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HomeMy WebLinkAboutNC0036277_Permit Issuance_20010309NPDES DOCYNENT SCANNINO COVER SMEET NPDES Permit: NC0036277 McDowell Creek WWTP Document Type: Permit Issuance Wasteload Allocation Authorization to Construct (AtC) Permit Modification Complete File - Historical Engineering Alternatives (EAA) Correspondence Instream Assessment (67b) Speculative Limits Environmental Assessment (EA) Document Date: March 9, 2001 This document is printed on reuse paper - igraore aazy content on the reverse side of w A rF9 b `o� Q� Q�� > r NCDENR o c Mr. Barry Gullet CMUD Administrative Division 5100 Brookshire Boulevard Charlotte, North Carolina 28216 Dear Mr. Gullet: Michael F. Easley Governor William G. Ross, Jr., Secretary North Carolina Department of Environment and Natural Resources Kerr T. Stevens, Director Division of Water Quality March 9, 2001 Subject: Issuance of NPDES Permit NCO036277 CMUD McDowell Creek WWTP Mecklenburg County Division of Water Quality (Division) personnel have reviewed and approved your application for renewal of the subject permit. Accordingly, we are forwarding the attached NPDES discharge permit. This permit is 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 dated May 9, 1994 (or as subsequently amended). The following changes have been made to your permit: • The cover letter to your facility's draft permit erroneously stated that the new effluent mercury limit would be 0.14 µg/L. The effluent limit is, as listed in the effluent limits page of the draft, 0.014 jig/L. • The June -September frequency for instream dissolved o:rygen, temperature, conductivity and pH monitoring has becn changed to once per week as per your request. • The last line to the cyanide footnote in the effluent limits page has been deleted. You are no longer required to report values of cyanide measured below the specified quantitation 'level. A value of less than 10 µg/L will be considered zero for compliance purposes. Additionally, you should consider adherence to the quantitation level of 10 µg/L for cyanide and 0.2 µg/L for mercury as fulfilling the intent of Part II Section D. (4) of the NPDES permit for utilization of the most sensitive laboratory methods possible. By transmittal of this letter, these quantitation limits apply to all NPDES permits for the CMUD wastewater treatment plants. • As per a conference call made on December 21, 2000 between members of the NPDES Unit and your staff, the reasonable potential analysis for nickel was re -run using data from June 1999 onward. The results of this analysis indicate that there is no need for a nickel limit. You will still be required to monitor nickel through the Pretreatment Long Term Monitoring Plan. • The draft permit erroneously reported your total residual chlorine (MC) limit as 22 µg/L. The limit, based on the instream waste concentration of your effluent, should be 20 µg/L. Please note the change on the effluent limits page. • The instream monitoring requirements in the draft permit (Part A.(3.)) required that a spatial composite. sample be taken for chlorophyll -a, total phosphorus, NH3-N, TILT, and NO2-NO3. Asper your request, the sample type has been changed to grab to account for the shallow water level in the stream at the sampling point. The Division feels that this sampling requirement will provide important information regarding the effect of your discharge on the water quality of both the receiving stream and Mountain Island Lake. In response to your concern over chlorophyll -a monitoring, while it is true that there is no certification for this analysis available through the Division's Laboratory Certification Program, you are nevertheless required to perform this monitoring. N. C. Division of Water Quality / NPDES unit Phone: (919) 733-5083 1617 Mail Service Center, Raleigh, NC 27699-1617 fax: (919) 73.3-0719 Internet: h2o.enr.state.nc.us DENR Customer Service Center:1800 623-7748 The expiration date of the permit will stand at February 28, 2005, as per the draft permit. This is in accordance with the Division's Basinwide permitting schedule. This system of issuing permits by subbasin allows the Division to spread out the permits in basins containing many pennittees, of which the Catawba is one. In doing so, the NPDES unit may maintain a balanced workload, regardless of the river basin. The silver monitoring requirement in your permit is based upon a fording of reasonable potential for effluent from your facility to violate the allowable instream silver concentration of 0.1 µg/L. A review of your facility's Discharge Monitoring. Reports indicated five silver detects in the past two years. Once your facility has collected one year of silver data for which there have been no detects, you may request a modification to the pen -nit that reduces or eliminates the monitoring requirement. In response to your query about measurement frequency, "daily" does indeed mean five days per week excluding weekends and/or holidays. The Division is currently working on documentation to clarify this for all NPDES permit holders. -- As mentioned in the cover letter to the draft NPDES permit, the request for a monthly maximum flow limit of 7.6 MGD requires an Environmental Assessment (EA). The State Environmental Policy Act (SEPA) requires all facilities utilizing public monies to submit an EA for any expansions to ensure that the increased flow will not have a detrimental effect on the stream. Your