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HomeMy WebLinkAboutNC0027626_Fact Sheet_20230606Page 1 of 7 FACT SHEET RENEWAL – NPDES PERMIT NC0027626 – WPCS Grade WW-1 [wetlands] (Reclassified from Grade WW-2 for this renewal) Table 1 - Basic Information for Permit Renewal Permit Writer/Date Joe R. Corporon, P.G. 06Jun2023 Permit Number NC0027626 Permittee North Carolina Department of Public Safety Facility Name / WWTP Class Caledonia Correctional Institution WWTP / WPCS WW-1 [downgraded from Grade WPCS -2] Facility Contacts Nainesh (Nash) Patel, PE, PEM Environmental Engineering Manager 919-324-1283 [nainesh.patel@dac.nc.gov] Basin Name/Sub-basin number Roanoke River / 03-02-08 Receiving Stream Roanoke River [Index 23-(26)] Stream Classification / IWC Class C / Winter 7Q10 = 1,000 cfs Summer 7Q10 = 1,500 cfs Does permit need Daily Max NH3 limits? Not needed. Monitor and Report only. Does permit need TRC limits/language? No. Existing Does permit have WET testing? Yes – TGE6C Acute @ 90% effluent concentration Does permit have Special Conditions? Yes. Electronic Reporting Does permit have instream monitoring? No. Is the stream impaired (on 303(d) list)? No Any obvious compliance concerns? No. During last permit cycle, fecal coliform Daily Max geometric mean exceeded on 12Jul2022 and 08Jun2021; one (1) NOV for frequency violation for MBAS. Request to discontinue Fecal monitoring denied. Any permit mods since last permit? No Current expiration date March 31, 2023 New expiration date March 31, 2028 Comments received on Draft Permit? Facility / Treatment System Narrative: North Carolina Stated Department of Public Safety (NCDPS) houses medium and minimum-security offenders. Caledonia Correctional Institution WWTP is used to treat wastewater generated by the Prison facility. Adding to domestic wastewater, the prison WWTP receives wastewater from a cannery operated by the prison. The WWTP consists of Primary lagoons, wetlands treatment, and a Chlorination/ Dechlorination disinfection system. Wetlands System – Effluent consists of 50% domestic and 50% industrial. Page 2 of 7 Receiving Stream – Discharge from said treatment works at the location specified on the attached map into the Roanoke River, HUC Code: 030101070204, Stream Index 23-(26), classified C waters in the Roanoke River Basin. Roanoke Streamflow: 7Q10w =1,000 cfs; 7Q10s = 1,500 cfs; 7Q10 Ave = 6,000 cfs [BIMS]; effluent discharge IWC = 0.052%. Compliance History / Data Review - Jan2021- Jun2023 PARAM VIOL DATE UNITS LIMIT CALC VALUE VIOL TYPE ACTION UPDATED BY 04/30/2023 Late/Missing GW-59 None bimsprod.cron 04/02/2023 Late/Missing GW-59 None bimsprod.cron 03/02/2023 Late/Missing GW-59 None bimsprod.cron 01/30/2023 Late/Missing GW-59 None bimsprod.cron 12/31/2022 Late/Missing GW-59 None bimsprod.cron 11/30/2022 Late/Missing GW-59 None bimsprod.cron 10/31/2022 Late/Missing GW-59 None bimsprod.cron 09/30/2022 Late/Missing GW-59 None bimsprod.cron 08/30/2022 Late/Missing GW-59 None bimsprod.cron 07/31/2022 Late/Missing GW-59 None bimsprod.cron Fecal 07/12/2022 #/100ml 400 816 Daily Maximum Proceed to NOV cheng.zhang 06/30/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 05/31/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 04/30/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 04/02/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 03/02/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 01/30/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 12/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 11/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 10/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 09/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum MBAS 09/30/2021 mg/l Frequency Violation Proceed to NOV alys.hannum 08/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 07/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 06/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum Fecal 06/08/2021 #/100ml 400 921 Daily Maximum Proceed to NOV alys.hannum 05/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 04/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum 04/02/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum Because Fecal coliform detected in the past year, Permittee’s request to discontinue Fecal monitoring is denied. Summary of Changes and Rationale for Renewal 1. As requested by the Permittee for renewal, down-graded the current wetlands WWTP from Class WPCS-2 to WPCS Class11, as approved on 27Apr2023 by NC Operator Certification Unit (OCU) and Raleigh Regional Office (RRO). 