFailures" (Part II, , nothing in this permit shall be construed to relieve the p r itt a from civil or criminal penalties for noncompliance pursuant to N. C. G. S. 143-215.6 or Section 309 of the d ral Act, 33 USC 1319. 7. Oil and Hazardous Substance Liability Nothing in this permit shall be construed to preclude the institution f any legal action or relieve the permittee from any,responsibilities, liabilities, or penalties to which the permittee is or may be subject under N. C. C. S. 3 .7 `et seq. or Section 311 of the Federal Act, 33 USC 121 . Property Rights The issuance of this permit does not convey any property rights in either real nr n r mn l nrnn rfv _ nr anv'axrlimivp nrivileces. nor s ` it rights, or any inringmant;of oral,State or local laws or regulations. . Severabi11ty The provisions of this Der it are severable, and if any provision of this perm,it. or the application of any provision of this permit to any circum- stance, is held invalid, the'application of such provision to other cir- cumstances, and the remolAndef this permit shall not be affected thereby.` 11 & 1 1 PART II Permit No NC 10. Expiration of Permit Permittee is not authorized to discharge after the expiration date In order to receive authorization to discharge beyond the expiration date, the permittee shall submit such information, forms, and fees a are required by the agency authorized to issue permits no later'than 13 days prior to the expiration date. Any discharge without a permit after the expiration will subject the permittee to enforcement procedures as provided in N. C. G. S. 143-215.6 and 33 USC 1251 et seq.. PART II Permit No. IBC OC B. previous Permits All previous State grater quality permits issued to this fac.lity, cat SvYA 3»4Mb&AW.43. Lt: u�vma. su �.,. e.+.,®-^.•• ,,,,. C. Construction No construction of wastewater tread shall be begun until Final Plans an to the Division of Environmental Authorization to Construct have been Plans and Specifications have been Management after 30 days following this permit, whichever is latter, t; and construction authorized. D. Certified Operator Pursuant to Chapter 90A of north Ca shallemploy a certified wastewater charge of the wastewater treatment ae rational Pollutant Discharge a :this facility. ac,lities or additions thereto Lfications have been submitted it and. written approval and y the Division of Environmental t of the plans or issuance of ns may be considered approved of the Clean Cuter Act, if the effluent standard or .i2-mJLaL,-L U >L or approved.: (1) contains different conditions or iscattier se more st it than any effluent limitation in the permit; or (2) controls any pollutant not limited in the permit. The permit as modified or reissued under this paragraph shall al: any other requirements of the Act then applicable. 112 Zi WiAl 8.11 Wxi r— 6 w+ a. xaras aas .aae —ew w.e sww wvYxm +.»an wu -- 1—. permutes is authorized to discharge from utalis serial numbs. 001. Such discharges shall be limited and monitored by the pemittee as specified bet �t Characteristics Discharge Limitations M i t i ui nt Kg/day lbs/day) Other Units (Specify) asurmt Sample Sample Dai ,l l t i y Aga atl y f Frequency ti .9 MGD Daily Continuous l or .45 (NH3-N j l l (2667) (8(8,001) gaily Composite ** 1, , 1, b .45(NH 2-W [2) 7 9 1 ,2 7) gaily Composite l,C,b,p ,(976) ,329 , Daily Composite I,C CaS(1a ) 1.6(3.6) Monthly Grab E ,oliform 00 /100 ml 20001100 ml Monthly Crab E,U,D Lure Daily Crab E,U,D ied Oxygen 5.6 mg/l Cady Crab E,U,D Weekly Composite residue Weekly Composite l,E able Matter Daily Crab F a Locations: l - Influent, C -, Effluent, b m upstream, D - Downstream stream samples shall be grab samples. ly means every day on which a discharge occurs except Saturday, Sunday, and legal holidays. Daily stream sampling reduced at each sampling station to one time per week except during the months of June, duly, August, and September he frequency must be no less than three 2 times per week at each sampling station. e temperature of the effluent shall be such that it will not cause a temperature in the receiving stream a e than 5 F above ambient st can water temperature. gil5 only on upstream and downstream samples. ' a 1_m -it -L-11 —L - 1 c— P ,zA2kwt t+c nnr nroator than n A qtandard units a u —Acenaphth —Acrtionitrito Tel Chlorobom r " 1.2 . c -1.1.1-Trichk -1 4 . karat -I.I*DkhWcm CrGr t 1 i+ 1.2-trans- DeADMOM -Z4. . . 1 mop ..1.3- ;-2,4_ thyt - 2.4- ok - 2,6 " tok Ettrowzeno F isj22 chlmisw ettw- Me -HexactooroW - Naphthalene_ -°Nttr - 2-Nitmpi 2,4-CKnitr phoe phond- . Sisj p to - - Diethyl rs ` thra SOAZO(a{a Ya sonzo&xwa � A 1 Tatra ,1 tha t Fiber for mar, f� :w as . t• a e-r s DRANDUM Steve `redder 4: Randy Dodd Js Trevor Cle eats RONMFNTAL MANAGEMENT r 17, 187 lation vtzj.w ,l--<*L UL auuvu average z or UCLO per in; a draft WLA for your review,. advise if questions. �ercash Cason ,eson Catawba River Fic u 1 2 3 14 1 J b 0 ,17 10 4 4 stain Island Dam 31 3 Recommended Compliance Reporting Form (3) () (5) (6) 7) Allowable )5 and NH3 requirements attached, Recommended %rastre .m Self-Monitorin East Barak approx. At or near Immed, Upstream 1 mile downstream 1-85 Belmont. Scam/Win Sum/Win Stataa/Mira / W/ M W/ M W/M W/ W / BW W BW W BW W / W j BW W/ BW W/ BW W/ �ty W/ BW W/ BW W/ BW W/ `e l W / BW W / BW W / BW W / W / W W / y Iy ekly V. C. DOE] ' , Ee tL POST :L"tF- f'6C;F EiC1X 334,19 C HAA,CC,TTE. NORTH CsA ROI INA 2Ci233 July 6# 1981 � t Robert F. Btlms actor t Office ox 27687 eigh, North Carolina 27611 Re: Ap Pea M .Helms: rye 29, 1981. re. Sincerely, OGLETREE, DEAI "f°EWA Attorneys fact By Lewis 1T. t-o" L. Page Benton STATE OF NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES AND COMMUNITY DEVELOPMENT DIVISION OF ENVIRONMENTAL MANAGEMENT FACT SHEET APPLICATION FOR NATIONAL. POLLUTANT DISCHARGE ELIMINATION SYSTEM PERMIT TO DISCHARGE TREATED WASTEWATER Application No.: NCO004 75 hate. March 22, 1988 I. SYNOPSIS OF APPLICATION a. tame And Address of Applicant Sandoz Chemicals Corporation P.O. Box 669246 Charlotte, NC 28266 b. Description of Applicant's Operation Manufacture and processingof dyes and organic chemicals C. Design Capacity of Facility 3.9 MGD (Summer) .6 MGD (Winter) d. Applicant's Receiving Waters Receiving Stream: Catawba River Classification: WS-11I Sub -Basin. 0 -08- 3 For a sketch showing the location of the disclinrge(s,), see Attachmei e. Description of Wastewater Treatment Fac i.l idt i e<.t The existing wastewater treatment plant coaatain a series of e basins for acid neutralization, Freaer.ation and equalization, f settling, biological treatment, thiosul fate oxidation, of luen polishing and effluent storage. There are also gravity cari.fa adjustment, chlorination and past aeration facilities, PWV I. description of Discharges (as reported by applicant) 2.2 domestic. 97. gindustrial Pollutants which are present in sfgn1fKnnt qunnt. i t ips or which are subj effluent limitations are as follows: Effluent aracter tic R or:tred^Value SEE ATTACHMENT B (Specify un'i Average Mardi 2. PROPOSED EFFL LIMIT °TIC M See attached copy of Effluent Page(s) from Prafc Permit The applicant will be required to monitor regularly f nr flow and t parameters limited in Section '2 above with sufficient frequency to compliance with the permit conditions. Frequency. methods of rampl and report dates will be 'specified in the final permit. 