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HomeMy WebLinkAboutNC0004839_Wasteload Allocation_19910520NPDES DOCYHEOIT $CANNINO COVER SHEET NC0004839 NPDES Permit: Document Type: Permit Issuance Wasteload Allocation,,.) Authorization to Construct (AtC) Permit Modification Speculative Limits Correspondence Instream Assessment (67B) Environmental Assessment (EA) Permit History Document Date: May 20, 1991 Mist document printed on reuse paper - ignore any content on the reirerse wide NPDES WASTE LOAD ALLOCATION PERMIT Na: NC0004839 — — Oa2- PERMI ITTEE NAME: Exxon Company, U. S. A. / Charlotte Facility Status: Existing Permit Status: Renewal Major Minor Pipe No.: 002 Design Capacity: 0.0288 MGD Domestic (% of Flow): 0 % Industrial (% of Flow): 100 % Comments: Permit was put on hold to include groundwater remediation. Outfall 001 has been received (WLA done by Betsy Johnson) See attached information on wastewater. RECEIVING STREAM: Class: C an unnamed tributary to Long Creek Sub -Basin: 03-08-34 Reference USGS Quad: F 15 SW (please attach) County: Mecklenburg Regional Office: Mooresville Regional Office Previous Exp. Date: 5/31/90 Treatment Plant Class: Classification changes within three miles: none LOTTED Requested by: Rosanne Barona Prepared by: Reviewed by: f ' u/t'& s4Li v - -1O t u t\M w 3/21/91 Date: Date: Date: Modeler Date Rec. # xKA 317:2-15 t 6 I d- s DrainageSAArea (m. ) G t; Avg. Streamflow (cfs): 0 7Q10 (cfs) p Winter 7Q10 (cfs) 30Q2 (cfs) t� Toxicity Limits: IWC 91 % Acut Instream Monitoring: Parameters Upstream Location Downstream Location Recommended Limits ** Wasteflow (MGD): Oil & Grease (mg/1): pH (SU): Benzene (ug/1) : Toluene (ug/1) : l'Ethylbenzene (ug/1): $ m/p-Xylene (ug/1) • TIE FAuLITI PA µoNIToP- o-Xylene (ug/1):j-NIS As TOTAL MENE Isopropyl ether (ug/1): MTBE (ug/1): Naphthalene (ug/1): 2-Methylnaphthalene (ug/1): Monthly Average Summer/Winter 0.0288 30 Toxicity: Chronic Q P/F at 99% Daily Maximum , 60 6-9 71.4 11 325 MONITOR MONITOR MONITOR MONITOR MONITOR MONITOR 7y6,-,E con•{ouNPS (8rAuwvlG, Tout 6, eiitiLsE.vzErrei ) /LE StiOLCLD ee Atom-roI Lila. of 2 PPS S. D 1151N4 AN EPA} vvr r4 p To 4 VM ,log 11110 OILY fi,104.9 grlo- V QTRL.1 qUILY Void Comments: OR4ANIcs r1temit n,afaJ . StfvuL.?) culucIDE & i3I Wk,c-G E,r-k-ai 'T i iCtiy 7 f//i . fl iz ic=--'V 'L cc,Au5e .SNvua1? 66 fLACEO 1 v 711E ItewstIT Yv ALLGW 4OPi770NAL L4/1117ry ON Tilb56 02V1W IZ Togcem'TS S/la[GA 7n1� F4C,1-ITY (Arc /rs WiloL& £`Ft.uaT 70$(fTY 7EsTS. Rrcc;Mu,Fivp con►Trnluuu-5 Gte. }- 41vN1-ea4A-f4 P.O. BOX 4415«-HOUSTON, TEXAS MARKETING DEPARTMENT REAL ESTATE & ENGINEERING ENVIRONMENTAL ENGINEERING P. B. SNYDER ENGINEER aYV. 041.. 77210-4415 Mr. M. Dale 0vercash, P.E. Supervisor, NPDES Permits Division of Environmental Management 512 North Salisbury Street Raleigh, North Carolina 27611-7687 Dear Mr. Over ash: January 2, 1990 NPDES Permit Renewal Permit No. NC0004839 Exxon Terminal, Charlott,b, N.C. .)AN u 1891 p.'Rh1CfC �, it:� i•'•i; ��::^ As indicated In my December 4, 1990, letter to you, the following information is being provided in response to your letter of November 5, 1990. 1) Laboratory analysis* indicates the following petroleum constituent concentrations in the local groundwater; Benzene 4400 ug/1 Toluene 13000 ug/1 Ethylbenzene 4200 ug/l M/P-Xylene 6300 ug/1 O-Xylene 5900 ug/1 Isopropyl Ether 1728 ug/1 MTBE 11 ug/1 Naphthalene 710 ug/1 2-Methylnaphthalene 690 ug/1 * Please note that the above concentrations reflect the maximum concentrations found in groundwater at or adjacent to the Exxon facility, and should be considered only a "worse case" scenario. 