2. Instream Monitoring for Total Nitrogen (TN) and Total Phosphorus (TP) – relaxed monitoring from Monthly to Quarterly. 3. Lastly, we resorted your effluent monitoring table by Measurement Frequency, most- often to least-often sampled [see Table A. (1.)]. Page 3 of 7 PROPOSED SCHEDULE FOR PERMIT ISSUANCE Draft Permit to Public Notice: June 13, 2023 [Tentative] Permit Scheduled to Issue: July 24, 2023 [Tentative] Effective date September 1, 2023 NPDES DIVISION CONTACT If you have questions about any of the above information, or on the attached permit, please email Joe R. Corporon, P.G. [joe.corporon@ncdenr.gov]. NAME: DATE: 06JUN2023 NPDES Implementation of Instream Dissolved Metals Standards – Freshwater Standards The NC 2007-2015 Water Quality Standard (WQS) Triennial Review was approved by the NC Environmental Management Commission (EMC) on November 13, 2014. The US EPA subsequently approved the WQS revisions on April 6, 2016, with some exceptions. Therefore, metal limits in draft permits out to public notice after April 6, 2016 must be calculated to protect the new standards - as approved. Table 2. NC Dissolved Metals Water Quality Standards/Aquatic Life Protection Parameter Acute FW, µg/l (Dissolved) Chronic FW, µg/l (Dissolved) Acute SW, µg/l (Dissolved) Chronic SW, µg/l (Dissolved) Arsenic 340 150 69 36 Beryllium 65 6.5 --- --- Cadmium Calculation Calculation 40 8.8 Chromium III Calculation Calculation --- --- Chromium VI 16 11 1100 50 Copper Calculation Calculation 4.8 3.1 Lead Calculation Calculation 210 8.1 Nickel Calculation Calculation 74 8.2 Silver Calculation 0.06 1.9 0.1 Zinc Calculation Calculation 90 81 Table 2 Notes: 1. FW= Freshwater, SW= Saltwater 2. Calculation = Hardness dependent standard Page 4 of 7 3. Only the aquatic life standards listed above are expressed in dissolved form. Aquatic life standards for Mercury and selenium are still expressed as Total Recoverable Metals due to bioaccumulative concerns (as are all human health standards for all metals). It is still necessary to evaluate total recoverable aquatic life and human health standards listed in 15A NCAC 2B.0200 (e.g., arsenic at 10 µg/l for human health protection; cyanide at 5 µg/L and fluoride at 1.8 mg/L for aquatic life protection). Table 3. Dissolved Freshwater Standards for Hardness-Dependent Metals The Water Effects Ratio (WER) is equal to one unless determined otherwise under 15A NCAC 02B .0211 Subparagraph (11)(d) Metal NC Dissolved Standard, µg/l Cadmium, Acute WER*{1.136672-[ln hardness](0.041838)} ∙ e^{0.9151 [ln hardness]- 3.1485} Cadmium, Acute Trout waters WER*{1.136672-[ln hardness](0.041838)} ∙ e^{0.9151[ln hardness]- 3.6236} Cadmium, Chronic WER*{1.101672-[ln hardness](0.041838)} ∙ e^{0.7998[ln hardness]- 4.4451} Chromium III, Acute WER*0.316 ∙ e^{0.8190[ln hardness]+3.7256} Chromium III, Chronic WER*0.860 ∙ e^{0.8190[ln hardness]+0.6848} Copper, Acute WER*0.960 ∙ e^{0.9422[ln hardness]-1.700} Copper, Chronic WER*0.960 ∙ e^{0.8545[ln hardness]-1.702} Lead, Acute WER*{1.46203-[ln hardness](0.145712)} ∙ e^{1.273[ln hardness]-1.460} Lead, Chronic WER*{1.46203-[ln hardness](0.145712)} ∙ e^{1.273[ln hardness]-4.705} Nickel, Acute WER*0.998 ∙ e^{0.8460[ln hardness]+2.255} Nickel, Chronic WER*0.997 ∙ e^{0.8460[ln hardness]+0.0584} Silver, Acute WER*0.85 ∙ e^{1.72[ln hardness]-6.59} Silver, Chronic Not applicable Zinc, Acute WER*0.978 ∙ e^{0.8473[ln hardness]+0.884} Zinc, Chronic WER*0.986 ∙ e^{0.8473[ln hardness]+0.884} General Information on the Reasonable Potential Analysis (RPA) The RPA process itself did not change as the result of the new metals standards. However, application of the dissolved and hardness-dependent standards requires additional consideration in order to establish the numeric standard for each metal of concern of each individual discharge. The hardness-based standards require some knowledge of the effluent and instream (upstream) hardness and so must be calculated case-by-case for each discharge. Metals limits must be expressed as ‘total recoverable’ metals in accordance with 40 CFR 122.45(c). The discharge-specific