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NC0021547_Fact Sheet_20190823
Fact Sheet NPDES Permit No. NCO021547 Permit Writer/Email Contact: Cassidy Kurtz, cassidy.kurtz@ncdenr.gov Date: August 23, 2019 Division/Branch: NC Division of Water Resources/NPDES Complex Permitting Fact Sheet Template: Version 09Jan2017 Permitting Action: ® Renewal ❑ Renewal with Expansion ❑ New Discharge ❑ Modification (Fact Sheet should be tailored to mod request) Note: A complete application should include the following: • For New Dischargers, EPA Form 2A or 2D requirements, Engineering Alternatives Analysis, Fee • For Existing Dischargers (POTW), EPA Form 2A, 3 effluent pollutant scans, 4 2" a species WET tests. • For Existing Dischargers (Non-POTW), EPA Form 2C with correct analytical requirements based on industry category. Complete applicable sections below. If not applicable, enter NA. 1. Basic Facility Information Facility Information Applicant/Facility Name: Town of Franklin / Franklin WWTP Applicant Address: PO Box 1479, Franklin, NC 28744 Facility Address: Off SR 1324, Franklin, NC 28734 Permitted Flow: 1.65 MGD Facility Type/Waste: MAJOR Municipal; 99% domestic Facility Class: Class III Treatment Units: Mechanical Screen, Grit Removal, EQ Basin, Oxidation Ditch, Clarifiers, Aerobic Digester, Chlorine Contact Chamber, Dechlorination Pretreatment Program (Y/l): Y County: Macon Region: Asheville Briefly describe the proposed permitting action and facility background: Town of Franklin applied for a NPDES permit renewal at 1.65 MGD. This facility serves a population of 4700 within the town of Franklin and Macon County. Franklin WWTP has one significant industrial user, and a modified pretreatment Page 1 of 9 program. This facility discharges through Outfall 001 into the Little Tennessee River, which feeds into Lake Emory. 2. Receiving Waterbody Information Receiving Waterbody Information Outfalls/Receiving Stream(s): Outfall 001 — Little Tennessee River Stream Segment: 2-(1)c2 Stream Classification: C * Drainage Area (miz): 299 Summer 7Q10 (cfs): 157 Winter 7Q10 (cfs): 186 30Q2 (cfs): Average Flow (cfs): 682 IWC (% effluent): 1.60% 303(d) listed/parameter: No, the segment is not listed in the 2016 303(d) for any parameters Subject to TMDL/parameter: Yes — State wide Mercury TMDL implementation. Sub-basin/HUC: 04-04-01 / HUC: 06010202 USGS Topo Quad: G5NW *Note: Stream segment and classification have been updated to reflect the facility's discharge. When comparing the facility map to the "NC Surface Water Classifications" map, the stream segment previously listed in BIMS (i.e. 2-(26.5)) is about 5 miles downstream from the actual discharge. 3. Effluent Data Summary Effluent data for Outfall 001 is summarized below for the period of August 2014 through August 2018. Table. Effluent Data Summary Outfall 001 Permit Parameter Units Average Max Min Limit 1'LVW MGD 0.767 2.162 0.253 MA 1.65 WA 45.0 BOD mg/1 5.98 21.2 < 2 MA 30.0 85% BOD Removal % 98.12 99.28 95.88 removal WA 45.0 TSS mg/l 5.89 59.3 < 2.5 MA 30.0 Page 2 of 9 85% TSS Removal % 98.36 99.13 96.87 removal (geometric) Fecal coliform #/100 ml 11.7 560 < 1 WA 400 MA 200 DM 28.0 TRC µg/l 32.2 49 < 20 (< 50 compliance) Temperature ° C 17.03 26 4 6.0 < pH < pH SU 7.2 7.8 6.4 9.0 NH3N mg/l 0.163 2.8 < 0.1 TN mg/1 10.93 20.8 2.01 TP mg/1 3.57 5.5 0.92 Total Mercury ng/1 3.50 19 < 0.2 AA 47.0 DO (from 3 effluent mg/1 8.75 8.94 8.4 pollutant scans) MA -Monthly Average, WA -Weekly Average, DM -Daily Maximum, DA-Daily Average, AA -Annual Average 4. Instream Data Summary Instream monitoring may be required in certain situations, for example: 1) to verify model predictions when model results for instream DO are within 1 mg/l of instream standard at full permitted flow; 2) to verify model predictions for outfall diffuser; 3) to provide data for future TMDL; 4) based on other instream concerns. Instream monitoring may be conducted by the Permittee, and there are also Monitoring Coalitions established in several basins that conduct instream sampling for the Permittee (in which case instream monitoring is waived in the permit as long as coalition membership is maintained). If applicable, summarize any instream data and what instream monitoring will be proposed for this permit action: While no instream monitoring is currently required by the facility, ambient monitoring station data is available. AMS station G0035000 is about 8 miles upstream of Franklin WWTP, and AMS station