request is functionally equivalent to an expansion, and so falls under the legislative requirements of SEPA. If any parts, measurement frequencies or sampling requirements contained in this permit are unacceptable to you, you have the right to an adjudicatory hearing upon written request within thirty (30) days following receipt of this letter. This request must be in the form of a written petition, conforming to Chapter 150B of the North Carolina General Statutes, and filed with the Office of Administrative Hearings (6714 Mail Service Center, Raleigh, North Carolina 27699-6714). Unless such demand is made, this decision shall be final and binding. Please note that this pemvt is not transferable except after notice to the Division. The Division may require modification or revocation and reissuance of the permit. This permit does not affect the legal requirements to obtain other permits which may be required by the Division of Water Quality or permits required by the Division of Land Resources, the Coastal Area Management Act or any other Federal or Local governmental permit that may be required. If you have any questions concerning this permit, please contact Natalie Sierra at telephone number (919) 733-5083, extension 551. Sincerely, ORIGINAL, 810FI 3Y ULL IREIC Kerr T. Stevens Cr- Mooresville Regional Office/Water Quality Section Mr. Roosevelt Childress, EPA Mecklenburg County Health Department Aquatic Toxicology Unit NPDES Unit Central Files NC Department of Environmental Health Permit NCO036277 STATE OF NORTH CAROLINA DEPARTMENT OF ENVIRONMENT AND NATURAL RESOURCES DIVISION OF WATER QUALITY PERMIT TO DISCHARGE WASTEWATER UNDER THE NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM In compliance with the provision 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, Charlotte -Mecklenburg Utility Department is hereby authorized to discharge wastewater from a facility located at the McDowell Creek Wastewater Treatment Plant NCSR 2074 Near the Town of Huntersville Mecklenburg County to receiving waters designated as McDowell Creek in the Catawba River Basin in accordance with effluent limitations, monitoring requirements, and other conditions set forth in Parts I, II, III and IV hereof. This permit shall become effective April 1, 2001. This permit and authorization to discharge shall expire at midnight on February 28, 2005. Signed this day March 9, 2001. C)RIGIKAL SIGNED BY BOLL REID Kerr T. Stevens, Director Division of Water Quality By Authority of the Environmental Management Commission Permit NC0036277 la SUPPLEMENT TO PERMIT COVER SHEET Charlotte -Mecklenburg Utility Department is hereby authorized to: y 1. Continue to operate the existing 6.0 MGD wastewater treatment facility consisting of: • Mechanical bar screens • grit removal • primary clarifiers -- • Biological Nutrient Removal (BNR) system • tertiary filtration • final clarifiers • anaerobic sludge digestion • sand drying beds • UV disinfection located at McDowell Creek Wastewater Treatment Plant, on SR 2074, Neck Road, near the Town of Huntersville in Mecklenburg County 2. Discharge from said treatment works at the location specified on the attached map into McDowell Creek, which is classified WS-IV waters in the Catawba River Basin. NC00036277 - CMUD McDowell Creek Facility 1 Latitude: 35°22'52" Sub -Basin: 03-08-33 Location Longitude: 80°56'25" uad N: FISNW/Lake Norman South Stream Class: Receiving Stream: WS-Iv McDowell Creek / Charlotte Mecklenburg Utilities Department (CMUD) NCa03627, Permitted Flow: 6.0 MGD CMUD - McDowell Creek W WTP Permit N 0036177 A. (1.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS - 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 N S, � ` r ¢;=�F,. L-. �i' �^ .+�':'•�,l'tn «F arti lr � its �he�6^;yii CHARACTERISTICS l•. �.� LIMITS f *r �� ,y�y�'' �Sy,�q y+ � `�' i�,�'�'%i°�`� .a"; '�%1'.b."��53 �',��'s?='a �� �� i =. a -. r e... �.�; 1. .a �: � MONI ORINGGREQUIREMENTS,,�� T=x ��{@� y' � ti �• �r �!"'Y�zE'?i��f�7i. �! K . <�y r+ i4vera e Z Wek Avee ra D a -1.mome, ; M1ea1.urlmen oehl nc Same SamIeLoca �Mont oti Flow 6.0 MGD Continuous Recording I or E BOD5 (20°C)2 April 1- October 31 5.0 mg/L 7.5 mg1L Daily Composite E, BOD5 (20°C)2 November 1- March 31 10.0 mg/L 15.0 mg/L Daily Composite E, Total Suspended Residue2 30.0 m /L 45.0 m /L Daily Composite E, I NH3 as N (April 1— October 31 2.0 m /L Daily Composite E NH3 as N November 1—March 31 2.5 m /L Daily Composite E Dissolved Oxygen3 Daily Grab E, U, D Fecal Coliform (geometric mean 2001100 ml 400 / 100 ml Daily Grab E Total Residual Chlorine4 20 /L Daily Grab E Temperature °C Daily Grab E, U, D Total Nitrogen NO2 + NO3 + TKN 10.0 m IL Monthly Composite E Total Phosphorus 1.0 m /L Monthly Composite E Chronic Toxicitys Quarterly Composite E Conductivity Daily Grab E, U, D Copper 2/Month Composite E Silver 2/Month Composite E Zinc 2/Month Composite E Mercury6 0.014 /L Weekly Composite E Footnotes: 1 Sample Locations: E - Effluent, I - Influent, U - Upstream at Beatties Ford Road, D- Downstream at Neck Road. Upstream and downstream samples shall be grab samples. Stream samples shall be taken once per week. 2 The monthly average effluent BOD5 and total suspended residue concentrations shall not exceed 15% of the respective influent value (85% removal). 3 The daily average dissolved oxygen effluent concentrations shall' not be less than 5.0 mg/ L. 4 Limit and monitoring only apply if effluent is chlorinated. S Whole effluent toxicity shall be measured by Chronic Toxicity (Ceriodaphnia) P/ F at 85 %. Samples shall be collected quarterly during the months of January, April, July and October. See Part A.