standards must be converted to the equivalent total values for use in the RPA calculations. We will generally rely on default translator values developed for each metal (more on that below), but it is also possible to consider case-specific translators developed in accordance with established methodology. Page 5 of 7 RPA Permitting Guidance/WQBELs for Hardness-Dependent Metals - Freshwater The RPA is designed to predict the maximum likely effluent concentrations for each metal of concern, based on recent effluent data, and calculate the allowable effluent concentrations, based on applicable standards and the critical low-flow values for the receiving stream. If the maximum predicted value is greater than the maximum allowed value (chronic or acute), the discharge has reasonable potential to exceed the standard, which warrants a permit limit in most cases. If monitoring for a particular pollutant indicates that the pollutant is not present (i.e. consistently below detection level), then the Division may remove the monitoring requirement in the reissued permit. 1. To perform a RPA on the Freshwater hardness-dependent metals the Permit Writer compiles the following information: • Critical low flow of the receiving stream, 7Q10 (the spreadsheet automatically calculates the 1Q10 using the formula 1Q10 = 0.843 (s7Q10, cfs) 0.993 • Effluent hardness and upstream hardness, site-specific data is preferred • Permitted flow • Receiving stream classification 2. In order to establish the numeric standard for each hardness-dependent metal of concern and for each individual discharge, the Permit Writer must first determine what effluent and instream (upstream) hardness values to use in the equations. The permit writer reviews DMR’s, Effluent Pollutant Scans, and Toxicity Test results for any hardness data and contacts the Permittee to see if any additional data is available for instream hardness values, upstream of the discharge. If no hardness data is available, the permit writer may choose to do an initial evaluation using a default hardness of 25 mg/L (CaCO3 or (Ca + Mg)). Minimum and maximum limits on the hardness value used for water quality calculations are 25 mg/L and 400 mg/L, respectively. If the use of a default hardness value results in a hardness-dependent metal showing reasonable potential, the permit writer contacts the Permittee and requests 5 site-specific effluent and upstream hardness samples over a period of one week. The RPA is rerun using the new data. The overall hardness value used in the water quality calculations is calculated as follows: Combined Hardness (chronic) = (Permitted Flow, cfs *Avg. Effluent Hardness, mg/L) x (s7Q10, cfs *Avg. Upstream Hardness, mg/L) (Permitted Flow, cfs + s7Q10, cfs) The Combined Hardness for acute is the same but the calculation uses the 1Q10 flow. 3. The permit writer converts the numeric standard for each metal of concern to a total recoverable metal, using the EPA Default Partition Coefficients (DPCs) or site-specific translators, if any have been developed using federally approved methodology. 4. The numeric standard for each metal of concern is divided by the default partition coefficient (or site-specific translator) to obtain a Total Recoverable Metal at ambient conditions. In some cases, where an EPA default partition coefficient translator does not exist (ie. silver), the dissolved numeric standard for each metal of concern is divided by the EPA conversion factor to obtain a Total Recoverable Metal at ambient conditions. This method presumes that the metal is dissolved to the same extent as it was during EPA’s criteria development for metals. For more information on conversion factors see the June, 1996 EPA Translator Guidance Document. Page 6 of 7 5. The RPA spreadsheet uses a mass balance equation to determine the total allowable concentration (permit limits) for each pollutant using the following equation: Ca = (s7Q10 + Qw) (Cwqs) – (s7Q10) (Cb) Qw Where: Ca = allowable effluent concentration (µg/L or mg/L) Cwqs = NC Water Quality Standard or federal criteria (µg/L or mg/L) Cb = background concentration: assume zero for all toxicants except NH3* (µg/L or mg/L) Qw = permitted effluent flow (cfs, match s7Q10) s7Q10 = summer low flow used to protect aquatic life from chronic toxicity and human health through the