G2000000 is about 5 miles downstream. Below is a table summary of data analyzed from January 2014 to October 2016. Upstream Downstream Avs, Max Min Avg, Max Min DO 9.7 12.8 7.6 9.9 13.5 7.8 Fecal Coliform 76.7 550 22 68.9 230 14 Temperature 15.6 1 25.4 1 3.8 16.5 27 4.9 H 6.8 1 7.4 5.9 7.0 1 7.6 1 5.5 Page 3 of 9 While DO, temperature, and pH showed increases from upstream to downstream, fecal coliform showed a decrease. Analysis shows no statistically significant differences between the upstream and downstream sites for all parameters listed. There are no recommended changes to instream monitoring requirements during this permit renewal. Is this facility a member of a Monitoring Coalition with waived instream monitoring (YN): NO Name of Monitoring Coalition: Nh 5. Compliance Summary Summarize the compliance record with permit effluent limits (past 5 years): The facility reported 1 TSS limit violation in January 2013, and 1 BOD limit violation in February 2013. The TSS violation exceeded the weekly average and resulted in an enforcement case; the BOD violation also was an exceedance of the weekly average and resulted in an enforcement case. Summarize the compliance record with aquatic toxicity test limits and any second species test results (past S years): The facility passed 18 of 18 quarterly chronic toxicity tests, as well as all 4 second species chronic toxicity tests. Summarize the results from the most recent compliance inspection: The last facility inspection conducted in May 2018 reported that the facility was well maintained and operated. The inspection report noted that this facility has been understaffed since a 2013 inspection. 6. Water Quality -Based Effluent Limitations (WQBELs) Dilution and Mixing Zones In accordance with 15A NCAC 2B.0206, the following streamflows are used for dilution considerations for development of WQBELs: 1Q10 streamflow (acute Aquatic Life); 7Q10 streamflow (chronic Aquatic Life; non -carcinogen HH); 30Q2 streamflow (aesthetics); annual average flow (carcinogen, HH). If applicable, describe any other dilution factors considered (e.g., based on CORMIX model results): NA If applicable, describe any mixing zones established in accordance with 15,4 NCAC 2B.0204(b): NA Oxygen -Consuming Waste Limitations Limitations for oxygen -consuming waste (e.g., BOD) are generally based on water quality modeling to ensure protection of the instream dissolved oxygen (DO) water quality standard. Secondary TBEL limits (e.g., BOD= 30 mg/1 for Municipals) may be appropriate if deemed more stringent based on dilution and model results. Ifpermit limits are more stringent than TBELs, describe how limits were developed: Limits for BOD are based on secondary treatment standards. No changes are proposed from the previous permit limits. Ammonia and Total Residual Chlorine Limitations Limitations for ammonia are based on protection of aquatic life utilizing an ammonia chronic criterion of 1.0 mg/1(summer) and 1.8 mg/1(winter). Acute ammonia limits are derived from chronic criteria, utilizing a multiplication factor of 3 for Municipals and a multiplication factor of 5 for Non -Municipals. Limitations for Total Residual Chlorine (TRC) are based on the NC water quality standard for protection of aquatic life (17 ug/1) and capped at 28 ug/1(acute impacts). Due to analytical issues, all TRC values reported below 50 ug/1 are considered compliant with their permit limit. Page 4 of 9 Describe any proposed changes to ammonia and/or TRC limits for this permit renewal: There are no limits for NH3-N, and no changes are recommended at this time. The IWC for this facility is 1.6%, and based on waste load allocation calculations, the allowable discharge concentrations are 48.9 mg/L (summer) and 116.7 mg/L (winter). The facility will continue to monitor NH3-N on a weekly basis. TRC was capped at 28 µg/L based on a waste load allocation. There are no proposed changes for TRC. Reasonable Potential Analysis (RPA)_ for Toxicants If applicable, conduct RPA analysis and complete information below. The need for toxicant limits is based upon a demonstration of reasonable potential to exceed water quality standards, a statistical evaluation that is conducted during every permit renewal utilizing the most recent effluent data for each outfall. The RPA is conducted in accordance with 40 CFR 122.44 (d) (i). The NC RPA procedure utilizes the following: 1) 95% Confidence Level/95% Probability; 2) assumption of zero background; 