(2.). 6 The quantitation limit for mercury shall be 0.2 ug/1 (0.2 ppb). Levels reported as less than 0.2 ug/1 shall be considered zero for compliance purposes. The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units. There shall be no discharge of floating solids or visible foam in other than trace amounts. Instream monitoring shall be in accord with the requirements specified in Part A.(3.), "Instream Monitoring Requirements." . Permit NCO036277 A. (2.) CHRONIC TOXICITY PERMIT LIMIT The effluent discharge shall at no time exhibit observable inhibition of reproduction or significant mortality to Ceriodaphnia dubia at an effluent concentration of 85%. The permit holder shall perform at a minimum, Quarterly monitoring using test procedures outlined in the "North Carolina Ceriodaphnia Chronic Effluent Bioassay Procedure," Revised February 1998, or subsequent versions or "North Carolina Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised -February 1998) or subsequent versions. The tests will be performed duri#g the months of January, April, July and October. Effluent sampling for this testing shall be performed at the NPDES permitted final effluent discharge below all treatment processes. If the test procedure performed as the first test of any single quarter results in a failure or ChV below the permit limit, then multiple -concentration testing shall be performed at a minimum, in each of the two following months ds described in "North Carolina Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised -February 1998) or subsequent versions. The chronic value for multiple concentration tests will be determined using the geometric mean of the highest concentration having no detectable impairment of reproduction or survival and the lowest concentration that does have a detectable impairment of reproduction or survival. The definition of "detectable impairment," collection methods, exposure regimes, and further statistical methods are specified in the "North Carolina Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised - February 1998) or subsequent versions. All toxicity testing results required as part of this permit condition will be entered on the Effluent Discharge Monitoring Form (MR-1) for the months in which tests were performed, using the parameter code TGP3B for the pass/fail results and THP3B for the Chronic Value. Additionally, DWQ Form AT-3 (original) is to be sent to the following address: Attention: North Carolina Division of Water Quality Environmental Sciences Branch 1621 Mail Service Center Raleigh, North Carolina 27699-1621 Completed Aquatic Toxicity Test Forms shall be filed with the Environmental Sciences Branch no later than 30 days after the end of the reporting period for which the report is made. Test data shall be complete, accurate, include all supporting chemical/physical measurements and all concentration/response data, and be certified by laboratory supervisor and ORC or approved designate signature. 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 Branch at the address cited above. Should the permittee fail to monitor during a month in which toxicity monitoring is required, monitoring will be required during the following month. Should any test data from this monitoring requirement 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. NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum control organism survival, minimum control organism reproduction, 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. Permit NCO036177 A.(3.) INSTREAM MONITORING REQUIREMENTS a In addition to the stream monitoring requirements specified in Part A. (1.), the permittee must monitor for the following between the months of April - October. Parameter Frequency/Type Location Chlorophyll -a Monthly/grab Downstream at Neck Road Total Phosphorus Monthly/grab Downstream at Neck Road NH3-N Monthly/grab Downstream at Neck Road TKN Monthly/grab Downstream at Neck Road NO2-NO3 Monthly/grab Downstream at Neck Road January 10. 2001 • CUt TL Ms. Natalie V. Sierra NCDENR — DWQ — NPDES Unit 1617 Mail Service Center Raleigh, North Carolina 27699-1617 Subject: McDowell Creek WWTP Permit Renewal NPDES Permit No. NCO036277 Dear Ms. Sierra: ui JAN 12 ?A01 �J I DEN R - WATER QUALITY POIi1T SOURCE BRANCH This is in response to your letter dated December 6, 2000, and received on December 12, 2000, concerning the renewal of the subject NPDES Permit. As directed by your letter, we are transmitting our comments within 30 days of our receipt of the letter and draft permit. We agree with your conclusions about cadmium, lead, and cyanide and concur with the removal of permit limits for these parameters. The cover letter states that the daily maximum limit for mercury will be 0.14 pg/I and the draft permit states it will be 0.0�14 a/I. Please clarify which is correct. 