consumption of water, fish, and shellfish from noncarcinogens (cfs) * Discussions are on-going with EPA on how best to address background concentrations Flows other than s7Q10 may be incorporated as applicable: 1Q10 = used in the equation to protect aquatic life from acute toxicity QA = used in the equation to protect human health through the consumption of water, fish, and shellfish from carcinogens 30Q2 = used in the equation to protect aesthetic quality 6. The permit writer enters the most recent 2-3 years of effluent data for each pollutant of concern. Data entered must have been taken within four and one-half years prior to the date of the permit application (40 CFR 122.21). The RPA spreadsheet estimates the 95th percentile upper concentration of each pollutant. The Predicted Max concentrations are compared to the Total allowable concentrations to determine if a permit limit is necessary. If the predicted max exceeds the acute or chronic Total allowable concentrations, the discharge is considered to show reasonable potential to violate the water quality standard, and a permit limit (Total allowable concentration) is included in the permit in accordance with the U.S. EPA Technical Support Document for Water Quality-Based Toxics Control published in 1991. 7. When appropriate, permit writers develop facility specific compliance schedules in accordance with the EPA Headquarters Memo dated May 10, 2007 from James Hanlon to Alexis Strauss on 40 CFR 122.47 Compliance Schedule Requirements. 8. The Total Chromium NC WQS was removed and replaced with trivalent chromium and hexavalent chromium Water Quality Standards. As a cost savings measure, total chromium data results may be used as a conservative surrogate in cases where there are no analytical results based on chromium III or VI. In these cases, the projected maximum concentration (95th %) for total chromium will be compared against water quality standards for chromium III and chromium VI. 9. Effluent hardness sampling and instream hardness sampling, upstream of the discharge, are inserted into all permits with facilities monitoring for hardness-dependent metals to ensure the accuracy of the permit limits and to build a more robust hardness dataset. 10. Hardness and flow values used in the Reasonable Potential Analysis for this permit included: Table 4 Parameter Value Comments (Data Source) Average Effluent Hardness (mg/L) [Total as, CaCO3 or (Ca+Mg)] N/A No metals monitored Average Upstream Hardness (mg/L) [Total as, CaCO3 or (Ca+Mg)] N/A 7Q10 summer (cfs) 8.9 N/A 1Q10 (cfs) ~ N/A Page 7 of 7 Permitted Flow (MGD) 0.500 N/A ROY COOPER STA1Fy" Governor ihrik,. r? 'y• MICHAEL S. REGAN 5j Secretaryieli, LINDA CULPEPPER 00'"-' Director NORTH CAROLINA Environmental Quality February 6,2019 Mr.Kenneth G.Hart Facility Engineering Specialist North Carolina Department of Public Safety 4216 Mail Service Center Raleigh,NC,27699-4216 Subject: Draft NPDES Permit NC0027626 Caledonia Correctional Institution WWTP Halifax County Grade II Biological WPCS Dear Mr.Hart: The Division has reviewed your request to renew the subject permit. Please review this draft carefully to ensure your thorough understanding of the information,conditions,and requirements it contains. The draft permit includes the following significant changes from the existing permit: eDMR requirements have been added. Regulatory citations have been added. Facility Grade has been updated and added to the permit. With this notification,the Division will solicit public comment on this draft permit by publishing a notice in newspapers having circulation in the general Halifax County area,per EPA requirements.Please provide your comments,if any,to me no later than 30 days after receiving this draft permit. Following the 30-day public comment period,the Division will review all pertinent comments and take appropriate action prior to issuing a final permit.If you have questions concerning the draft,please contact me at 919-707-3622, or via e-mail [Anjali.Orlando@ncdenr.gov]. Sincerely, 44446.7746....