4. EFFECTIVE ' DATE OF PROPOSED EFFLUENT LIMITS ANTI~ CQP IANCE S DULE IF APPLICA Q)T The proposed effluent limits will he affPc# ivo "porgy issuance of the Permit, a. P 0170 ED P "ITT, C_t?R } iTION a Will 3 1 11& _PjVE t. SICNII ICAN'i MPACT CN' THE C. SCl{ARGE Part III W -;Toxicity Requirement 6, E a i _ PE -Pt Pf SED F'F LU _._ L l; "I" The Division of Environmental Management uses an EPA -approved model assign limits for BOD , ammonia nitrogen, and "dissolved oxygen to p the dissolved oxygen crater quality standard fn the "recniving stream water_ :duality standard for dissolved oxygen is staved in 15 NCAC 2 The total suspended :solids limit is based can guidelines rontaf.ned it NCAC 2E.0400. The pH and fecal col iform limits are based on water quality <standa l contained in 15 NCAC 2B. f121.2. e toxicity limit is based on the instream wfftKer- concentration. `Cl and organic pesticides limits are contained in the federal guidelini MBAS, sulfate, mercury, manganese anese and phenols limits are based on quality standards. VARIANCES OR AID RNA IVE TO _R t�illPFt3 STANDARDS S 8. DISCUSSION OF PREVIOUS NPDES PERMIT CONDITIONS The previous NPDFS Permit contained the following limitntions, (e'N monthly averages): 11OD5 + .45 (N113-N) 2667 lbs/day BOD5 + >45 (NI13-N) 4749 lbs!(iny TSS 976 lbs/day Phenols 1.8 lbs day Fecal Colliform 1006.0/100 ml Dissolved Oxygen (minimum) 5.0 mg/1 The NPDES Permit expires on: March 10, 1988 igh, North Carolina 27611, between the hours of 8:00 n. ay through Friday. Copies will be provided at a clinyge E CONTACT tional information concerning the permit. Appliccat. ion may r, Luln Harris 919) 733-5083 Ell SCHEDULE FOR PERMIT 1SSUANGE raft Permit to Public Notice ermit Scheduled to Issue - URES FOR THE FORMULATION OF FINAL DETERMINATIONS t Period Dn of Environmental Management proposes to [s%no an NPDES pot subject to the effluent limitations and specie] conditions cat ase determinations are tentative and are open Lo comment fron persons are invited to subudt written comments on the permit )ivision of Environmental Management's Proposed dotorminatior %ddress: DIVISION OF ENVIRONMEITFAL MANAGEMENT WATER QUALITY SECTION POST OFFICE BOX 27687 RALEIGH, NORTH CAROLINA 27611 All, comments received within thirty days fol lowing the, date of public notice will be considered in the formulation of final determinations with regard to this application. b. Public HeAr—jig The Director of the Division of Environmental Management may hold a public hearing if there is a significant degree of public interest in a proposed permit or group of permits. Public notice of Riirl, n i A tirtin —11 1— —,--1 ns. .4 1- fl- 1-- geographical. area of the discharge and to 'those on the Di'visio'n of' Envi Management's mailing list at least thirty days prior to the hearing. Following the public hearing, the Director of the Division of Envirormic, Management may make such modifications In the terms and conditions of t permit as may be appropriate and shall issue or deny the permit. Notic or denial, will be circulated to those who participated in the hearing 6 appropriate persons on the. Division of Environmerittil Management's malli If the permit is issued, it will become offective 30 days following dat and will be the final action of the Division of Environmontn"! Managemen appeal, hearing is granted. c. Appeal jfeartn&:i An applicant whose permit is denied, or is granted subject to condition unacceptable, shall have the right to a nearing before the Commission is written demand to the Director within 30 days following issuance or den permit. d. Issuance of the it - when -11no-lea? .ings PrIf,, lield If no public hearing or appeal hearing is held, and nftet- review of tl-,(- itially unchanged, the permit will be issued arid become effective Ltely. This will, be the final action of the Division of Environmental ient. earings are held, but there have been substantial changes, public notici ision of Environmental Management's revised determinations will be made. ng a 30-day comment period, the permit will be issued and become effect.1 rely and this will be the final action of the Division of Environmental ent unless a public or appeal hearing is grantt,,,.d. i NORTH CAROLINA ENVIRONMENTAL MANAGEMENT COMMISSION MECKLENBURG �TTER OF WLINA AMENDMENT TO ZMIT NO. SPECIAL ORDER BY CONSENT 5, HELD EMC WQ 83-05 Ad ,0 INC. Sodyeco and the Commission here (a) That Sodyeco holds North Carol for making an outlet to the Ca (b) That Sodyeco is unable to coml-, tations and mcnitoring requirE constructing and properly opei ment facilities; (n) That non-comoliance with the c in nArAa-ranh 1(h) above c �co is within the jurisdiction of the C meats of North Carolina General Statute 143-215.4 an rules in 15 NCAC 21, and also hereby waives its righ this Special Order by Consent in accordance with Nor General Stature 143-215.5 (eco, desiring to comply with conditions of the Permit )aragraph l(b) above, does hereby =agree to do and perf following things: Comply with all conditions of the permit except thos in paragraph l(b) above; Upon execution of this Order, undertake the followir, in accordance with the indicated time schedule: -2w (1) Submit plans, specifications and requests for Authorization to Construct additional facilities and modificationsto existing facilities necessary to comply with the final efflu- ent limitations and monitoring requirements within three months of execution of this Order. () Rein construction of proposed facilities and modifications within one month of .issuance of Authorization to Construct. () Complete construction of proposed facilities and modifications within nine months of beginning construction. () Comply with the final effluent limitations and monitoring requirements within three months of completing construction and no later than thirteen months after receiving Authorization to Construct. (c) Daring the time in which this Special Order by Consent is effective comply with the followings interim effluent:limitations and monitorin requirements (1) S nner April 1 - October 31 (2) Winter: November 1 - March 31 SEE ATTACHMENT (d) No later than 14 calendar days after any date or time identified fear acc�ompl shr ent of any activity lasted in 2(b) above, submit to the Director, Division of Environmental Management, North Carolina Department of Natural Resources and Community Develop- ment, written notice of compliance or non-compliance herewith. In the case of non-compliance, ce, the notice shall include a state - times for accomplishment of listed activities ation of terms of this Special Order by Consen to achieve interim effluent limitations set fo nd Commission rules ,in 15 NCAC 2J. his Special Order by Consent shall expire; on August 1, 1984. ntered into this they 9th day of dune � 1 N.C. ENVIRONMENTAL NMENTAL MANAGEMENT CGMMI P ( BY: 1�r°e ident Chairman Ual ry Aug. Dai ly Max. Da ya g.�g_y pI p Daily Avg. DailyMax. Y uenc Y [i M Flow 3m9 MGD ally Continuous I dr BOD5 + d (N 3-) (1) (800) (1,600) Daily Composite***** 1,E,U,D BOD5 .31 (NN3 ) (2) (6,225) (12, 00) Daily Composite***** I, ,U,D TS 443(976) 1,32(2,9) Daily; Composite I,E Phenols (1) () (10) Monthly Grab E (2) (1) (0) Monthly Grab E Fecal Coliform 1000/100 ml 20001100 ml Monthly Grab E,U,D Temperature Daily Grab E,U,D Dissolved Oxygen (Minimum) 5 mg/l Daily Grab E,3,D COD Weekly Composite E Total Residue Weekly Composite 1 E Settleable Matter Daily Grab E *Sample locations: I -Influent, E-Effluent, U-Upstream, D-Downstream **All stream samples shall be grab samples, ***Daily means every day on which a discharge occurs except Saturday, Sunday, ;and legal holidays. Daily stream sampling may be reduced at each sampling station to one time per week except during the months of June, duly, August, and September when the frequency must be :no less than three () times per week at each sampling station. ****The temperature of the effluent shall be such that it will not cause a temperature in the receiving stream of more th F above ambient strum water temperature. *****BOD5 only on upstream and downstream samples. The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units and shall be monitored daily by grab sample at I, E, U and D. Perm SUPPLEMENT OT PERMIT COVER SHEET Martin Marietta Corporat1 on-Sadyecc Division authorized to: Continue to operate a 3,9 MGD activated a.11lud e wastewater t` During the period beginning on the effective state dnU IOILI"q W1411 eXPt.rcii.VUII permittne is authorized to discharge from outfal1(s) serial number(s).00l . Such discharges shall be limited and monitored by the permittee as specified below: EffluentCharacteristics shar e 1 �l tatc�ns Mons turin e u cements Kg/day (,lbs/day) Other Units (Specify) }:.