3) use of/z detection limit for "less than" values; and 4) streamflows used for dilution consideration based on 15A NCAC 2B.0206. Effective April 6, 2016, NC began implementation of dissolved metals criteria in the RPA process in accordance with guidance titled NPDES Implementation of Instream Dissolved Metals Standards, dated June 10, 2016. A reasonable potential analysis was conducted on effluent toxicant data collected between June 2013 and February 2016. Pollutants of concern included toxicants with positive detections and associated water quality standards/criteria. Based on this analysis, the following permitting actions are proposed for this permit: • Effluent Limit with Monitoring. The following parameters will receive a water quality -based effluent limit (WQBEL) since they demonstrated a reasonable potential to exceed applicable water quality standards/criteria: None • Monitoring Day. The following parameters will receive a monitor -only requirement since they did not demonstrate reasonable potential to exceed applicable water quality standards/criteria, but the maximum predicted concentration was >50% of the allowable concentration: Silver • No Limit or Monitoring: The following parameters will not receive a limit or monitoring, since they did not demonstrate reasonable potential to exceed applicable water quality standards/criteria and the maximum predicted concentration was <50% of the allowable concentration: Cadmium, Total Chromium, Copper, Cyanide, Lead, Nickel, Zinc • POTW Effluent Pollutant Scan Review: Three effluent pollutant scans were evaluated for additional pollutants of concern. o The following parameter(s) will receive a water quality -based effluent limit (WQBEL) with monitoring, since as part of a limited data set, two samples exceeded the allowable discharge concentration: None o The following parameter(s) will receive a monitor -only requirement, since as part of a limited data set, one sample exceeded the allowable discharge concentration: Bis(2- Ethylhexyl) phthalate (max predicted concentration >50% of allowable) Attached are the RPA results and a copy of the guidance entitled "NPDESImplementation oflnstream Dissolved Metals Standards — Freshwater Standards. " Toxicity Testinv Limitations Permit limits and monitoring requirements for Whole Effluent Toxicity (WET) have been established in accordance with Division guidance (per WET Memo, 8/2/1999). Per WET guidance, all NPDES permits issued to Major facilities or any facility discharging "complex" wastewater (contains anything other than domestic waste) will contain appropriate WET limits and monitoring requirements, with several exceptions. The State has received prior EPA approval to use an Alternative WET Test Procedure in Page 5 of 9 NPDES permits, using single concentration screening tests, with multiple dilution follow-up upon a test failure. Describe proposed toxicity test requirement: This is a Major POTW, and a chronic P/F test at 1.60% effluent will continue on a quarterly frequency. Mercury Statewide TMDL Evaluation There is a statewide TMDL for mercury approved by EPA in 2012. The TMDL target was to comply with EPA's mercury fish tissue criteria (0.3 mg/kg) for human health protection. The TMDL established a wasteload allocation for point sources of 37 kg/year (81 lb/year), and is applicable to municipals and industrial facilities with known mercury discharges. Given the small contribution of mercury from point sources (^-2% of total load), the TMDL emphasizes mercury minimization plans (MMPs) for point source control. Municipal facilities > 2 MGD and discharging quantifiable levels of mercury (>1 ng/1) will receive an MMP requirement. Industrials are evaluated on a case -by -case basis, depending if mercury is a pollutant of concern. Effluent limits may also be added if annual average effluent concentrations exceed the WQBEL value (based on the NC WQS of 12 ng/1) and/or if any individual value exceeds a TBEL value of 47 ng/l Table. Mercury Effluent Data Summary 2014 2015 2016 2017 2018 # of Samples 2 6 6 4 3 Annual Avera e Conc. n /L 4.9 5.9 2.4 2.1 2.3 Maximum Conc., n L 5.69 19.00 4.08 3.63 3.73 TBEL, ngfL 47 WQBEL, n /L 748.7 Describe proposed permit actions based on mercury evaluation: Since no annual average mercury concentration exceeded the WQBEL, and no individual mercury sample exceeded the TBEL, no mercury limit is required. Additionally, since the facility is less than 2 MGD, the mercury minimization plan (MMP) will be removed from the permit. Other TMDL/Nutrient Management Strategy Considerations If applicable, describe any other TMDLs/Nutrient Management Strategies and their implementation within this permit: NA Other WQBEL Considerations If applicable, describe any other parameters of concern evaluated for WQBELs: NA If applicable, describe any special actions (HQW or ORW) this receiving stream and classification shall comply with in order to protect the designated waterbody: NA If applicable, describe any compliance schedules proposed for this permit renewal in accordance with 15A NCAC 2H. 0107(c)(2)(B), 40CFR 122.47, and EPA May 2007 Memo: NA If applicable, describe any water quality standards variances proposed in accordance with NCGS 143- 215.3(e) and 15A NCAC 2B.0226 for this permit renewal: NA Page 6 of 9 7. Technology -Based Effluent Limitations (TBELs) Municipals Are concentration limits in the permit at least as stringent as secondary treatment requirements (30 mg/1 BODs/TSS for Monthly Average, and 45 mg/l for BOD.VTSS for Weekly Average). YES If NO, provide a justification for alternative limitations (e.g., waste stabilization pond). NA Are 85% removal requirements for BOD51TSS included in the permit? YES If NO, provide a justification (e.g., waste stabilization pond). NA 8. Antidegradation Review (New/Expanding Discharge) The objective of an antidegradation review is to ensure that a new or increased pollutant loading will not degrade water quality. Permitting actions for new or expanding discharges require an antidegradation review in accordance with 15A NCAC 2B.0201. Each applicant for a new/expanding NPDES permit must document an effort to consider non -discharge alternatives per 15A NCAC 2H.0105(c)(2). In all cases, existing instream water uses and the level of water quality necessary to protect the existing use is maintained and protected. If applicable, describe the results of the antidegradation review, including the Engineering Alternatives Analysis (EAA) and any water quality modeling results: NA 9. Antibacksliding Review Sections 402(o)(2) and 303(d)(4) of the CWA and federal regulations at 40 CFR 122.44(1) prohibit backsliding of effluent limitations in NPDES permits. These provisions require effluent limitations in a reissued permit to be as stringent as those in the previous permit, with some exceptions where limitations may be relaxed (e.g., based on new information, increases in production may warrant less stringent TBEL limits, or WQBELs may be less stringent based on updated RPA or dilution). Are any effluent limitations less stringent than previous permit (YES/NO): NO If YES, confirm that antibacksliding provisions are not violated: NA 10. Monitoring Requirements Monitoring frequencies for NPDES permitting are established in accordance with the following regulations and guidance: 1) State Regulation for Surface Water Monitoring, 15A NCAC 2B.0500; 2) NPDES Guidance, Monitoring Frequency for Toxic Substances (7/15/2010 Memo); 3) NPDES Guidance, Reduced Monitoring Frequencies for Facilities with Superior Compliance (10/22/2012 Memo); 4) Best Professional Judgement (BPJ). Per US EPA (Interim Guidance, 1996), monitoring requirements are not considered effluent limitations under Section 402(o) of the Clean Water Act, and therefore anti - backsliding prohibitions would not be triggered by reductions in monitoring frequencies. For instream monitoring, refer to Section 4. 11. Electronic Reporting Requirements The US EPA NPDES Electronic Reporting Rule was finalized on December 21, 2015. Effective December 21, 2016, NPDES regulated facilities are required to submit Discharge Monitoring Reports (DMRs) electronically. Effective December 21, 2020, NPDES regulated facilities will be required to submit additional NPDES reports electronically. This permit contains the requirements for electronic reporting, consistent with Federal requirements. Page 7 of 9 12. Summary of Proposed Permitting Actions A. Table. Current Permit Conditions and Proposed Changes 1.65 MGD Parameter Current Permit Proposed Change Basis for Condition/Change Flow MA 1.65 MGD No change 15A NCAC 2B .0505 BOD5 MA 30.0 mg/1 No change TBEL. Secondary treatment WA 45.0 mg/1 standards / 40 CFR 133 / 15A NCAC 2B .0406 TSS MA 30.0 mg/l No change TBEL. Secondary treatment WA 45.0 mg/1 standards / 40 CFR 133 / 15A NCAC 2B .0406 Fecal coliform MA 200 /100ml No change WQBEL. State WQ standard, 15A WA 400 /100ml NCAC 2B Toxicity Test Chronic limit, 1.60% No change WQBEL. No toxics in toxic effluent amounts. 