„ Anjali Orlando Compliance&Expedited Permitting Unit cc: NPDES Files Raleigh Regional Office State of North Carolina I Environmental Quality I Water Resources 1617 Mail Service Center I Raleigh,NC 27699-1617 919 807 6300 919-807-6389 FAX hops://deq.nc.gov/about/divisions/water-resources/water-resources-permits/wastewater-branch/npdes-wastewater-permits Permit NC0027626 STATE OF NORTH CAROLINA DEPARTMENT OF ENVIRONMENTAL QUALITY DIVISION OF WATER RESOURCES PERMIT TO DISCHARGE WASTEWATER UNDER THE NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM In compliance with the provisions of North Carolina General Statute 143-215.1,other lawful standards and regulations promulgated and adopted by the North Carolina Environmental Management Commission,and the Federal Water Pollution Control Act, as amended, North Carolina Department of Correction is hereby authorized to discharge wastewater from a facility located at the Caledonia Correctional Institution WWTP 2787 Caledonia Drive NE of Tillery Halifax County to receiving waters designated as the Roanoke River in the Roanoke River Basin in accordance with efflueni limitations, monitoring requirements, and other conditions set forth in Parts I, II, III and IV hereof. This permit shall become effective This permit and authorization to discharge shall expire at midnight on March 31,2023. _ Signed this day Linda Culpepper Director,Division of Water Resources By Authority of the Environmental Management Commission Page 1 of 6 Permit NC0027626 SUPPLEMENT TO PERMIT COVER SHEET All previous NPDES Permits issued to this facility,whether for operation or discharge,are hereby superseded and,as of this issuance,any previously issued permit describing this treatment facility or bearing this number is no longer effective.Therefore,the exclusive authority to operate and discharge from this facility arises under the permit conditions,requirements,terms,and provisions described herein. The North Carolina Department of Correction is hereby authorized to: 1. Continue to operate an existing 0.500 MGD extended aeration wastewater treatment plant consisting of the following treatment components: Influent headwork's with coarse bar screen and fine rotary screens Influent pump station Wetlands treatment system Chlorination/Dechlorination disinfection system Magnetic flow meter g 2. This facility is located at the Caledonia Correctional Institution,2787 Caledonia Drive,Tillery,NC,27887 in Halifax County. 3. Discharge from said treatment works at the location specified on the attached map into the Roanoke River, classified C waters in the Roanoke River Basin. Page 2 of 6 Permit NC0027626 Part I. A. (1.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS 15A NCAC 02B .0400 et seq., 02B .0500 et seq.] Grade II Biological Water Pollution Control System [15A NCAC 08G.0302] During the period beginning on the effective date of this permit and lasting until expiration, the Permittee is authorized to discharge from outfall 001. Such discharges shall be limited and monitored) by the Permittee as specified below: EFFLUENT - MONITORING REQUIREMENTS CHARACTERISTICS Monthly Daily Measurement Sample Type Sample Location Average Maximum Frequency 50050-Flow 0.500 MGD Continuous Recorder Influent or Effluent 50060- 2 Total Residual 28 µg/L Weekly Grab EffluentChlorine 00010-Temperature(°C) Weekly Grab Effluent C0310-BOD,5-day(20°C) 30.0 mg/L 45.0 mg/L 2/Month Composite Effluent C0530-Total Suspended 90.0 mg/L 135.0 mg/L 2/Month Composite EffluentSolids C0610-NH3 as N 2/Month Composite Effluent 00556- Oil&Grease 30.0 mg/L 60.0 mglL 2/Month Grab Effluent 31616-Fecal Coliform 200/100 ml 400/100 ml 2/Month Grab Effluent geometric mean) 38260—Surfactants(MBAS) 2/Month Composite Effluent 00400-pH Between6.0- 9.0 s.u. 2/Month Grab Effluent C0600-Total Nitrogen Monthly 'Composite Effluent NO2+NO3+TKN) C0665—Total Phosphorus Monthly Composite Effluent TGE6C- Acute Toxicity3 Quarterly Composite Effluent Footnotes: 1. The permittee shall begin submitting discharge monitoring reports electronically using the Division's eDMR application system [see A. (4.)] 2. The Division shall consider all effluent TRC values reported below 50 ug/L to be in compliance with the permit.However,the Permittee shall continue to record and submit all values reported by a North Carolina certified laboratory(including field certified),even if these values fall below 50 ug/L. 3. Acute Toxicity(fathead minnow)Pass/Fail at 90% [See A. (3.)]