°Measurement ::°% Sample :i Sample arly Avg. Daily Max. Daily Avg. Daily Max. ire uency I.ype I atinn 3.9 M D Daily Continuous 1 or k ow + ` .wn Mi 10 1 ) (2667) (8,001) Daily Cottr cr.aale * *I,E,U,D + 5(NH N) t2l (4749) (14,247) '. . , r ... . .,, � <. Ilar.ly ..r r... ..1 .E.a oml»�aate ,,i ,it 5� 443(376) 1,3 9(2,92S) Daily Composite l,E l c t r Form 1000/100 ml 2000/100 nml Monthly Grab t;,U,D r: Daily Grab E,U,D } aqoLved Qxyfen (minimum) 5 mg/1 Lally Grab E,U,D Weekly Composite E )1) 'Mal Residue Weekly Composite l,L j1le Matter Daily Grata L r im€mp i e Locations: I - In f°l.uont it - Effluent, U -- Upstream, D - Downstream ll stream samples shall be gran samples. .Qaarly means every day on calmich ar dr.schaarrge occurs except Saturday, Sunday, and legal holidays. Daily stream sampling may be reduced at each sampling station to one time per week except during the months Of June, July,August, and �k�,t. arnErcr when tll,a Cr k'r4imr�. rmcy must b n Less than three (3) times maes per creek at each �aampl in station. c� ..`:ems, temperatureof theeffluent shall be such that It aial.ls not cause a temperaturein the receiving stream Qf 21 ;,l —, morH l,hi`4an 5 above ambient' stream am water temperature. ,.BOD . oniv on upstream and downstream samples. ttC D and Nil -N ,hall both be reported. on I and E. a can be released in accordance 7:00 P.M. period will be deter include the minimum instantane released by one turbine from 7 If the 4-hour average flow r PM. to 7:00 A.M. in accordance and NH3-N can be discharged fr operates after 7:00 P.M., BOp EQUATION NO. 1 ( EQUATION NO. 2 B B N D A ,..�.....0 ..x.w...,��...«y,..tea -� 10 P.M. If at least one turbine begins operation after 7:00 P.M., BOD5 and NB - i Equation 1. At 7 00 P.M. the total daily stream flow daring ,the 7:00 A.M. to �d as follows. A 24-hour average discharge rate will be calculated which will flow quantity plus 15 US 7Q10 from Dutchman Meek. (i.e. if 30 x 106 ft3 was A.M. to 7: 0 P.M., the - bour average would be (30 x 10 + 80 + 15) = 442). 3600 x 24 .a greater than or equal to 329 CFS, BOD5 and NH3-N can be discharged from 7:00 i Equation No. 1. If the 24-hour average flow rate is less than 329 CFS, BOD5 1:00 P M.to`7:00 A.M., in accordance with Equation No. 2. If at least one turbine I NB3_N can be released in accordance with Equation 1 until 7:00 A.M. (1) Winter () -I Offi45( 3 N) < i111.1 l.bs/err. avg. BOTH + 0.5 (NH3--N) < 197.9 lbs/hr. avg. 3 l.bs/hr max.) (593.7 lbs/hr: max.) 0.54 (NH3-N) < (A) lbs/hr» B00 + 0.31 (NH3-N) c (B) lbs/hr. BOD5 discharge rate, lbs/hr* I = NH --N discharge rate, .bs/h . Large Day begins at 7:00 A.M. l B are defined Below (The hourly rates will be calculated dividing daily; :arge by 24); A lb/hr) B (lb/hr) CFS AvZ. Max. s Avg. Max. 175 23.6 47.2 54.2 1083:4 : 20 43.5 87>0 99.8 1996 329 84,5 169»0 150.3 300'.6 Part I Pe I JLC OF COMPLIANCE 4 4 4. nn mniiara uii+h fhp Affluent li A - specified for discharges in accordance with the following 'sct NOT APPLICABLE No later than 14 calendar days following a date identified i schedule of compliance, the permittee shall submit either a progress or, in the case of specific actions being required dates, a written notice of compliance or noncompliance. In case, the notice shall include the cause of noncompliance, a actions taken, and the probability of meeting the next sched PART I Permit No. NC REVISED t used herein means the Federal Water Pollution Control Act, As acne., M used herein means the Division of Environmental Management of the partment of Natural Resources and community Development MVI used herein means the North Carolina Environmental Management mmfission. GRIN G AND REPORTING presentative Sampling �d discharge. ,ti ng .oring results obtained du ing any calendar day. ocedures ocedures for the analysis of pollutants shall conform to The EMC ions published pursuant to N. C. G. S. 143-215.63 et'seq.. The nd Air Quality Reporting Act, Section 304(g), 13 CSC 1314, of th Water Pollution Control Act, As Amended, and Regulation 40 CFR ng Results h measurement or sample taken pursuant to the requirements of mit, the permittee shall record the following information: PART T Permit No. NC a. The exact place, date, and time ofsampling; o. The dates the analyses were performed; c: The person(s) who performed the analyses; d. The analytical techniques or methods used; and e. The results of all required analyses® Additional Monitoring by Permut e f the permittee monitors any pollutant at the locations)' designated herein more frequently than required by this permit, using approved -onmental Protection A envy. t ii UIREMENTS Discharge %rnpq authorized herein shall be ccztnv i 1 t x ance Notification ,rms and ;i`fi d 11s installed or owes vjy a t— .... s and conditions this permit. impact iittc shah takerascbi steps act navigable waters raslti from p inc s specified i this permit')dateding i h theertatdr l an ial monitor i a necessary t : m l ing discharge. ng rsicn from or bypass of facilities necessary to maiI ,e, terms and conditions of this permit is prohibited, 1 PART II Permit No. I unavoidable to prevent loss of life or severe property damage, or (ii) where excessive storm drainage or runoff would damage any facilities necessary for compliance with the effluent limitations ire hibitions of this permit. 'y the Water Quality Section c �sion or bypass. fed Substances permittee shall promptly M in writing of each such i ties; power source is not in existen ars in Part I, tewater control facilities upon the reducti0i of the primary source of power to said wastes es. ,ffshore Construction shore physical structures or facilities or the undertaking c n any navigable waters. Y. 2 a. o FORM 3. ITEM SACI€LTA ORA Ii TO 0 LO TTt RIVER PAST FILL WATER DRUM 90 PAGE$ 100t INTAKE AREA R x R ACID I OLLEC'I R S INCR 2 EETE \0R S RACE Iota a_I51Y t 0 AREA (20'x 25 NEUTRALIIION P R06IC FACILITY t LANDFILL tI50' 2 A o { NS I t 25' x $0' ) SEE _ CATAWB N "Pitt RIVER SE INC 250' It 750' LIQUID WASTE STORACt PRIMARY C TANKS NW I0'a III $% SETTLINC SET ING I00'X 350° E UA I I FINAL ROAD AERATIO PRI14ARY 5rt+# I SETTLING ISO"* 100 LONC CREEK ERMINE LANDFILL IO'X 200' I.S. c TRASi! «O s OR . > PRIXARY 25 0, SE INC 0RUH 150'tt 2000' 11KASHINC 25'X 50' PAST LANDFILL I00'x 200' AEROBIC LACOONSz ACID COLLECTION; I 200 -. A00 I w 150 x 00 .k !$ EC E 2 00' 250' 2 - 2 ' 300' A 3 - 5'M 250' SIER LONC CREEK Scale: " 1,000 ft. approx. k This section provides ;gametal description of the hazardous waste storage facil- ity required by 40 C p 270.14 . This description is intended to acquaint the ;permit application reviewer/permit writer with an overview of the facility. More complete details can be found in other parts of this permit application. 