15A NCAC 2B TRC 28 µg/1 No change WQBEL. Based on protection of State WQ criteria (WLA). 15A NCAC 2B Temperature Monitor 3/week No change WQBEL. State WQ Standard, 15A NCAC 2B pH 6.0 — 9.0 SU No change WQBEL. State WQ standard, 15A NCAC 2B NH3-N Monitor Weekly No change Based on protection of State WQ criteria. 15A NCAC 2B .0500 Total Nitrogen Monitor Monthly No change WQBEL. State WQ standard, 15A NCAC 2B .0500 Total Phosphorus Monitor Monthly No change WQBEL. State WQ standard, 15A NCAC 2B .0500 Mercury AA 47 ng/l Remove limit, Mercury TMDL evaluation monitoring, and MMP Bis(2-Ethylhexyl) No requirement Add quarterly effluent Based on RPA, predicted maximum Phthalate monitoring concentration > 50% Allowable concentration Silver No requirement Add quarterly effluent Reasonable potential found in RPA monitoring Total Hardness No requirement Add quarterly effluent Hardness -dependent dissolved and upstream metals water quality standards monitoring approved in 2016 Effluent Pollutant 3/permit cycle No change 40 CFR 122 Scan Page 8 of 9 Electronic No requirement Add Electronic hi accordance with EPA Electronic Reporting Reporting Special Reporting Rule 2015. Condition MCil]-1Vlilllon gallons per day, MA -Monthly Average, WA -Weekly Average, DM-lllaily Max, AA -Annual Average 13. Public Notice Schedule Permit to Public Notice: 04/24/2019 Per 15A NCAC 211.0109 & .0111, The Division will receive comments for a period of 30 days following the publication date of the public notice. Any request for a public hearing shall be submitted to the Director within the 30 days comment period indicating the interest of the party filing such request and the reasons why a hearing is warranted. 14. Fact Sheet Addendum (if applicable) Were there any changes made since the Draft Permit was public noticed (Yes/No): NO If Yes, list changes and their basis below: NA — No comments received. 15. Fact Sheet Attachments • NH3/TRC WLA Calculations • BOD & TSS Removal Rate Calculations • Mercury TMDL Calculations • PERCS Pretreatment Information Request Form • RPA Sheets o Input Information o Data Analyzed o Results Summary o Dissolved to Total Metal Calculation • WET Testing and Self -Monitoring Summary • Monitoring Report Violations Summary • Instream Data from AMS stations • NPDES Implementation of Instream Dissolved Metals Standards - Freshwater Standards • Water Compliance Inspection Report (May 23, 2018) Page 9 of 9 NH3/TRC WLA Calculations Facility: Franklin WWTP PermitNo. NCO021547 Prepared By: Cassidy Kurtz Enter Design Flow (MGD): 1.65 Enter s7Q10 (cfs): 157 Enter w7Q10 cfs : 186 Total Residual Chlorine (TRC) Daily Maximum Limit (ug/1) Ammonia (Summer) Monthly Average Limit (mg NH3-N/1) s7010 (CFS) 157 s7Q10 (CFS) 157 DESIGN FLOW (MGD) 1.65 DESIGN FLOW (MGD) 1.65 DESIGN FLOW (CFS) 2.5575 DESIGN FLOW (CFS) 2.5575 STREAM STD (UG/L) 17.0 STREAM STD (MG/L) 1.0 Upstream Bkgd (ug/1) 0 Upstream Bkgd (mg/1) 0.22 IWC (%) 1„60 IWC (%) 1.60 Allowable Conc. (ug/l) ; 1061 Allowable Conc. (mg/1) 48.9 Ammonia (Winter) Monthly Average Limit (mg NH3-N/1) Fecal Coliform w7Q10 (CFS) 186 Monthly Average Limit: 200/100m1 DESIGN FLOW (MGD) 1.65 (if DF >331; Monitor) DESIGN FLOW (CFS) 2.5575 (If DF<331; Limit) STREAM STD (MG/L) 1.8 Dilution Factor (DF) 62.39 Upstream Bkgd (mg/l) 0.22 IWC (%) 1.36 Allowable Conc. (mg/1) 116.7 Total Residual Chlorine 1. Cap Daily Max limit at 28 ug/I to protect for acute toxicity Ammonia (as NH3-Ny 1. If Allowable Conc > 35 mg/l, Monitor Only 2. Monthly Avg limit x 3 = Weekly Avg limit (Municipals) 3. Monthly Avg limit x 5 = Daily Max limit (Non-Munis) If the allowable ammonia concentration is > 35 mg/L, no limit shall be imposed Fecal Coliform 1. Monthly Avg limit x 2 = 400/100 ml = Weekly Avg limit (Municipals) = Daily Max limit (Non -Muni) a Y C m L. LL. e Ln T`I N O O U 1 n N Oqr N N w r-1 n M O N tD M O tD Lneq R;t n ri Ln -! qt n ri Ln w a-i m Ln M .1 M M ri, 00 w M ao M oo n o0 0o n n 1, 00 w M o0 00: rn! 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C D_ O LL LU r-I .. E M LD O m Z Z !