3. The draft permit includes increased instream monitoring requirements for chlorophyll -a, total phosphorus, NH3-N, TKN, and NO2-NO3 at Neck Road. At that \n point, the stream is very shallow and it is expected to be difficult to collect a rt(W" spatial composite sample (please confirm that composite in this instance does not Jmean a time composite). We also understand that there is no certification for chlorophyll -a analysis available through the NCDENR Laboratory ertification Program. Lzp-)1 3- 5&� (may�� _A Please note also that Mecklenburg County Department of Environmental Lo Protection (MCDEP) routinely conducts both stream and lake sampling across the county. Their routine sites include McDowell Creek at Neck Road and at Beatties Ford Road (upstream of the WWTP) and a lake site in McDowell Cove of Mountain Island Lake. Their routine sampling at the lake site includes chlorophyll - a, total phosphorus, NH3-N, TKN, nitrates and nitrites, secchi disk, and a number of other parameters. Their present sampling schedule is monthly except February, April, October, and December. MCDEP is also conducting an intensive sampling program to support development of a very detailed water quality model for the McDowell basin. Administration Division 5100 Brookshire Blvd. Charlotte, NC 28216 Phone: 704/399-2221 Fax: 704/393-2219 Charlotte -Mecklenburg Utilities We believe that the sampling and modeling conducted by MCDEP and the data base that they maintain would be adequate and available for DENR needs and request that section A.(3) be removed from the permit. 4. til It is requested that sampling frequency for in -stream samples other than those in section A.(3.) be reduced from three times per week during summer months to e once per week. Please revise the language concerning cyanide and mercury testing and reporting to reflect the discussions we have had about the same issues relative to the McAlpine Creek Permit. Specifically, the revision would recognize quantitation limits of 10 pg/I and 0.2 pg/I for cyanide and mercury respectively and would not require reporting numeric values less than these levels. Also, please confirm that laboratory methods using these quantitation levels will fulfill all permit covev- requirements and, that for all parameters, compliance with NCDENR Laboratory Certification Regulations meets the requirements for "adequate laboratory controls and appropriate quality assurance procedures." The draft permit adds a new monitoring requirement for silver. We have routinely sampled for this parameter for several years as part of our headworks analysis and have not detected any. Although we plan to continue to monitor for headworks purposes, we request that the twice per month sampling requirement be deleted from the permit. 5 , vG e - a, i 0') rS . lure 7. In our application for renewal, we requested that the permit allow a maximum monthly treatment rate of 7.6 mgd and an annual average daily rate of 6.0 mgd to recognize the design criteria and capabilities of the plant. Your letter states that an environmental assessment would be required to make this change. Please note that we are currently planning and designing an expansion of McDowell Creek. The permit requested for the expanse n and associated EA may request an interim rating based on this criteria. j�p�2o �j t;m 4� .� Notwithstanding basin -wide permitting schedules and our anticipated request for an expansion permit, we request that the permit be issued for a full five year tet rather than the proposed approximately four year period. tb . vvJu Voe. zt,C t IEOUA The plant description in the draft permit includes sludge thickening. Gravity belt sludge thickeners are under construction at this time but are not yet in-service. 10. It appears that we may have received the incorrect "boilerplate" sections for the McDowell Creek Permit. Particularly, Part I Section B and Part III would not �,.. appear to apply. If the corrected versions are different than those last issued, we ' request additional time to review and comment. 11. Please clarify that "daily" in the "Measurement Frequency" column of Section A.(1.) means five days per week excluding weekends and/or holidays." `AIL 12. We have discussed the proposed nickel limit by phone recently and have / submitted additional relevant information. Please review this additional information to determine if the nickel limit is necessary. Please let me know if you have any questions or need additional information. If you would like, we would be glad to meet with you to discuss any outstanding issues. Sincerely, CHARLOTTE MEJ)�( CKLLEENBURG UTILITIES r� d Barry M,� Gullet, PE Deputy Director C: Jackie Jarrell Pete Goins Myra Zabec Dawn Padgett Dave Goodrich Rex Gleason File - �e North Carolina } as Mecklenburg County} NCDENR/DWQ/BUDGET OFFICE ACCOUNTS PAYABLE 1617 MAIL SERVICE CENTER RALEIGH NC 27699-1617 The Knight Publishing Co., Inc. Charlotte, NC Affidavit of Publication THE CHARLOTTE OBSERVER +------------- ------- REFERENCE: 30019881 3917854 NPDES WASTEWARTER PE Before the undersigned, a Notary Public of said County and State, duly authorized to administer oaths affirmations, etc., personally appeared, being duly sworn or affirmed according to law, doth depose and say that he/she is a representative of the Knight Publishing Company a corporation organized and doing business under the laws of the State of Delaware, and publishing a newspaper known as The Charlotte Observer in the city of Charlotte, County of Mecklenburg and State of North Carolina and that as such he/she is familiar with the books, records, files and business of said Corporation and by reference to the files of said publication the attached advertisement was inserted. The following is correctly copied from the books and files of the aforesaid Corporation and Publication. PUBLISHED ON: 11/14 PUBLIC NOTICE STATE OF NORTH CANOLINA ENVIRONMENTAL MANAGEMENT COMMISSIONINPOE9 