1. C x� t l cri 140 CFR 270.14> 1 Sody c , Inc. is located on Highway 27 West in western Mecklenburg County, North Carolina. facility is bordered by the Catawba diver on the west. The mailing address is: Sody co, Inc. Post Office Sox 66946 Charlotte, North Carolina 8 66 9 46' This facility is primarily a manufacturer of sulfur dyes, disperse dyed, and miscellaneous organic chemicals. This application covers hazardous waste storage containers and tanks, and hazardous waste surface impoundments. The contingency plan covers the satire facility. Hazardous 'wastes that are stored on -site are generated as distillation residues of o-dichlorooen ede, toluene and methanol, off -specification products, clean-up wastes, and production waste's. These;ea to are stored at two sites in drums and at a third site in tank. Surface impoundments in S dyeco:`a wastewater treatment facility are used to store, treat, and disperse of wastewater and associated sludges that l are classified as hazardous wastes. Acid wastewater, prior to neutralization exhibits the characteristic of corrosivity. Otherwise, the wastewater and sludge is classified as hazardous because it contains trace quantities of solvents and sulfide, and could include a small quantity of several listed wastes. Correspondence and inquiries concerning hazardous waste management activities at 5ocyeco should be sent to: Edwin J. Eccles Manager,Environmental Services (704) 827-4351 2 hic 7Ci� b(1; Figure l is topographic maps showing buildings, waste management areas, and ether details. The sole is l inch feet, with foot contour intervals of elevation. Figure 2 is a topographic map showing the facility* boundaries And land uses. The scale on this map is l inch = 400 feet. All of these maps show surface waters. a Ladd Uses: Figure 2 shows surrounding land `use areas. Other industry Lies across the river; the area surrounding the plant is mostly undeveloped wood- lands with some residential/commercial areas. r b. Hazardous Tate na event pacilit iiodndar The hazardous waste management facilities consist of the drum loaded trailer At Bldg. 33, the concrete storage tank at Bldg. 45, the drum storage area inside Bldg. 42 warehouse, and the wastewater treatment facility. H SCION WASTE: CHARACTERISTICS This section describes the chemical and; physical nature of the hazardous wastes at the Scdyeco facility and the Waste Analysis Plan for sampling, testing, and evaluating the wastes to ensure that sufficient information; is available for their safe handling. The information submitted is in accordance with the requirements of 40 'CFR S 270.1 (b)(1)(2) and (3). 1. Chemical and Physical Analyses for Steed as J CE `270.1 (b)(2) List of hazardous waste stored at facility. Hazardous wastes are stored at this facility in 55-gallon drum containers, a 100,0C-gallop. concretetank, and a , 00 gallon tang. Current inventory (718l83) consists o. 58 containers (55-gallon drums) One 1 0 CCC gallon concrete basin (empty) One 5, 0--gal.l n tank <1 2 full) (This tank is being closed under interim Status and is included here for information only.) The containers (55- allon drums) can be broadly classified into solid wastes and liquid wastes. The wastes are generally compatible with each ether. Occasionally, an ignitable liquid waste may be included in the storage area. Typical contents of each group; are Listed'below. --1 Solid Wastes Still Bottoms -- 'F0 51 F002 Waste Chemicals - -003 Liquid Wastes Waste Chemicals D-003 Still Residues - F003 The solid still bottoms resulted from the recovery of .toluene and of o-d.chloroben ene» The liquid still residues (FO03) result from the recovery of Methanol and are treated as hazardous although repeated tests have given a flash point above 60*C. Are ignitable aqueous waste and a F005 still bottom were previously stored in the 100,000 -gallon concrete basin, but that material has recently been removed to an EPA approved landfill upon completion'oE the production campaign yield- ing those wastes. There are no hazardous waste storage piles at Sodyeco Table. °1 lists the hazardous wastes presently or routinely stored at the Sodyeco facility, ;their associated hazard classification and the basis for the hazard classification. In most cases the classification is based on known characteristics of the wastes, such as i nitability, reactivity, corrosi ity, or EP toxicity ;analyses. For listed wastes, the classification is based can the listing. -w2 Table C--1 c rites associated ila aids, and basis for Hazard Ileac nation Basis for Hazard Chemical Hazard 'Hesi nation Drums Aqueous still residue* Ignitable Listed caste F003 Organic still residue Toxic Listed waste F002 Waste Dinitrochlorobenaene Reactive 0003 Characteristic and dust Tanks`, Organic still residue* Toxic, ignitable Listed caste F005 *Current inventory Waste 11anin All hazardous wastes are labeled at the time they are put into a drum. The label describes the contents of each drum, tank, of container and its asso— ciated hazard, i.e.,, corrosivlty or i nitability< This practice informs workers handling these wastes of the associated hazards so that appropriate precautions can be taken. Details regarding the tanks, containers, storage areas, and personnel training are presented in ether sectionsof this application. General information and hazardous characteristics of the waste types are included in Appendix 1. 2. Waste Anai,,sis flan Stored Waste [40 CFR 270.14 b ( a. Parameters and Rationales 'cable C-°°2 shows the hazardous wastes presently or routinely stored in the facility, the analytical parameters that apply to each, and the rationale for their selection C-3 . A ditinal Ede uirements for W This facility only handles on - requirements for waste receive �nerated Off -Site: venerated wastes; therefore, a off -site generators do not apply. f . New Des of Waste generated: Due to the operation of our chemical manufacturing facility, we will continue to generate new types of waste materials. We will continue to evaluate each new waste streams to determine if the waste is a hazardous materiel. The analysis of these wastes will be made by standard approved methods after which a determination will be made for their proper disposal. 3. Chemical and p sisal Anal sea -Surface im o ndme its Sodyeco has a segregated sewer system for its hazardous wastewater streams. An acid sewer collects the acidic wastewater (corrosive by virtue of its low p and discharges it into storage impoundments ZOO and Z 8. An alkaline sewer collects non -acidic wastes including some sulfide bearing wastes that could be classfied as reactive. Both acid and alkaline waste streams contain grace quantities of spent solvents with classifications of F0 2 and. F003. The l002 wastes include "Y"U 'L*AAI 4-^I,.A- under 261. (a)(2). The wastewater treatment plant staff is notified when unintentional losses occur and actions are taken to properly handle and treat that caste. The acid stream is neutralized with CaO, Ca(OH)2 and/or CaCO3. It then flows to a settling lagoon cohere it mixes with the alkaline stream. Gypsum precipitate generated from the neutralization of sulfuric acid, solids in the alkaline wastewater, and biological solids from wasted activated sludge farm sludges that are classified as hazardous because of the hazardous designation of the. wastewater. These sludges are disposed of in impoundments Z02 , B, and C. .s part of the NPDES`treatment facility, hazardous waste management in the surface impoundments relies on 'proper operation of the entire 'treatment facility. Toward this end, analyses that provide for proper operation of the wastewater treatment facility also provide for proper management of the hazardous castes. Average values of routine