_ r-I � r-ILn Ln Ln Ln ri Ln WtD ko W n n r 00 00 00 r-Ir-Ii ++ U W ci M N c-I c-I ri n \ en 00 r Ln r-I N r cn r-I c ri ri M ri ri ri M r-I ` 01 M l\D L! N Ln � t\p tp l rn ntD LL IDr\-I d' O rNi r-I ^ r-I eO..1 ! r-I ON I NIn Ieeyi ON MINIly, M O IN � I� I n Ln NI�ILo r-I O eq U n N LO L Ln � U N 'r J Z O C \ on O1 j d A to M m J Q � _ Q OD ;G U � E J W t0 SXm w co CCf j Il Xk Q ` P NPDES/A uifer Protection Permitting Unit Pretreatment Information Request Form PERMIT WRITER COMPLETES THIS PART: PERMIT WRITERS - AFTER you get this form back Check all that apply from PERCS: - Notify PERCS if LTMP/STMP data we said should be Date of Re uest 9/13/2018 municipal renewal X on DMRs is not really there, so we can get it for you Re uestor Cassidy Kurtz new industries (or NOV POTW). Facility Name Franklin WWTP WWTP expansion - Notify PERCS if you want us to keep a specific POC Permit Number NC0021547 Speculative limits In LTMP/STMP so you will have data for next permit Region Asheville stream reGass. renewal. - Email PERCS draft permit, fact sheet, RPA. Basinj Little Tennessee outfall relocation - Send PERCS paper copy of permit (w/o NPDES 7Q10 change boilerplate), cover letter, final fact sheet. Email RPA if other changes. other Check applicable PERCS staff: Other Comments to PERCS: BIRD, CPF, CTB, FRB, TAR Vivien Zhon 807-6310 Facility is rated 1.65 MGD with 1 SIU listed in its application (Macon X CHO HIW, LTN, LUM, NES, NEW, ROA YAD County Landfill - Landfill leachate 1 Municipal Solid Waste), and is listed in POTW with pretreatment spreadsheet. Monti Hassan (807-6314) L__ - .. I PERCS PRETREATMENT STAFF COMPLETES THIS PART: - Status of Pretreatment Program (check all that apply) 1) facility has no SIU's, does have Division approved Pretreatment Program that is INACTIVE 2) facility has no SIU's, does not have Division approved Pretreatment Program 3) facility has SIUs and DWQ approved Pretreatment Program (list "DEV' if program still under development) 3a) Full Program with LTMP 3b) Modified Program with STMP 4) additional conditions regarding Pretreatment attached or listed below Flow, MGD Permitted Actual Time period for Actual STMP time frame: Industrial Most recent: Uncontrollable n/a N t Cycle: d d Parameter of POC due to NPDESI Non- Required by Required POC due POTW POC S P LTMP Concern Disch Permit EPA* 503 to SIU*** (Explain Effluent Effluent Check List List Limit u Slludge'" below) ** Freq Freq Q = Quarter M= on y BOD v 4 Q M TSS 4 Q M NH3 4 Q M Arsenic 4 Q M Cadmium 4 Q M Chromium 4 Q M Copper 4 Q M Cyanide 4 Q M Is all data on DMRs? ti dead 4 Q M YES11 Mercury 4 Q M NO attach data Molybdenum 4 Q M ckel 4 Q M Sliver 1r 4 Q M Selenium 4 Q M Zinc 4 Q M /s data inspreadsheet? Total Nitrogen 4 Q M YES email to writer Phosphorus 4 Q M NO 4 Q M 4 Q M 4 Q M 4 Q M *Always in the LTMP/STMP ** Only in LTMP/STMP if sludge land app or composte (dif POCs for incinerators) *** Only in LTMP/STMP while SIU still discharges to POTW **** Only in LTMP/STMP when pollutant is still of concern to POTW Comments to Permit Writer lox., explanation of arw POCs: info you have on IU related investigations into NPDES problems): s Ikns me , j (tee S` Lk NCO021547 - PERC NPDES_Pretreatment.request.fonn.xlsx Revised: July 24, 2007 9 is J O3 a `m .o V C V H E z r m F- J �L J J J 4 J J J= , J J `1 J _-_ J == 1 J J J J OS m O m m 01 m Ot ZA O) 07 0I m 3 7 7 O 7 7. 1 O O O O � O O Cl) O M � O Q n CD fD O OO O ¢O O OM O Z cM to MZQ d N c 3 ¢ Cl' _ _ L. y LL LL LL LL LL LL LL LL. 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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 1. NC Dissolved Metals Water Quality Standards/Aquatic Life Protection Parameter Acute FW, µg/1 (Dissolved) Chronic FW, µg/l (Dissolved) Acute SW, µg/1 (Dissolved) Chronic SW, µg/1 (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 1 Notes: 1. FW= Freshwater, SW= Saltwater 2. Calculation = Hardness dependent standard 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 213.0200 (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 2. 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/1 Cadmium, Acute WER*{1.136672-[In hardness](0.041838)} a^{0.9151 [In hardness]-3.1485} Cadmium, Acute Trout waters WER*{l.136672-[1n hardness](0.041838)} a^{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 a^{0.8190[In hardness]+0.6848} Copper, Acute WER*0.960 a^{0.9422[ln hardness] - 1.700) Copper, Chronic WER*0.960 • e^{0.8545[ln hardness] - 1.702} Lead, Acute WER*{1.46203-[In hardness](0.145712)) • e^{1.273[ln hardness]-1.460) Lead, Chronic WER*{1.46203-[In hardness](0.145712)) • e^{1.273[ln hardness]-4.705} Nickel, Acute WER*0.998 a^{0.8460[ln hardness]+2.255) Nickel, Chronic WER*0.997 a^{0.8460[ln hardness]+0.0584} Page 1 of 4 Permit No. NCO021547 Silver, Acute WER*0.85 - e^{1.72[ln hardness]-6.59} Silver, Chronic