UNIT 1617 MAIL SERVICE CENTER RALEIGH, NC Y16941647 NOTIFICATION OF INTENT TO ISSUE A NPOES WAS EE AATCRER PER BIT AD SPACE: 100 LINE FILED ON: ll/15/001 ------- -------' -- --------------j/ } 7---------------------- NAME: �....... ,(„-41:-x. I L 4L'"� TITLE • / tC. / L�:eY /%,-. In Testimony Whereof I have hereunto set my hand and affixed my seal, the day and N aforesaid. Notary: ) Commission Expires:// Vo.16f DENR/DWQ FACT SHEET FOR NPDES PERMIT DEVELOPMENT NPDES No. NCO036277 Facility Information Applicant/Facility Name: Charlotte -Mecklenburg Utilities Department (CMUD) — McDowell Creek WWTP Applicant Address: 5100 Brookshire Blvd.; Charlotte, NC 28216 Facility Address: NCSR 2074, near the Town of Huntersville Permitted Flow 6.0 MGD Type of Waste: 85% Domestic 15% Industrial Facility/Permit Status: Class IV/Active; Renewal County: Mecklenburg County Miscellaneous Receiving Stream: McDowell Creek Regional Office: Mooresville Stream Classification: WS-IV State Grid / USGS Quad: F15NW/Lake Norman 303 d Listed? Yes Permit Writer: Natalie Sierra Subbasin: 03-08-33 Date: 7November00 Drainage Area (mi): 28.3 ^ Lat. 35022 52" N Long. 80° 56' 25" W Summer 7Q10 (cfs) 1.8 Winter 7Q10 (cfs): 4.2 30Q2 cfs Average Flow cfs): 31 IWC (%): 85 � BACKGROUND !??? McDowell Creek WWTP is one of the five Charlotte -Mecklenburg Utilities Department (CMUD) plants, regently expanded to a total design flow of 6.0 MGD. The facility serves the Town of Huntersv je, Town of Davidson, Town of Cornelius, and unincorporated areas of Mecklenburg County. In addition, the plant also accepts wastewater from 3 significant industrial users (SIUs) and as such, has a full Long Term Monitoring Program (LTMP) with the Pretreatment program. At the time of the last permit renewal, the facility had applied for an Authorization to Construct (ATC) that would allow for a plant expansion to 6.0 MGD along with other capital improvements. The 1995 permit was therefore a phased permit, setting limits for 3.0 MGD, interim flow of 3.5 MGD and the final 6.0-MGD flow. Construction on the plant expansion was completed in April 1999 and includes improvements to the headworks and the residuals management portions of the plant. Instream Monitoring and Verification of Existing Conditions and DMR Data Review. DMRs were reviewed beginning in January 1999 through August 2000. This period of time was selected since expansion was near finished at the beginning of 1999. Average flow during this time was 4.3 MGD. Dissolved Oxygen and Total Phosphorus instream data were analyzed for the permit renewal. Between Jan 1999 and August 2000, the dissolved oxygen (DO) values downstream of the discharge were above 6 mg/L on all but 5 summer sampling days. Downstream DO values were always above 5 mg/L both upstream and downstream of the discharge. Both upstream and Fact S,wl NPDES N00036277 Rcncwol Pagc I downstream DO measurements were below the saturation DO value for the measured temperatures. The average DO drop from upstream to downstream was 1.4 mg/L. Please see the attached plot of DO stream data for more information. Instream phosphorus data downstream of the discharge were also analyzed. Among 80 samples, 60 measured total phosphorus values below 0.1 mg/L. The remaining sampling points measured total phosphorus values at or below 1.0 mg/L. Low phosphorus loads are important given the close proximity to Mountain Island Lake downstream. CMUD-McDowell Creek monitors for a broad range of metals due to the large industrial contribution to its wastestream. Data from both the Pretreatment LTMP and the DMRs were used to assess reasonable potential for arsenic, cadmium, chromium, lead, copper, nickel, silver, zinc, cyanide, mercury, molybdenum, and selenium. Results of Reasonable Potential Analysis (RPA): A reasonable potential analysis (RPA) was performed for all monitored parameters. It was determined that there is reasonable potential for violations of instream standards of the following: • Copper • Nickel • Silver • Zinc • Mercury No reasonable potential exists for the following: • Arsenic • Cadmium • Chromium \ • Lead • Cyanide • Molybdenum • Selenium Copper, Silver, and zinc are all action level pollutants. Since CMUD —McDowell does not currently have toxicity problems, these compounds will be monitored only, not limited. The current NPDES permit does not limit nickel, so a limit will be added. Correspondence: The inspection reports generally reveal a well -run facility with few problems. There have been, however, several NOVs issued per year. The bulk of these have been for flow exceedences. The facility had one toxicity violation in 1999, but none since completion of the expansion. PERMITTING STRATEGY AND SUMMARY OF PROPOSED CHANGES The most recent basin plan for the Catawba River (December 1999) discusses the contribution of McDowell Creek WWTP to downstream impairment of both McDowell Creek and Mountain Island Lake. Nutrient loading upstream of Mountain Island Lake has been responsible for a eutrophic response in this lake. It is hoped that the recent improvements to McDowell Creek will reduce phosphorus loadings to the lake. Pact Sheet NPI)ES NCO036277 Renewal Page 2 Due to finding of reasonable potential, mercury and nickel will be limited in the NPDES permit. Cadmium, lead, and cyanide limits and monitoring will be eliminated from the NPDES permit, though they will continue to be monitored by the Pretreatment program. All the other parameters will