analyses performed on incoming wastes from January 1, 1983 to June 30, 1983, are given in Table C-6. "cable C6 Wastewater Influent Average Values for Analyses of Do ily C6m oste Sam les frcim Jaxivary 1, 19'83 thru June 30;, 198 Acidity BOD5 COD ` OC Sulfide a ii Stiff 9/1) Lm9/1) (m /1.) /I) Acid Waste- 0.513 493 1556 474 water Alkaline 479 1296 226 13.1 Wastewater Combined 412 985 16 2. Wastewater In addition to routine analyses, GC analyses for specific wastewater constit- uents have been carried out periodically in the past. -" 4. Sam lin and Analysis Plan urface' m oundments Wastewater composite samples are collected using an automatic sampler programmed to collect equal portions of the wastewater at 1.5 to 30 minute intervals. Grab samples are collected using a glass quart jar attached to a wooden sampling stick. Sampling locations are as follows. Acid Stream 01 influent flume, discharge ..from neutrali- zation tanks Alkaline Stream - Final alkaline suer junction box Combined Waste At Z028 outlet Fixed Liquor Z04 recirculation line Clarifier Effluent,- Chlorine contact basin entrance Final effluent - Final flow measurement flume Continuous pH monitoring probes are in the final alkaline ,junction lox, two places in the acid neutralization tank., Z03, Z04, and the final sampling paint. Continuous dissolved oxygen probes are in Z04 and the final sampling print. Table 7 is a copy of our NPDES permit limitations and monitoring requirements. All these parameters are analyzed using methods approved by EPA. for wastewater. Copies of data log sheets used for process control information are included as 'fable -8. .analyses for specific F002, F003, and F005 constituents are not performed on a scheduled basis. Periodic studies using GC and GC/MS analysis have shown these constituents to normally be present in the raw wastewater in concentrations less than 25 ppm. These wastes, however, do not presently meat the conditions for exclusion under the mixture rule [261.3)(a)(2)'fv. A. & B.I. Any unin-- C-8 tended production Losses of these compounds are reported immediately to the wastewater treatment plant. Several commercial chemical products could be lost to the seder by accidental releases -in greater than de minimis quantities. Small quantities of these materials may also be present as process wastes. Analysis for these compounds is not normally performed unless an unintended loss to the serer warrants such analysis. 5. Cly su ludEe and lastewater Effluent hsract ristics for Basin Z02B Table C-8 shows the results of sludge analyses for 'hazardous constituents which are solvents 00 , 005 that may be in the wastewater. These samples present a composite description of the waste characteristics during the eleven years the basin has been in service. liable C-9 presents the results of tests on Basin Z0 B effluent discharging into Basin Z03. odyeco instituted a spill prevention program and installed facilities to control and contain spills when they occur. The results of this program and new facilities has been a; reduction in the rash wastewater organic constituents based on verbal analysis results from the EPA Effluent guidelines Division. EPA conducted a four week: study of the Eodyeco wastewater treatment facility and reported that early results indicate the raw wastewater generally contains 2 to 3 m /l. of organic priority pollutants and the effluent leveloforganic priority pollutants was less than 0.01 mg/l. This data will be provided to EPA as an addendum to the Part 'B' Application after receipt from the EPA Effluent Guidelines Division. -1 TABLE U-8 WASTEWATER/SLUDGE ANALYSIS RESULTS BASIN ZO B (f1) Sample # #1 #2 #3 #4 #5 #6 #7 Avg. Parameter Tetraehloroethylec e (F 02) <0.200 <0.100 <0.100 <0.100 <0.100 <0.100 <0.1.00 <0.100 <0.100 <0.100 <0.200 <0.200 <0.125 ' 'r ohloroe hylene (FO02) <0.200 <0.100 <0.100 <0.100 <0.100 <0.100 <0.100 <0-.100 <0.100 <0.1.00 <0.200 <0.200 <0.125 Ohloroben e e (F002) <0.200 0.:70 <0.1.00 <0.100 <0.100 <0.1000.150 0.160 0.200 0.110 <0.200 <0.200 <0.166 'toluene (F005) 2.900 2.400 0.170 0.230 0.460 0.300 3,000 3.000 2.900 1.900 0.400 0.820 1.540 Methyl Ethyl Ketone (F005) <0.401 <0.200 <0.200 <0.200 <0.200 <0.200 <0.200 <0..200 0.210 <0.200 <0.400 <0.400 <0.251 ODCB (FO02) 0.550 27.000 3.300 6.800 2.900 43.000 9.600 20.000 8.900 27.000 2.700 3.500 12.940 Pyridine (F005) <0.100 1.500 <0.200 <0.200 <0.200 <0.20 <0.200 0.360 <0.200 <0.200 <0.200 <0.200 <0.313 TABLE C-9 WASTEWATER EFFLUENT RESULTS BASIN 202E (mg/1) Parameter Toluene Chlorcben ene 0-dichloroben ene No. Date 1 10/23/79 2.17 0.01 -- 2 12/17/79 8.80 0.30 1.82 3 1/14/80 19.61 0.11. 4.77 4 2/7/80 15.33 .4 5 3/10/80 9.68 0.06 3.30 6 4/16/80 3.20 0.22 9.62 7 5/27/80 5.2 0.05 0.78 8 6/25/80 4.70 0.02 1.14 9 /23/80 8.09 0.01 1.28 10 9/25/80 2.00 0.10 0.45 11 12/14/80 7.35 0.04 6.14 12 2/10/81 8.75 0.33 4.37 13 3/18/81 1.75 0.35 2.41 4 4/27/81 1.59 0.10 2.1' Average 7.05 0.08 3.22 C'-2 fi SECTION p PROCESS INFORMATION The information provided in this section is submitted in accordance with the requirements of. 40 CFR Part 270.15 and 270.16. Other regulations addressed to complete this section include 44 CFR § 264.1.7, § 264.175, §'274.176, § 264..177, § 264.191, § 264.192, and § 264.198. This section discusses specific process information for the storage of containers and tanks and the surface impoundments. Sod eco has two container storage ;sites and one storage tank at s third location. The waste container storage area, and tank storage area designs and specifications were all certified by a registered professional engineer. I. Containers,40 CFI. 27t1.15 Sodyeco's two container storage areas are located at Building 33 and inside Building 42. The total drum storage capacity at the two sites is 176 drums, however, inventory at the facility will normally be 100 drums or :less. Hazardous wastes are generally stored only long enough to accumulate a truckload for shipment to are EPA approves disposal facility. a. Building 33 Store e reap Hazardous waste materials steered at Building 33 are generatedwithin that building and consist of two types of waste. One waste is a still bottom tar that results from the distillation of o-- i hlorobenzene ( C{12) which carries a toxicity hazard. The other wasteis an aqueous still residue resulting from distillation of methanol (FO03). although D- this waste is listed as ignitable, repeated tests have shown it to have a flash point above 60*C. Present inventory consists of 16 drums of the F003 waste. .After the waste materials are drummed, they are labeled as to their content's in conformance with 40 C p 262.32(b). 'These two waste mater- ials are compatible and are stored together can. a 40-foot truck trailer located at the south dock. of Building 3 (See Figure D-l). Drums are manually placed on the trailer one drum high. This area is away from any sources of ignition and is inspected regularly (See Section F 2). The area surrounding and under the trailer is sloped to drain to an acid suer. The waste materials stored in this location can be treated in Sodyeco's wastewater treatment system if a spill should occur. When the trailer is full, it is transported to the Building 42'area. The drums are manually moved from the trailer onto another truck trailer for shipment to a disposal facility. b. Building 42 Storage Area: Presently stored at this site are 17 drams containing dinirtrochloroben ene and rust (DO03). This storage site could receive for storage in the future other miscellaneous hazardous wasted arising --rimarily from dis- carding of off -specification products, production hazardous wastes, and clean. -cep materials. The container storage consists of a curbed 20' x 23' concrete area within Building 42 shown it Figure D-2. Figures -3 and -4 show the containment and sump design. The entrance to the containment area is - . 