2) The proposed groundwater treatment system consists of an oil/water seperlator, packed column stripping tower, and effluent weir. The estimated flow through the treatment system is 20 gallons per A DIVISION OF EXXON CORPORATION Mr. M. Dale 0vercash -2- January 2, 1990 minute. The preliminary design assumes a removal efficiency of 95 percent for the aromatics benzene, ethylbenzene, toluene, and xyle es. A removal efficiency of 75 percent is assumed for the more soluile compounds, isopropyl ether, MTBE, naphthalene and 2-methylnaphthalene. After treatment, the water will be discharged from outfall 002, located adjacent to outfall 001. The attached diag am represents the proposed system. 3) Give h the previously described removal efficiencies, the following petroleum constituent concentrations may be expected in the outfall 002 ischarge; Benzene 220 ug/1 Toluene 650 ug/1 Ethylbenzene 210 ug/1 M/P Xylene 315 ug/1 0-Xylene 295 ug/1 Lsopropyl Ether 432 ug/1 MTBE 3 ug/1 Naphthalene 178 ug/1 2-methylnaphthalene 173 ug/1 4) Wastewater Flow Diagram: Facility Stormwater Drains Pumped Groundwater, 0rl/Water Separator 0il/Water Separator Air ,Stripper 0utfall 001 Outfall 002 , 5) 0utf11 002 will discharge into the same stream as outfall 001. The discharge point will be in the same area as the existing discharge, and both outfalls may be sampled individually. Attached, please find a topographic map of the area, indicating the location of outfalls 001 and 002. Should you ne d additional information on this project before a renewed NPDES permit can be completed, please contact me at (713) 656-9219. Si ncerely, -rad -n -A-74/4- PBS 4352D Attachments OVERNIGHT OFF -GAS (TO TREATMENT IF REQUIRED) t t AIR SUPPLEMENTAL ie LIFT PUMP* Su.% p 061- ��I I ecv.tor ! 4110.11 >0 • 411.111.1 GROUND WATER RECOVERY WELL PACKED COLUMN STRIPPING TOWER WATER o) III -II AIR BLOWER • SUPPLEMENTAL LIFT PUMP MAY BE REQUIRED, DEPENDING OH HEIGHT OF TOWER. u EFFLUENT WEIR (FLOW MEASUREMENT AHD EFFLUENT SAMPLING) OUT FRILL ooz 11134 ER ENGINEERING, SCIENCE. AND TECHNOLOGY, INC. DRAWN JKS DATE 7/12/90 REVIEWED AMH DRAWING NO. TREAT 1 FIGURE 4. DISSOLVED CONSTITUENT REMEDIATION SYSTEM AT EXXON BULK DISTRIBUTION TERMINAL/ 6800 FREEDOM DRIVE CHARLOTTE, NORTH CAROLINA 90% R.E. • K.a Co rasa ,/c /4"1/41 9u; E=ALt.._ . 0o ( / r 1on1l G2p,�) ��� > :fit{;" _ 0� 0 aa8 LIT • • loth CAC' 0• • 0 04 �oaot 7q(� _ v T. Way 7r o- f .T4rr {b2T 1/ 10, 0 7 Ott( tl itisAd refs of Q cy EXxotJ NA.P /1 Pe17M rr 47 oUTf;4CC COI row ,21JAJcFF •▪ , Of O0_2 (s foie c -f4o 12 /74tD(A7/v4 s i7"1-1 �T r° Srr1D2Aia7 M{1K. D�>�V� conic. 644 } (L)' . Pr. 1 ILK- T�TMI'r 1 M 1 A PPI.I Gp 1. �ucNe i .Cfh.6et1t&t tAh - ?0,1L /i-XYL 7- 1.50t'4?PYc. j-e. (J et rs-1A t._d 1, 2-NerHY4-0 CO , ot. ;6744..e OIL 1 71, 4 (H) I 1 325" 4400 13�0 4zoo 63e)0 6°[00 172-5 440 130o 420 625o 5S50 '71, 4 J I 325 r iv.../4i orZ — 43 z ncoalrorz M9wlroe . p...11 i o 2 nAoplio2 — 1 1 - 3_ 1 7g 173 N o ,_ _ I 0 6`t0 o�D �u�� S A2 /V©r �1"o�ED ��►o L Aar /�fON0444, -1- Facility Name NPDES No. Type of Waste Facility Status Permit Status Receiving Stream Stream Subbasin County Regional Office Requester Date of Request Topo Quad FACT SHEET FOR WASTELOAD ALLOCATIONS :EXXON USA/Charlotte :NC0004839 — Oo 2% :100% Industrial :Existing :Renewal :UT Long Creek Classification:C :030834 : MRO:Meck(A) {{yynrg :R. Baroh--����1a :3/21/91 :F15SW Request # 6148 /fQRES'?uRCE .. ; SECTION E AY�E�91 HEALTH ANDENVIRON;,.ENT NATURAL RESOURCES Stream Characteristics: USGS # Date Drainage Area: 0.01 sq.mi. Summer 7Q10: 0.0 cfs Winter 7Q10: 0.0 cfs Average Flow: 0.0 cfs 30Q2: cfs Wasteload Allocation Summary (approach taken, correspondence with region, EPA, etc.) 1 Exxon currently has a permit (outfall 001) for a storm water discharge. Outfall 002 is a groundwater remediation project for various fuels which have contaminated the groundwater around the area. The 1990 staff report states that unleaded fuels, kerosene, No. 2 heating oil and diesel fuels I4jy are stored