Not applicable Zinc, Acute I WER*0.978 • e^{0.8473[ln hardness]+0.884) Zinc, Chronic I 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. RPA Permitting Guidanct BELs far 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, 7Q 10 (the spreadsheet automatically calculates the 1 Q10 using the formula 1 Q 10 = 0.843 (s7Q 10, 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. Page 2 of 4 Permit No. NCO021547 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) + (s7Q 10, 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. EPA default partition coefficients or the "Fraction Dissolved" converts the value for dissolved metal at laboratory conditions to total recoverable metal at in -stream ambient conditions. This factor is calculated using the linear partition coefficients found in The Metals Translator: Guidance for Calculating a Total Recoverable Permit Limit from a Dissolved Criterion (EPA 823-B-96-007, June 1996) and the equation: Cdiss = I Ctotal 1 + { [Kp.] [Ss(1+a)] [10-6] } Where: ss = in -stream suspended solids concentration [mg/1], minimum of 10 mg/L used, and Kpo and a = constants that express the equilibrium relationship between dissolved and adsorbed forms of metals. A list of constants used for each hardness -dependent metal can also be found in the RPA program under a sheet labeled DPCs. 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. 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 + Ow) (Cwgs) — (s7Q10) (Cb) Qv, 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 s7Q 10 may be incorporated as applicable: 1 Q 10 = used in the equation to protect aquatic life from acute toxicity Page 3 of 4 Permit No. NC0021547 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: Parameter Value Comments (Data Source) Average Effluent Hardness (mg/L) 41.67 E Effluent pollutant scans [Total as, CaCO3 or (Ca+Mg)] Average Upstream Hardness (mg/L) 25 Default value [Total as, CaCO3 or (Ca+Mg)] 7Q10 summer (cfs) 157.00 Previous fact sheet, BIMS 1Q10 (cfs) 127.75 RPA calculation Permitted Flow (MGD) 1.65 1 Previous permit Date: October 23 2018 Permit Writer: Cassidy Kurtz Page 4 of 4 United States Environmental Protection Agency Form Approved. EPA Washington, D.C. 20460 OMB No. 2040-0057 Water Compliance Inspection Report Approval expires 8-31-98 Section A: National Data System Coding (i.e., PCS) Transaction Code NPDES yr/mo/day Inspection Type Inspector Fac Type 1 E 2 15 I 3 1 NCO021647 111 121 18/05/23 J 17 18 1,,E 19 1 s j 201 I 21111111IIIIIIIIIII1IIIIII1IIIIIIIIIIIIIII 166 Inspection Work Days Facility Self -Monitoring Evaluation Rating B1 QA Reserved 72 LNJ 67 70LJ 71 LJ 731 74 751 I I I I I 80 Section B: Facility Data Name and Location of Facility Inspected (For Industrial Users discharging to POTW, also include Entry Time/Date Permit Effective Date POTW name and NPDES permit Number) 10:00AM 18/05/23 12/12/01 Franklin WWTP Sierra Dr Exit Time/Date Permit Expiration Date Franklin NC 28734 02:OOPM 18/05/23 17/11/30 Name(s) of Onsite Representative(s)rritles(s)/Phone and Fax Number(s) Other Facility Data /// William Logan Deal/ORC/828-524-2516/ Name, Address of Responsible Officiairritle/Phone and Fax Number Contacted Sam Greenwood,PO Box 1479 Franklin NC 287441479/Town No Manager/828-524-2516/ Section C: Areas Evaluated During Inspection (Check only those areas evaluated) Permit N Operations & Maintenance E Other Section D: Summary of Finding/Comments (Attach additional sheets of narrative and checklists as necessary) (See attachment summary) Name(s) and Signature(s) of Inspector(s) Agency/Office/Phone and Fax Numbers Date Timothy H Heim ARO WQ//828-296-4665/ Signature of Management Q A Reviewer Agency/Office/Phone and Fax Numbers Date EPA Form 3560-3 (Rev 9-94) Previous editions are obsolete. Page# NPDES yr/mo/day Inspection Type (Cont.) 31 NCO021547 1218/05/23 17 18 � ( Section D: Summary of Finding/Comments (Attach additional sheets of narrative and checklists as necessary) Tim Heim of the Asheville Regional Office performed a Compliance Evaluation Inspection on May 23, 2018. Bill Deal (ORC) was present at the time of the inspection. The facility appeared to be well maintained and operated and in compliance with Permit NC0067326. Inspections conducted in 2013, 2015, and 2017 indicated the plant is understaffed. The facility continues to be vulnerable under this condition. Additional personnel may help maintain continued compliance with increasing regulatory requirements and