'Tank [40 C k 270 - I I I a. Description of Tank: 100,000-gallon concrete tank is located adjacent to one another north- west of guiding 45. This tank has been used for storage: of hazardous wastes from Building 45 generated during the manufacture of a product which is no longer produced. The 1 0,000-gallon tank is of concrete construction and was farmed in place. The dimensions of the tank and construction specifications are spawn in Figure -. The tank is covered by a fiberglass pitched roof with a slope of 8.9%. The wooden frame of the roof is supported by the 40-foot sides of the tank, with approximately a 2-foot clearance in the middle of each. -foot side. Approximately 3 feet of the tank is exposed above ground level with the remainder below ground. . Tank Corrosion and Erosion: The concrete tank is constructed of materials that are resistant to cor- rosion and erosion by the wastes stored in; them. The tang is inspected according to the schedule in Section F for evidence of corrosion, d Tank Nianaement practices The campaign that generated the wastes stored in the tank has been com- pleted and no more of: these wastes are expected to be generated. The concrete tank has been pumped out with the wastes going to a hazardous waste landfill. This tank may be used in the future for storage of some new production wastes classified as hazardous. D--d- The waste stored in the concrete storage tank was a liquid production waste (FO05), and also contained some of a tar material that doses not flow at ambient temperatures. The wastes were pumped directly into the tank from the top through a fixed piping system in a batch operation. Tank levels are measured before ;pumping operations to ensure adequate space exists. The pumping operation is manually controlled. At lust one foot of freeboard is maintained. 3. Process Information ® Surface m ourdment Sodyeco's hazardous caste surface impoundments are used as stowage, treatment, and disposal units in the NPDE S Wastewater Treatment Facility. Figure D-µ6 (p. it-14) shows"a schematic of the wastewater flow through the various impoundments and tanks of the wastewater treatment system. Figures --1 and -2 show plan views of the facility. . akgroiund. The wastewater treatment facility was first constructed in 1966 as a neutralization and aeration facility. The activated :sludge system was added in 1973 and became operational in 1974. A number of modifications and additions have been made to the facility over the years to improve treatment and to expand sledge disposal impoundments. Spill control and pretreatment projects have significantly reduced production losses into the surface impoundments. These projects have included additional tank dikes, concrete loading/unloading areas, railcar loading/unloading catchment, phenol pretreatment and similar projects.- b. Present Operation: Acid wastes having the characteristic of corosivity are collected in a separate sewer system and discharged into impoundment Z01 for temporary storage. Z01 can overflow through a pipe into Z 5@ Wastewater is pumped -1 from either Z1 or Z08 to the acid neutralization concrete tank. Typic- ally, the acid is neutralized initially to a phi of approximately 3 with a powdered CaO/CaCO3 material or with powdered CaCO3- Ca(OH)2 slurry is then added to bring the wastewater to a roughly neutral p8. Both feed systems work independently off of two: separate pit controllers. In this way the Ca(OH)2 slurry can be used alone for neutralization or can act as a safety backup for the powdered lute system. After this treatment, the wastewater no longer has the corrosive characteristic. The neutralized acid stream carrying gypsum solids resulting from the neutralization of sulfuric acid flows through a canal in the eastern edge of Z 2A into the northeast corner of Z02E. Except for the canal, Z02A is full with acid neutralization solids accumulated in years past. Z028, which was constructed in 1972, acts as a settling and equalization basin. Non-acid wastewater is collected in a separate serer system called the alkaline sewer. It flaws into a`pump station and is pumped to the south- west corner of Z 2E. If the pH of the alkaline sewer should become acid, the flow is automatically diverted to<Z08.< Impoundment Z 3 acts as a storm surge basin for the alkaline suer. In Z 28 the alkaline stream mixes with the neutralized acid stream. Most solids in the alkaline stream settle out with the gypsum. Waste activated sludge is discharged into the final alkaline sewer junction box and is pumped with the alka- line stream ;out to Z02E. fixers near the discharge of Z02E help produce an equalized waste stream for the biological system. Z02C was completed in 1980 to dispose of gypsum sludge that was filling Z 2B. Z02C was but in service on .January 25, 1983. A Mudcat hydraulic i 1 l dredge is used to transfer sludge material from Z02 - to Z02C. Superna- tant can then flow back into Z02 . A fixed pump station with two 3 MGD pumps will be added to Z02B in 1984 to pump wastewater from Z02B to Z02C for temporary storage. A controlled release facility will also be com- pleted in 1984 which will allow treated effluent to be pulped to Z02C for storage at a design rate of 4 MGD. This material will then flow back through the treatment system prior to discharge. The equalized wastewater in Z02B flows by gravity through a 20-inch diameter pipe to Z03. Z03 with 12 floating aerators, acts as a preaera- tion facility from April to September and as the first stage in the acti- vated sludge process from September to April. The wastewater then flaws freers Z03 into ZC . " 4, with S fined mechanical aerators, is the primary biological system, utilizing the extended aeration complete mix activated sludge process. The biological mixed liquor flows by gravity through a splitter box into either or both of two 80-foot circular concrete clari- fiers. Sludge underfl.ow is recycled to Z04 and/or Z03, or is disposed via the alkaline pump station to Z02B. Effluent leaving the clarifiers passes through a baffled concrete tank called the contact basin. This basin was originally built for chlorine addition and contact; however, there is no need to add chlorine to the effluent. ;from the contact basin the effluent flows into Z30, the first of two final settling ponds. Very few solids, however, are left in the effluent at this time, to settle out. After leaving this polishing pond., the effluent mixes with the non -hazardous backwash water :from our process and potable water treatment facility. The combined effluent then flows -12 through a narrow earthern canal into Z32, the final settling pond for settling pond for polishing. Bath Z30 and Z32 are periodically dredged out with the Mud at dredge and the solids pumped into Z02B or Z02 « Two floating aerators in the discharge sale of Z32 ensure sufficient dissolved oxygen is present for =discharge 'to the. river. Caustic and acid can be added at this paint for emergency pH adjustment. A controlled release facility is; planned for part of Z32, downstream from the aerators. This facility will consist of three 2 MGD pumps and a mechanism for controlling effluent discharge flow to a pre -determined amount. Excess incoming flow will be pumped to Z02C for temporary storage. This controlled release facility is specified in a new NP ES permit to limit BOO-NH3 discharge during periods of very low riven flow. This plaint at the end of Z32 is the final sampling