remain the same in accordance with the previous permit and 1995 WLA. In that (as well as the current) permit, BOD, Total Suspended Residue, Total Nitrogen, fecal coliform, Total Phosphorus and mercury were all water quality limited parameters. We may wish to include upstream/downstream nutrient monitoring to assess the impact of the discharge on the receiving stream. CMUD-McDowell performs considerably less instream monitoring than McAlpine, Irwin, and Sugar Creek W WTPs. Pact Sheet NPDES NC0036277 Renewal Page 3 PROPOSED SCHEDULE FOR PERMIT ISSUANCE Draft Permit to Public Notice: Permit Scheduled to Issue: NPDES DIVISION CONTACT December 13, 2000 January 29, 2001 If you have questions regarding any of the above information or on the attached permit, please contact Natalie Sierra at (919) 733-5083 ext. 551. NAME: DATE: REGIONAL OFFICE COMMENTS ,fP/`2R-' i o /Ic o 3 6 Z X2 /1 c c S vBn�/7c�i� o -v M/3�j1 / 9' ,9— SA411� W 77G L /!/i% SG -� O O� ZZjt"�/^' - -- %q`G?S&- conif-�R/� 3 - cjAt t D6 /s A4i G�N,Tt�� /%u�/fy /s — �/n/.4L C�4�/Hir� S �R� L/s% �, �IG � a '� .✓ %f� / DATE: /—/ 7/ - Fact Sheet NPI)LS N00036277 Renewal Page 4 REASONABLE POTENTIAL ANALYSIS Prepared by: Natalie Sierra, 11/7/00 Facility Name = NPDES # _ Qw (MGD) _ Qw (cfs) = 7Q90s (cfs)= /WC (%) _ CMUD-McDowell Creek NC0036277 6 9.2832 1.8 83.78 Chronic CCC w/s7Q10 dil. Acute CMC w/no dil. Frequency of Detection Parameter FINAL RESULTS, ug/I FINAL RESULTS, ug/I #Samples # Detects Arsenic Max. Pred Cw 3.8 Allowable Cw 59.7 360 40 0 Cadmium Max. Pred Cw 1.1 Allowable Cw 2.4 15 83 2 Chromium Max. Pred Cw 30.9 Allowable Cw 59.7 1022 80 6 Lead Max. Pred Cw 19.2 Allowable Cw 29.8 34 81 7 Copper (A.L.) Max. Pred Cw 87.2 Allowable Cw 8.4 7.3 81 68 Nickel Max. Pred Cw 41.1 Allowable Cw 105.0 261 58 31 Silver (A.L.) Max. Pred Cw 26.7 Allowable Cw 0.1 1.2 81 5 Zinc (A.L.) Max. Pred Cw 262.3 Allowable Cw 59.7 67 81 77 Cyanide Max. Pred Cw 4.3 Allowable Cw 6.0 22 75 5 Mercury Max. Pred Cw 1.5 Allowable Cw 0.014 NA 42 3 Molybdenum Max. Pred Cw 27.6 Allowable Cw NA NA 41 8 Selenium Max. Pred Cw 3.8 Allowable Cw 6.0 20 41 1 Modified Data: Use 0.5 Detection Limit for non -detects nickel concentrations at McDowell Subject: nickel concentrations at McDowell Date: Thu, 4 Jan 2001 08:47:42 -0500 From: "Padgett, Dawn" <DPadgett@ci.charlotte.nc.us> To: "'natalie.sierra@ncmail.net"' <natalie.sierra@ncmail.net> CC: "Jarrell, Jackie" <JJarrell@ci.charlotte.nc.us>, "Gullet, Barry" <BGullet@ci.charlotte.nc.us>, "Zabec, Myra" <MZabec@ci.charlotte.nc.us>, "Goins, Pete" <PGoins@ci.charlotte.nc.us> Ms. Sierra, As we discussed in the phone conference 12/21, I have put together a letter of explanation about the high nickel results that may be biasing the RPA. I have the letter attached to this e-mail. The letter will also go out in the mail today. I believe that the rest of our comments on the proposed McDowell Creek Permit will go out at the beginning of next week. Thanks for you help with this, Dawn Padgett 704.391.5162 <<mcdowellnickel.doc>> Name: mcdowellnickel.doc Fimcdowellnickel.doc Type: Microsoft Word Document (application/msword) Encoding: base64 Download Status: Not downloaded with message 1 of 1 1 /4/01 1:23 PM • CHARLOITE January 4, 2001 Ms. Natalie Sierra NCDENR-DWQ-NPDES Unit 1617 Mail Center Drive Raleigh, NC 27699-1617 Dear Ms. Sierra, i JAN 11 2001 v. DENR - WA.ER QUALITY POINT SOURCE BRA.HCN As discussed in the conference call with you and Dave Goodrich last Wednesday 12/21/00, the nickel 1 PA done by you for McDowei: Creek W ffrP, NPvES Permit #NC0336277 may be biased due to analytical difficulties. Prior to 7/1/99, nickel analyses were conducted on an Atomic Absorption Spectrophotometer using flame ionization. The detection limit for that analytical method was 30ug/I, but there was significant background noise present at that detection limit, causing a potential for false positives. In July 1999, the analytical methodology was changed to the graphite furnace; which lowered the reportable detection limit to 5ug/I. Between July *1999 and February 2000, nickel was detected only 5 times. During that period, nickel was analyzed on a weekly basis and the highest detected nickel concentration was 19ug/l, on 9/27199. Since March 2000, the metals for the treatment plants have been analyzed using an ICP/MS. The new detection limit is Zug/I and nickel has been routinely detected in the effluent of the wastewater at very low levels. The highest detected concentration was 12ug/I on May 8, 2000. With the exception of a 5.7ug/I result, reported for May 30, 2000, all other detectable concentrations of nickel have been under 5ug/I. As you can see from these results, the amount of nickel in the effluent discharge from McDowell Creek WWTP is negligible. If you have any questions about this information, please give me a call at 704.391.5162, or you may e-mail me at dpadgett(a)ci.charlotte.nc.us. Thank you for your assistance. Respectfully, 4 K/cq�7� Dawn K. Padgett Environmental Management Division Cc: JJarrell BGullet MZabec PGoins Administrative Division 5100 Brookshire Blvd. Charlotte, NC 28216 Phone: 704/399-2221 Fax: 704/393-2219 Charlotte -Mecklenburg Utilities State of North Carolina Department of Environment and Natural Resources Division of Water Quality James B. Hunt, Jr., Governor Bill Holman, Secretary Kerr T. Stevens, Director December 8, 2000 MEMORANDUM A :: i� j NCDENR NORTH CAROLINA DEPARTMENT OF ENVIRONMENT AND NATURAL RESOURCES {v.t: vzeb. uk. ua