. There shall be no discharge of floating solids or visible foam in other than trace amounts. Page 3 of 6 Permit NC0027626 A. (3.) ACUTE TOXICITY PASS/FAIL PERMIT LIMIT(QRTRLY) 15A NCAC 02B.0200 et seq.] The permittee shall conduct acute toxicity tests on a quarterly basis using protocols defined in the North Carolina Procedure Document entitled"Pass/Fail Methodology for Determining Acute Toxicity in A Single Effluent Concentration"(Revised-July 1992 or subsequent versions).The monitoring shall be performed as a Fathead Minnow(Pimephales promelas)24-hour static test.The effluent concentration at which there may be at no time significant acute mortality is 90% (defined as treatment two in the procedure document).Effluent samples for self-monitoring purposes must be obtained during representative effluent discharge below all waste. treatment.The tests will be performed during the months of January,April,July and October. 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 TGE6C. Additionally,DWQ Form AT-2(original)is to be sent to the following address: Attention: NC DENR/DWQ/Environmental Sciences Section 1621 Mail Service Center Raleigh,North Carolina,27699-1621 Completed Aquatic Toxicity Test Forms shall be filed with the Environmental Sciences Section no later than 30 days after the end of the reporting period for which the report is made. 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 effluent toxicity sample must be measured and reported if chlorine is employed for disinfection of the waste stream. Should there be no discharge of flow from the facility during a month in which toxicity monitoring is required, the permittee will complete the information located at the top of the aquatic toxicity(AT)test form indicating the facility name,permit number,pipe number, county,and the month/year of the report with the notation of No Flow"in the comment area of the form. The report shall be submitted to the Environmental Sciences Section at the address cited above. 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 the permittee fail to monitor during a month in which-toxicity monitoring is required,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 either these monitoring requirements or tests performed by the North Carolina Division of Water Quality indicate potential impacts to the receiving stream,this permit may be re-opened and modified to include alternate monitoring requirements or limits. If the Permittee monitors any pollutant more frequently than required by this permit,the results of such monitoring shall be included in the calculation&reporting of the data submitted on the DMR&all AT Forms submitted. 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 follow-up testing to be completed no later than the last day of the month following the month of the initial monitoring. Page 4 of 6 Permit NC0027626 A. (4.) ELECTRONIC REPORTING OF DISCHARGE MONITORING REPORTS NCGS 143-215.1 (b)] Proposed federal regulations require electronic submittal of all discharge monitoring reports(DMRs)and specify that,if a state does not establish a system to receive such submittals,then permittees must submit DMRs electronically to the Environmental Protection Agency(EPA). The Division anticipates that these regulations will be adopted and is beginning implementation in late 2013. NOTE: This special condition supplements or supersedes the following sections within Part II of this permit Standard Conditions for NPDES Permits): Section B. (11.) Signatory Requirements Section D. (2.)Reporting Section D. (6.)Records Retention Section E. (5.) Monitoring Reports 1. Reporting [Supersedes Section D. (2.) and Section E. (5.)(a)], The permittee shall begin reporting discharge monitoring data electronically using the NC DWR's Electronic Discharge Monitoring Report(eDMR)internet application. Monitoring results obtained during the previous month(s)shall be summarized for each month and submitted electronically using eDMR. The eDMR system allows permitted facilities to enter monitoring data and submit DMRs electronically using the internet. Until such time that the state's eDMR application is compliant with EPA's Cross-Media Electronic Reporting Regulation(CROMERR),permittees will be required to submit all discharge monitoring data to the state electronically using eDMR and will be required to complete the eDMR submission by printing, signing,and submitting one signed original and a copy of the computer-printed eDMR