at Exxon. Standard operating procedures for groundwater remediation projects mill be applied. The proposed treatment is oil/water separator and an air stripper. ki Special Scheduled Requirements and additional comments from Reviewers: Recommended by: J Reviewed by I Instream Assessment: /ALL x N(r`,�Q tG)-y"- Regional Supervisor: lam, Permits & Engineering: RETURN TO TECHNICAL SERVICES BY: MAY 31 1991 Date: 5/1/fi1 Date: 6 a f�J i Date: 5-j%/�/ Date: 5Ast 1991 • 1 r -2- CONVENTIONAL PARAMETERS Existing Limits NONE FOR OUTFALL 002 Recommended Limits ** Wasteflow (MGD): Oil & Grease (mg/1): pH (SU) : Benzene * Toluene Ethylbenzene m/p Xylene o-Xylene Isopropyl ether (ug/1): MTBE (ug/1) : Naphthalene (ug/1) : 2-Methylnap thalene (ug/1): Toxicity: Chronic Q P/F at 99% Monthly Average Daily Maximum Freq Summer/Winter 0.0288 30 60 2/mon 6-9 2/mon (ug/l) : 71.4 qtrly (ug/1) : 11 qtrly (ug/1): 325 qtrly (ug/1) : TaE FAt tt,tTV MA`I £oNIToa- MONITOR qtrly (ug/1) :J AS T°TAL PILE -NE- MONITOR qtrly MONITOR qtrly MONITOR qtrly MONITOR qtrly MONITOR qtrly ORGANICS TESTING MUST COINCIDE WITH TOXICITY TESTING. Twass CaMPatNOS (RCP' S/ Toc.ur.JE) 'Einyl 8CWZEMBI j�Yttiv¢) Sccoctt D $+� 4N eP 4107HvD To Pt brT Ttonl (girt OF i (p. INSTREAM MONITORING REQUIRMENTS: NONE Upstream: Location: Donwstream: Location: hum tTo4ED uS(NCB e • using test pr 10/89 Facility Name tXX.o4 UsA Cili(L o Pcnnit t *DOD+BSc) arrFA t. t. ooZ CHRONIC TOXICITY TESTING REQUIREMENT (QRTIZLY) The effluent d ischarge shall at no time exhibit chronic toxicity in any two consecutive toxicity tests, ures 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 9% (defined as treatment two in the North Carolina procedure document). a permit holder shall perform quarterly monitoring using this procedure to establish compliance' ;le the permit condition. The. fast test will be performed after thirty days from issuance of this. permitduring the months of Amy Ai14, Noll, .Feet . Effluent sampling for this testing shall be performed at the hPD permitted final effluent discharge below all treatment rooesses. g All toxicity testing results required as part of this permit condition will be entered on the Effluent Discharge Monitoring Form (MR-1) for the month in which it was performed, using the parameter code.IGP3B. Additionally, DEM Form AT-1 (original) is to be sent to the following address: Attention: Environmental Sciences Branch North Carolina Division of Environmental Management P.O. Box 27687 Raleigh, N.C. 27611 Test data shall be complete and accurate and include all supporting chemical/physical measurements performed in. sociation with the toxicity tests, as well as all dose/response data. Total residual chlorine of the effluent toxicity,sample must be measured and reported if chlorine is employed for disinfection o;] the ,waste strewn. Should any s' le quarterly monitoring indicate a failure to meet specified limits, then monthly monitoring begin immediately until such time that a single test is passed. Upon passing, this monthly test requirement will revert to qu -terly in the months specified above. Should any test data from this rconitoring.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: Failur to achieve test conditions as specified in the cited document, such as minimum • control organism survival and appropriate environmental controls, shall constitute an invalid test and will require immediate retesting(within 30 days of initial monitoring event). Failure to submit suitable test results will constitute noncompliance with monitoring requirements. 7Q10 0.0 cfs ' Permuted Flow b, o ZZ$ i cGD. IWC% goo. o0 Basin & Sub-bsin 030834 Receiving Stream LIT L.oNe� Cstoc. County Mai-ttae.uie Rccommended.by: thm4, Dare ivvou **Chronic Toxicity (Ceriodaphnia) P/Fat 11 'Io, MAI,FfiSt See Rt _11J., Condition 4