VIW14MENT, HEAL' Tli • NATURAL RIBBWRGES To: Britt Setzer 15 NC DENR / DEH / Regional Engineer Mooresville Regional Office 9l109ilY�TAI YANA6�Fn +nnI1E91QtE @FAIflB@J '�+ From: Natalie Sierra NPDES Uni _ Subject: Review of Draft NPDES Permit NCO056277 I i CMUD McDowell Creek WWTP DEC 28 2000 =� Mecklenburg County Please indicate below your agency's position or viewpoint on the draft permit and returq AilssfUh7SmEI�E A January 8, 2000. If you have any questions on the draft permit, please contact me at the telephone number or e-mail address listed at the bottom of this page. RESPONSE: (Check one) Concur with the issuance of this permit provided the facility is operated and maintained properly, the stated effluent limits are met prior to discharge, and the discharge does not contravene the designated water quality standards. ❑ Concurs with issuance of the above permit, provided the following conditions are met: ❑ Opposes the issuance of the above permit, based on reasons stated below, or attached: 1617 Mail Service Center, Raleigh, North Carolina 27699-1617 919 733-5083, extension 538 (fax) 919 733-0719 Vlsn us ON THE INTERNET@ httpYth2o.encstate.nc.us/NPDES Christie.Jackson@ ncmail.nel DENR/DWQ • FACT SHEET FOR NPDES PERMIT DEVELOPMENT NPDES No. NCO036277 Facility Information pp ican aci ityName: Charlotte -Mecklenburg Utilities Department — McDowell Creek WWTP ApplicantAddress: 5 100 Brookshire Blvd.; Charlotte, NC 28216 FacilityAddress: NCSR 2074, near the Iown of Huntersville Permitted ow 7T MUD Type of Waite: o Domestic 15% Industrial Facility/PermitStatus: ClassIV/Active; Renewal ounty: Mecklenburg County Miscellaneous Receiving tream: McDowell CreekRegional ice: Mooresville tream Classification: WSAV State rid Quad: a e Norman tste es PermitWriter: Natalie Sierra u asin: - - ate: r7NovemberOO Drainage Area (mi ): 28.3 gx �� Lat. 350 22 52" N Long. 80° 56' 25" W Summer c s' Winter c s cs verageFlow c s : IWC° ' BACKGROUND McDowell Creek WWTP is one of the five Charlotte -Mecklenburg Utilities Department (CMUD) plants, recently expanded to a total design flow of 6.0 MGD. The facility serves the Town of Huntersville, Town of Davidson, Town of Cornelius, and unincorporated areas of Mecklenburg County. In addition, the plant also accepts wastewater from 3 significant industrial users (SIUs) and as such, has a full Long Term Monitoring Program (LTMP) with the Pretreatment program. At the time of the last permit renewal, the facility had applied for an Authorization to Construct (ATC) that would allow for a plant expansion to 6.0 MGD along with other capital improvements. The 1995 permit was therefore a phased permit, setting limits for 3.0 MGD, interim flow of 3.5 MGD and the final 6.0-MGD flow. Construction on the plant expansion was completed in April 1999 and includes improvements to the headworks and the residuals management portions of the plant. Instream Monitoring and Verification of Existing Conditions and DMR Data Review. DMRs were reviewed beginning in January 1999 through August 2000. This period of time was selected since expansion was near finished at the beginning of 1999. Average flow during this time was 4.3 MGD. Dissolved Oxygen and Total Phosphorus instream data were analyzed for the permit renewal. Between Jan 1999 and August 2000, the dissolved oxygen (DO) values downstream of the discharge were above 6 mg/L on all but 5 summer sampling days. Downstream DO values were always above 5 mg/L both upstream and downstream of the discharge. Both upstream and downstream DO measurements were below the saturation DO value for the measured temperatures. The average DO drop from upstream to downstream was 1.4 mg/L. Please see the attached plot of DO stream data for more information. Instream phosphorus data downstream of the discharge were also analyzed. Among 80 samples, 60 measured total phosphorus values below 0.1 mg/L. The remaining sampling points measured total phosphorus values at or below 1.0 mg/L. Low phosphorus loads are important given the close proximity to Mountain Island Lake downstream. Fact Sheet NPDES NCO036277 Renewal Page 1 • ' CMUD-McDowell Creek monitors for a broad range of metals due to the large industrial contribution to its wastestream. Data from both the Pretreatment LTMP and the DMRs were used to assess reasonable potential for arsenic, cadmium, chromium, lead, copper, nickel, silver, zinc, cyanide, mercury, molybdenum, and selenium. Results of Reasonable Potential Analysis (RPA): A reasonable potential analysis (RPA) was performed for all monitored parameters. It was determined that there is reasonable potential for violations of instream standards of the following: • Copper • Nickel • Silver • Zinc • Mercury No reasonable potential exists for the following: • Arsenic • Cadmium • Chromium • Lead • Cyanide • Molybdenum • Selenium Copper, Silver, and zinc are all action level pollutants. Since CMUD —McDowell does not currently have toxicity problems, these compounds will be monitored only, not limited. The current NPDES permit does not limit nickel, so a limit will be added. Correspondence: The inspection reports generally reveal a well -run facility with few problems. There have been, however, several NOVs issued per year. The bulk of these have been for flow exceedences. The facility had one toxicity violation in 1999, but none since completion of the expansion. PERMITTING STRATEGY AND SUMMARY OF PROPOSED CHANGES e most recent basin plan for the Catawba