point for NPDES permit compliance. Hazardous wastesentering the surface impoundments are discussed in; Section C. All impoundments were existing and in use prior to January 26, 1983, and, therefore, are exempt from the liner requirement. More information is contained in Section K. D-13 TABLE APPENDIX VIII CONSTITUENTS USED/SUSPECTED AT SG Y CO INC GROUP A - High to Moderate Use Raw Materials or Products Aniline phenylamine Formaldehyde p-Nitroaniline Phenyl nedi mine;(raw material and product) Toluene Dian ine Acrylonitrile Chlorobenzene o-Dichloroben ene 2 4- initrophenol (product) Phenol GROUP R Moderate to how Use Raw Materials or Materials Used in the Past: Acetophenone Chloroacetaldehyde l(o h orophenyl)thioarea (intermediate) Cresols Formic Acid; Malononitrile Methyl Ethyl Ketone Paraldehyde Pyridine Thiourea imethyl Sulfate Phthalic Anhydride Penid.ne Chromium N.O.S. (cooling tower water treatment) pichlorobcnene Hexachloroben en Naphthalene Nitrobenzene Sodium `Cyanide Toluene 12,4Trichorobenene ll,l-Trichloroethan GROUP Haw Materials Used in the Past in Ver- Low Quantities: enyl Chloride Dinitroben ene N.O.S. Ethylene Oxide Arsenic N.O.S. Cadmium N.O.S. GROUP D - o ands Known or EvInected as iE-E tt t atdrial urities or Products of Reactions in the Sewer or Treat ent ste : p en oquinnne -Chloroan line -Chlrcphdnc Hydrogen Sulfide ethanethio (primarily air emission if formed) ` oluidine Hydrochloride Benzene - ichloroben ene ,4-Di ethylphenol 4-Nit ophencl Nitric Oxide (air emission if formed) Nitrogen Dioxide (air emission if formed)` n-Nitrescdiphenylamine n-Nitrosn -n-° ropy ine o-Toluidine hydrochloride, b Chloroform Cresols ichldromethane Dead Acetate Methyl Methacrylate A waste material from anthracene extraction was purchased by Scdyeco as'a carba o e ram material. This material may have contained impurities of rather polycycl.ic compounds. Priority pollutants in Groups E, F, and G. --14 GROUP E (Continued) Nitrobenzene Pyridine Silver, N.G.S. Tetrachloroethyl ne Tetrachloropmethane Toluene Acetonitril. Acetyl Chloride Acrolein Allyl Alcohol Barium Benzene Eenzenthio. Sia(2-Chloroethyl)ether Eia(chloromethylethe Brucin 2--aee-butyl-4,6- init o henol Carbon Disulfide Chloral. Chlorinated Ethane, N.O.S.° 1 Chlo o 2, -epox ro ane Chloromethane Chloroemthyl methyl ether 2'-Chlo ophenol Cyanides, N.O.S. 1i,2-dibromoethane 3,3'°-di.chloobenzidine 1, 2-dichloroethane Trans-1, 2-dichl.oroethylend 3,3'di.methbybenzidine 3.3'-dimethylbenzidine Dimeth lcarbamoyl. chloride 2,dimethylphen►l , -dinitro o-cresol 1,4-dio ane thyleeimine thylethacylate Fluorine Fluoroacetic, acid, sodium "salt 1ydroEen cyanide Hydrofluoric acid Iodomethane' l obut l alcohol Lead acetate tethanethi,ol 4. '-methyl nebis(2 chloroeniline Priority pollutants in Groups E, F, and G. E-15 OUP G (Continued) l-t aph hylamina 2 Naph hyla i.na Nickel, N.O.S. 5-nit d-o-toluidina Pentac alorophanol NPhanylthioura' Phosgene Phosphlina 2-Picolina Potassium Cyanide I,Propanesultana N-Propylamine Resorcinol Sodium Cyanide Tctrachlorobanasac Tatrachloroethaua Thioacatamida Thiosaicararide Tolylena diisocyanata 'richloroathylan 2, ,6-trichloropaanol Tris (2,, -dibrmopropy.)phophate Vanadium Pantaa Zinc Cyanide control) )phthalate (plastic products) to control) rocarbons,,N.O.S. (refrigeration) nS) one pules pilings) r� R k #k (stainlesseak . 1 kers, I 1 atraethyl?lead (gasoline) � Priority pollutants in Groups E, F, RM in past years) ) ontol) foam insulation) and soaps) gauges; losses to the sewer may and G. TABLE R--7 PART E - GROUNDWATER MONITORING AND PROTECTION OUTLI » I.dentificetinn of.: e :'iflCf t. %T-A Y-A9.... 1 4 -,-I I- T- .- -„ w,+,--4.-A uifer under f°enilit inch, Water flow rate and dire Bases for identificetior 2. TO re hic a €a Location of aquifers � Delineation of nlu Lin ction s inetion nt °- Concentrationsthroughout plume - Maximum concentration in plume :ailed Plans and an Engineering' Re ort of Groundwater xitorin arora Description of wells - Number of wells - Locations - Depths Assurance of unaffected background water measurement Casing description o Description of sampling/analysis procedures Sample e collection methods Sample preservation/shipment Analytical procedures - Chaim of custody control o Documentation of proper/adequate analytical procedures o Procedure for determination of groundwater elevation with each sample -1 b» lisle S ace i uirements 4C FR 264.3 Aisle space requirements are addressed in Sections D and G. 4. Preventive Proc270.14(b)(8)] a. Los""! /Unloadin erdti on 40 CFR 270.14(b)(8)i a Drum filling is normally accomplishedin the processing areas. The still residues generated in Building 33 are piped directly from the still into drugs. The drums are manually leaded onto the trailer located at the building dock. Any spills occurring during this operation would either be contained and re drummed', or could flow' into the wastewater itreatment system and he treated. Drums stored at Building 42 can come from a number of sources.' Off - specification products or production wastes will normally be drummed within the processing area and transported to Building 42 by forklift. Most of these wastes are solid at ambient temperature and spillage would be contained. Liquid spills within process areas would go to the serer system. A spill in the storage area would be contained within the curb. Some materials in this area could be the result of cleanup of spills within the plant area. These materials world either be pumped or shov- eled into drums by personnel properly; equipped for safety;. Waste stored in the concrete tang is piped directly from the processing area to the storage tank Unloading operations at the container storage areas generally involve moving of drums from storage onto a true for transportation to a disposal facility. In the case of the storage at Building 33 the storage trailer P2 is moved to an open area near Building 42 situated back-to-back with a second trailer, and drums manually moved to the second trailer for trans- porting to the disposal facility. The drums in storage in Building 42 are generally loaded onto a truck which is backed up to the edge of the cubed storage area at the door of the building. Unloading of the storage tank involves pumping of wastes to a tank truck or to drums for transportation to storage or disposal. facilities. The tanker loading area at the concrete tank is curbed to contain any small spillage. . Runoff O CF'R 270. 4(b)(S)jii Runoff from ;Building 33 storage flows; into the plant sewer system and is treated by the wastewater treatment plant which is designed to handle these stored waste materials. Storage at Building 42 is diked: and is located within the building, effectively eliminating runoff from this site. . titer u lies 4iC CF°R 270.'l4(b)i8(il.il c Groundwater movement in the area is toward the Catawba River and for Creek, both of which act as discontinuities. The wastewater treatment plant treats the facility wastewater prior to discharge into t Catawba River. Provisions to minimize the passibility of hazardous waste contain- ination of ground or surface wager have been covered by F.4.(a) and F4.