reduce the chance for injuries and deferred maintenance. As noted in the 2017 Inspection: The Northeast Guide for Estimating Staffing at Publicly and Privately Owned Wastewater Treatment Plants indicates that a staff of 7 is more appropriate to adequately operate and maintain a system with the characteristics of the Franklin WWTP. Page# Permit: NCO021547 Inspection Date: 05/23/2018 Other Owner - Facility: Franklin WWTP Inspection Type: Compliance Evaluation Yes No NA NE Comment: Inspections conducted in 2013 2015. and 2017 indicated the plant is understaffed. The facility continues to be vulnerable under this condition. Additional personnel may help maintain continued compliance with increasing re, ulaq toy requirements and reduce the chance for iniuries and deferred maintenance. Operations $ Maintenance Yes No NA NE Is the plant generally clean with acceptable housekeeping? ❑ ❑ ❑ Does the facility analyze process control parameters, for ex: MLSS, MCRT, Settleable ❑ ❑ ❑ Solids, pH, DO, Sludge Judge, and other that are applicable? Comment: Permit Yes No NA NE (If the present permit expires in 6 months or less). Has the permittee submitted a new ❑ ❑ 0 ❑ application? Is the facility as described in the permit? ❑ ❑ ❑ # Are there any special conditions for the permit? ❑ M ❑ ❑ Is access to the plant site restricted to the general public? a ❑ ❑ ❑ Is the inspector granted access to all areas for inspection? M ❑ ❑ ❑ Comment: The faciWy ppj eared well maintained at the time of the inspection. Bar Screens Yes No NA NE Type of bar screen a.Manual ❑ b.Mechanical Are the bars adequately screening debris? ❑ ❑ ❑ Is the screen free of excessive debris? ■ ❑ ❑ ❑ Is disposal of screening in compliance? 0 ❑ ❑ ❑ Is the unit in good condition? M ❑ ❑ ❑ Comment: Grit Removal Yes No NA NE Type of grit removal a.Manual ❑ b.Mechanical Is the grit free of excessive organic matter? 0 ❑ ❑ ❑ Page# 3 Permit: NCO021547 Owner - Facility: Franklin VW TP Inspection Date: 05/23/2018 Inspection Type: Compliance Evaluation Grit Removal Yes No NA NE Is the grit free of excessive odor? ❑ ❑ ❑ # Is disposal of grit in compliance? ❑ ❑ ❑ Comment: E ualization Basins Yes No NA NE Is the basin aerated? M ❑ ❑ ❑ Is the basin free of bypass lines or structures to the natural environment? 0 ❑ ❑ ❑ Is the basin free of excessive grease? ❑ ❑ ❑ Are all pumps present? ❑ ❑ ❑ Are all pumps operable? ❑ ❑ ❑ Are float controls operable? M ❑ ❑ ❑ Are audible and visual alarms operable? ❑ ❑ ❑ # Is basin size/volume adequate? ❑ ❑ ❑ Comment: Oxidation Ditches Yes No NA NE Are the aerators operational? M ❑ ❑ ❑ Are the aerators free of excessive solids build up? 0 ❑ ❑ ❑ # Is the foam the proper color for the treatment process? 0 ❑ ❑ ❑ Does the foam cover less than 25% of the basin's surface? ❑ ❑ ❑ Is the DO level acceptable? ❑ ❑ ❑ Are settleometer results acceptable (> 30 minutes)? ❑ ❑ ❑ M Is the DO level acceptable?(1.0 to 3.0 mg/1) ❑ ❑ ❑ ■ Are settelometer results acceptable?(400 to 800 ml/l in 30 minutes) ❑ ❑ ❑ ■ Comment: ORC reports operating the 3 oxidation rinds sequentially from a range of approximately .5 to 1 ma/L DO. Secondary Clarifier Yes No NA NE Is the clarifier free of black and odorous wastewater? 0 ❑ ❑ ❑ Is the site free of excessive buildup of solids in center well of circular clarifier? 0 ❑ ❑ ❑ Are weirs level? ■ ❑ ❑ ❑ Is the site free of weir blockage? ■ ❑ ❑ ❑ Is the site free of evidence of short-circuiting? M ❑ ❑ ❑ Is scum removal adequate? 0 ❑ ❑ ❑ Page# 4 r Permit: NC0021547 Inspection Date: 05/23/2018 Secondary Clarifier Owner - Facility: Franklin WWTP Inspection Type: Compliance Evaluation Is the site free of excessive floating sludge? Is the drive unit operational? Is the return rate acceptable (low turbulence)? Is the overflow clear of excessive solids/pin floc? Is the sludge blanket level acceptable? (Approximately % of the sidewall depth) Comment: Standby Power Is automatically activated standby power available? Is the generator tested by interrupting primary power source? Is the generator tested under load? Was generator tested & operational during the inspection? Do the generator(s) have adequate capacity to operate the entire wastewater site? Is there an emergency agreement with a fuel vendor for extended run on back-up power? Is the generator fuel level monitored? Comment: Yes No NA NE ■ ❑ ❑ ❑ ■ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ■ ❑ ❑ ❑ Yes No NA NE M ❑ ❑ ❑ ■ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ 1111 Page# 5