to the following address: NC DENR/Division of Water Resources/Information Processing Unit ATTENTION: Central Files/eDMR 1617 Mail SerTrice Center Raleigh,NC 27699-1617 If a permitteeis unable to use the eDMR system due to a demonstrated hardship or due to the facility being physically-located in an area where less than 10 percent of the households have broadband access,then a temporary waiver from the NPDES electronic reporting requirements may be granted and discharge monitoring data may be submitted on paper DMR forms(MR 1, 1.1,2,3)or alternative forms approved by the Director. Duplicate signed copies shall be submitted to the mailing address above. Requests for temporary waivers from the NPDES electronic reporting requirements must be submitted in writing to the Division for written approval at least sixty(60)days prior to the date the facility would be required under this permit to begin using eDMR. Temporary waivers shall be valid for twelve(12)months and shall thereupon expire. At such time,DMRs shall be submitted electronically to the Division unless the permittee re-applies for and is granted a new temporary waiver by the Division. Information on eDMR and application for a temporary waiver from the NPDES electronic reporting requirements is found on the following web page: http://portal.ncdenr.org/web/wq/admin/bog/ipu/edmr Page 5 of 6 Permit NC0027626 Regardless of the submission method,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. 2. Signatory Requirements [Supplements Section B.(11.) (b) and supersedes Section B.(11.) (d)1 All eDMRs submitted to the permit issuing authority shall be signed by a person described in Part II, Section B.(11.)(a) or by a duly authorized representative of that person as described in Part II, Section B. 11.)(b). A person,and not a position,must be delegated signatory authority for eDMR reporting purposes. For eDMR submissions,the person signing and submitting the DMR must obtain an eDMR user account and login credentials to access the eDMR system. For more information on North Carolina's eDMR system,registering for eDMR and obtaining an eDMR user account,please visit the following web page: http://portal.ncdenr.org/web/wq/admin/bog/ipu/edmr Certification. Any person submitting an electronic DMR using the state's eDMR system shall make the following certification [40 CFR 122.22]. NO OTHER STATEMENTS OF CERTIFICATION WILL BE ACCEPTED: I certify, under penalty of law, that this document and all attachments were prepared under my direction or supervision in accordance with a system designed to assure that qualified personnel properly gather and evaluate the information submitted. Based on my inquiry of the person or persons who manage the system, or those persons directly responsible for gathering the information, the information submitted is, to the best of my knowledge and belief true, accurate, and complete..1 am aware that there are significant penalties for submitting false information, including the possibility offines and imprisonment for knowing violations." 3. Records Retention [Supplements Section D. (6.)1 The permittee shall retain records of all Discharge Monitoring Reports,including eDMR submissions. These records or copies shall be maintained for a period of at least 3 years from the date of the report. This period may be extended by request of the Director at any time [40 CFR 122.41]. Page 6 of 6 c 1 r • 1 l 11 ti--- ti I l jfls ' 1= p• J a H /47 I rc_-------_____...... s._-..;„.„„_e.ss,: llril i 4"4. a\ ,1,- k 9„ Outfall 001 ,, v off a 4 '': Ai 1,/ C 7 tO \N. N416 Q vimi, a 1 K rage is •offalga i& s V/7/? C..? 1 & c o0 vo s,kYYY • — 'o rill p 4 4, t„ 6 * a x.. \ \ a ss - Qa 4 w r J t M 5a AOs *. a 4 N 14Y, 0 \. , ' . ' (77 -7 - O`` N i 4.# li n.4. ct- N\J— (/) 0 N '•.--NI N'.', ,, 40 * 11 4 N c 0 ..0.0. C----N4' N ;---) ... .' i IL N ems e \ 4s 7!4 ai¢' rz 0 M N 0 c:\\\:\:,sass so•rsasa r I O A so O t...... H.ea g")%(6 r sn tea_ ;.. \` _`1 dr. l\ l m, _ 't, N.C. Department of Correction FacilityCaledoniaCorrectionalInstitutionWWTPAif OW Latitude: 36° 18'51" N State Grid: Boones Crossroads Location Longitude: 77°26'06" W Stream Class: C not to scale Receiving Stream: Roanoke River Drainage Basin: Roanoke River Basin Permitted Flow: 0.500 MGD Sub-Basin: 03-02-08 North NPDES Permit No. NC0027626 1 V Halifax County