(b), and in the Groundwater Protectiori, Section C. F21 S'odyeco is a manufacturer of sulfur dyes, disperse dyes, and miscellaneous organic chemicals. list of emergency eoordi aZors is included in the plan. Hazardous Waste Lana ment activities odyeco's wastewater treatment plant surface impoundments are classified as part of the hazardous waste management facility and are subject to RCRA regu- lations. The acid wastewater prior to neutralization exhibits the, character- istic of corrosivity:because of its low p,. Otherwise, the wastewater (and sludge generated from it) is classified as hazardous waste because it contains trace quantities of solvents and sulfide, and could include a small quantity of several listed wastes. Sodyeco stores hazardous wastes in the following locations: . Pildirs 33t' drum 'storage trailer located at Building 33 loading dock is used to store distillation still residues from the distillation of o-dichloto benzene and methanol. The o dichloroben ene still residue is a listed hazardous waste with the EPA Hazardous Waste No. F002 toxicity hazard. The material is a non flowing tar at ambient temperature. When heated to above 5 C it becomes a viscous fluid. The methanol distillation residue is a listed hazardous caste with the EPA Hazardous Waste No. F003. EPA lists this waste with a hazard'of irritability, although repeated tuts have shown this material has a flash point of 0* . This material is an aqueous liquid. These two *pastes are compatible. G b. Buildin 2 Area: A drum storage area in the northeast cornet of Building 42 stores various solid and liquid wastes. The wastes stored in this area may be corrosive 2 , reactive DO 3 , or occasionally ignitable DO01 Spill clean-up residues from listed hazardous chemicals are occasionally stored. Off - specification commercial chemicals are also occasionally stored in this area. All materials are checked for compatibility with the other stored' wastes. This area, stores approximately 96 drums. a. Buildi� o hazardous waste storage tanks are located at Building 45. A 10 ,000- gallon concrete tank previously held an ignitable aqueous waste and a F0 5 still bottom tar with both ignitable and toxicity hazards. A , 00 - gallon metal tank presently stares the still bottom material. The pro- duction campaign that produced these wastes has been completed. The 1 0,t)00--gallon tang was emptied in August 1982 with the material being sent to an EPA approved disposal facility. Closure plane are presently being made for the 5,000-g llon tank, to have it removed during 1983. Figure -1 is a'facility map showing locations of buildings, hazardous waste storage areas, and raw material tank farms. Amer enc oordinator A special "restricted use"` telephone is located in the boiler room and 'guard° house. The number is 228. In the event of a fire or other emergency at odyeco, the discoverer will simply dial the number 228`to obtain help and notify other pliant personnel of the situation. 3 le .11 Owe I..eam diti b y cs C71- 9 a > 0 3 i O, 0 n a 9 f• .Scatt 300, &$#* a Pend, C**,-/ A; HWS }lfia: P"dwcrt Xo✓w of K.': + )ermines is authoried'to-discharge from outfall(s) aerial number(s.;001. .such discharges shall be limited and monitored by the permittee as specified below: Effluent Characteristics Discharge Limitations Monitcrin Kg/day (lbs%d y) Other Units (Specify) ***Measurement ** Daily Avg. Daily Max. Daily Avg. Daily Max. Frequency i'"()w 3.9 MGD Daily ly Cori 1301) + . (Nil3-N) {l} (2 67) (8,001) Daily Corr 1301) + . (Nll3--N) W (4749) (14,247) Gaily Carr TSS 443(97 ) 1, 29(2,92 ) Daily Corr Phenol 0.8(1.8) 1.6(3.6) MonthIy Gra Fecal Crolx form 1000f 100 ml 2( 00/'100 ml Monthly Gra Temperature Daily Gra Dissolved Oxygen (minimum) 5 mg/1 Daly Gra COD Weekly Cons Total Residue Weekly Corn, Settleable Matter Daily Gra *Saniple %ocationr : 1 - Influent, B- Effluent, U _. Upstream, D - Downstream **All Stream samples shall be;grab samples. ***Daily means eNcry day on which a discharge occurs except Saturday, Sunday, and legal holidays. Ida; may be reduced at each sampling station to one tame per week except dt,ring the months of June, July, a when the frequency must be no less than three (3) times per week at er(ci sampling station, NORTH CAROL11NA ENVIRONMENTAL MANAG,MUN" (" OMM I Si I ON' COUNFY OF MECKLENBURG IN THE MATTER OF NORTH CAROL INA NPDES PEW11T NO. SPECIAL ORDER NC 0004375, HELD BY CONSENT BY MARTIN MARIETTA CORPORATION EMC WQ 83-05 SODYECO DIVISION Pursuant to provisions of North Carolina General Statute 143-21i WJ 1XV I kA I %,Gf V I I I t(l UUI It: 1 0 1 .>LQ LULC I It,) D—LOe , dfm rier-edi the Commission: 1. Sodyeco and the Commission hereby stipulate the follo� (a) That Sodyeco holds North Carolina NPDES Permit N( for making an outlet to the Catawba River, waterx- (b) That Sodyeco is unable to comply with the final i and monitoring requirements of the Permit, wittyt and properly operating additional wastewater trei IfW/ UUWV�Z; EUULIIIV UV pollution of waters of this State named above; (d) That Sodyeco is within the jurisdiction of the Commission & set forth in Chapter 143, Article 21 of the North Carolina General Statutes; (e) That Sodyeco hereby waives its right to a hearing on the to of this Special Order by Consent pursuant to procedural reqi me is of North Carolina General Statute 143-215.4 and Commi! rules in 15 NCAC 21, and also hereby waives its right to api this Special Order by Consent in accordance with North Caro' General Statute 143-215.5. 2. Sodyeco, desiring to comply with conditions of the Permit identil in paragraph l(b) above, does hereby agree to do and perform all the following things: (a) Comply with all conditions of the Permit except those ident- in paragraph l(b) above); b t1por execution of' tiff activities in ;tcc. rryd 1 ) Submit. plans, s to Construct ad existing fac li' effluent l im to three months of (2) Begin construct within one mcnt (3) Couplets constr within mine ron' (4) Comply with the requirements wi i G r nd—rtake the fol low1n :h the indicated time sct iitions and request for An (1) Summer: April 1 - Octo (2) Winter: November 1 SEE A`CTACHM ...1.,_1 —1 . we,_.- _..._..__ _.. rf` this Order. osed facilities ber 31 March 31 ENT &.U.NIZ�t®, tt%a U yd 4✓C64✓ t1IL,„ti4 t0.AGR(tski ttex{ 41I4. 4/1 i.. 4.:1R4 - isatrwR:.+ v dates or times for accomplishment of listed activities r affected. 3 Any violation of terms of this Special Order by Consent, inc' failure to achieve interim effluent limitations set forth at 2() above, sublet Sodyeco to enforcement authority of the I and of the Director pursuant to North Carolina General Statu' and Commission rubes in 15 NCAC 2J. 4. This Special Order by Consent shall expire on August 1, 1984 Entered into this the day of MARTIN MARIETTA CORPORATION By: 1983 "FrI actin�retl oarlrrsitin N th C mental' Management Commission 3y _ _ _ 1983 Chairman of the Commission 'low 3.9MGD Da OD 5 + 54 (NH3-N) (1) (800) (1,600) Da Q5+ 31 ( -) () (6,225) (12,500) Da _SS 443(976) 1 329(2,92) D 1h nols (1 (5) (1 ) M (2) (15) (30) Mrs e a1 Coliform 1000/100 ml 2 00/100 ml M Vie! perature * * D )i solved Oxygen (Minimum) 5' mg/l D e otal Residue We >e tleable Matter Da <Slmple Locations: I -Influent, 6-.Effluent, U-Upstream, D-Downstream **All'stream sari —Daily means every day on which a discharge occurs except Saturday, Sunday, and legal hn saki be reduced at each amplincg station to one time per week except during the months of JU Then the frequency must be no less than three (3)' times per week at each sampling station. K'1**Tk_ +n.M,nr wn#iav+n rah -$•fix ."<'-CCCi ,;M#- ,. G.wi g# k L 3. C. .a A. .*� »'Te µ9. .k. �.__m._m. s....:�.. y Ds C( y C1 y C1 hly G hly G1 hly G y G" G1 1 dls .#,. ...o +.+ asr ✓sauc a vv:, .auvFa u+tcx ar tt,a rrr # E t#Ci tr 4. i.8 L(J G` #d 4Gtll�d#G#. t.{#:G &#6 4111U #:Gk+#Y:## above ambient stream water temperature.` t***BOD5 only on upstream and downstream samples. The PH shall not be less than 6.0 standard -unitnor greater than 9. ,tAndArd ijnit� sosite.... i,t u,u sosit :**** I,S U,D sosite I,C s F,UD s S,UD s S,UD stream sampling t, and September" team of more than