River (December 1discusses the contribution of McDowell Creek WWTP to downstream impairment of both McDowell Creek and Mountain Island Lake. Nutrient loading upstream of Mountain Island Lake has been responsible for a eutrophic response in this lake. It is hoped that the recent improvements to McDowell Creek will reduce phosphorus loadings to the lake. Due to finding of reasonable potential, mercury and nickel will be limited in the NPDES permit. Cadmium, lead, and cyanide limits and monitoring will be eliminated from the NPDES permit, though they will continue to be monitored by the Pretreatment program. All the other parameters will remain the same in accordance with the previous permit and 1995 WLA. In that (as well as the current) permit, BOD, Total Suspended Residue, Total Nitrogen, fecal coliform, Total Phosphorus and mercury were all water quality limited parameters. We may wish to include upstream/downstream nutrient monitoring to assess the impact of the discharge on the receiving stream. CMUD-McDowell performs considerably less instream monitoring than McAlpine, Irwin, and Sugar Creek WWTPs. Fact Sheet NPDES NCO036277 Renewal Page 2 PROPOSED SCHEDULE FOR PERMIT ISSUANCE Draft Permit to Public Notice: Permit Scheduled to Issue: NPDES DIVISION CONTACT December 13, 2000 January 29, 2001 If you have questions regarding any of the above information or on the attached permit, please contact Natalie Sierra at (919) 733-5083 ext. 551. NAME: REGIONAL OFFICE COMMENTS NAME: SUPERVISOR: DATE: DATE: DATE: Fact Sheet NPDES NCO036277 Renewal Page 3 Instream Dissolved Oxygen for McDowell Creek VOWP 16 14 12 Upstream DO —�- Downstream DO -�- Saturation DO 4 2 0 11 /1 /98 2/9/99 5/20/99 8/28/99 12/6/99 3/15/00 6/23/00 10/1 /00 Date 0 ov tom` REASONABLE POTENTIAL ANALYSIS Prepared by: Natalie Sierra, 11/7100 Facility Name = NPDES # _ Qw (MGD) _ Qw (cfs) _ 7Q10s (cfs)= / WC (%) _ CMUD-McDowell Creek NC0036277 6 9.2832 1.8 83.78 Chronic CCC w/s7Q10 dil. Acute CMC w/no dil. Frequency of Detection Parameter FINAL RESULTS, ug/I FINAL RESULTS, ug/I #Samples # Detects Arsenic Max. Pred Cw 3.8 t 1 Allowable Cw 59.7 360 40 0 idJ Cadmium / M�k Max. Pred Cw 1.1 Allowable Cw 2.4 15 83 2 Chromium Max. Pred Cw 30.9 Allowable Cw 59.7 1022 80 6 \ rGJ Lead ��. Max. Pred Cw 19.2 ^} Allowable Cw 29.8 34 81 7 j' Copper (A.L.) �� Max.ax. Pred Cw 7.2 ablePred Cw C8.4Z IMor�H 7.3 81 68 Nickel Max. Pred Cw �-L`l � 129.4 �21 MPJ Allowable Cw �0�' 105.0 OV-0 NG 261 75 39 Silver (A.L.) Max. Pred Cw 26.7T*4A,MXAllowable Cw 0.1 lo�� 1.2 81 5 Zinc (A.L.) Max. Pred Cw 262.3 �pw cT C Allowable Cw 59.7 2 1Mo tN—kAA 67 81 77 Cyanide Max. Pred Cw 4.3 Allowable Cw 6.0 22 75 5 Mercury Max. Pred Cw 1.5 Allowable Cw 0.014 NA 42 3 Molybdenum Max. Pred Cw 27.6 Allowable Cw NA NA 41 8 Selenium Max. Pred Cw 3.8 Allowable Cw 6.0 20 41 1 L)" 1T L v'rA y Parameter = Arsenic Standard = 50 pg/l Dataset= DMR99 Modified Data Nondetects RESULTS 2.5 <5 Std Dev. 0.756 1 <2 Mean 1.825 1 <2 C.V. 0.414 1 <2 Sample# 40.000 1 <2 1 <2 Mult Factor = 1.530 1 <2 Max. Value 2.500 pg/I 1 <2 Max. Pred Cw 3.825 pg/l 1 <2 Allowable Cw 59.677 pg/I 1 <2 1 <2.0 1 <2 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 Parameter = Cadmium Standard = 2 1 pg/l Dataset= DMR99 Modified Data Nondetects RESULTS 0.3 Std Dev. 0.059 0.5 <1 Mean 0.504 0.5 <1 C.V. 0.118 0.5 <1 Sample# 83.000 0.5 <1 0.5 <1 Mult Factor = 1.118 0.5 <1 Max. Value 1.000 pg/I 0.5 <1 Max. Pred Cw 1.118 pg/l 0.5 <1 Allowable Cw 2.387 pg/l 0.5 <1 0.5 <1 0.5 <1 0.5 <1 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 1 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 0.5 <1.0 i Parameter = IChromium Standard = 50 pg/l Dataset= DMR99 ModifiedData Nondetects RESULTS 6.3 Std Dev. 4.085 15 <30 Mean 3.854 1 <2 C.V. 1.060 15 <30 Sample# 80.000 15 <30 15 <30 Mult Factor = 2.060 15 <30 Max. Value 15.000 pg/l 1 <2 Max. Pred Cw 30.900 pg/l 1 <2 Allowable Cw 59.677 pgA 15 <30 6 5 15 <30 15 <30 1 <2 1 <2 11 1 <2.0 11 1 <2 2.5 <5 2.5 <5 2.5 <5 1 <2 2.5 <5 2.5 <5 5 2.5 <5 1 <2 2.5 <5 2.5 <5 2.5 <5 1 <2 2.5 <5 2.5 <5 2.5 <5 2.5 <5 1 <2 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 1 <2.0 2.5 <5 2.5 <5 1 <2.0 2.5 <5 2.5 <5 2.5 <5 Parameter = Lead Standard = Dataset= DMR99 ModifiedData Nondetects RESULTS 3.6 Std Dev. 1.786 2.5 <5 Mean 2.767 1 <2 C.V. 0.646 2.5 <5 Sample# 81.000 2.5 <5 2.5 <5 Mult Factor 2.5 <5 Max. Value 11.000 pg/l 1 <2 Max. Pred Cw 19.206 pg/l 1 <2 Allowable Cw 29.839 pg/I 2.5 <5 11 5 2.5 <5 2.5 <5 1 <2 1 <2 8 2.5 <5 2.5 <5 4 2.5 <5 2.5 <5 10 2.5 <5 1 <2 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 1 <2 2.5 <5 2.5 <5 1 <2 2.5 <5 2.5 <5 O Parameter= Copper(A.L.) Standard = 1 7 pg/l Dataset= DMR99 (12/99-8/99) ModifiedData Nondetects RESULTS 30 Std Dev. 9.289 3 Mean 11.926 15 <30 C.V. 0.779 15 <30 Sample# 81.000 15 <30 15 <30 Mult Factor = 1.779 2 Max. Value 49.000 pg/l 15 <30 Max. Pred Cw 87.171 pg/I 15 <30 Allowable Cw 8.355 pg/l 15 <30 41 41 15 <30 15 <30 7 6 49 15 <30 15 <30 6 15 <30 15 <30 40 11 8 10 5 12 16 11 6 11 5 7 4 6 3 9 11 37 7 12 8 8 10 3 6 17 8 15 3 3 Parameter = Nickel Standard = 88d pg/l Dataset= DMR99 12/99-4/99 ModifiedData Nondetects RESULTS 3 Std Dev. 10.843 46 Mean 6.827 <2 C.V. 1.588 36 Sample# 75.000 37 15 <30 Mult Factor 15 <30 Max. Value 50.000 pg/l 1 <2 Max. Pred Cw 129.400 pg/l 15 <30 Allowable Cw 105.032 pg/l 15 <30 4 3 48 50 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2 2.5 <5 2.5 <5 3 2.5 <5 2.5 <5 1 <2 2.5 <5 19 18 3 2.5 <5 11 2.5 <5 1 <2 2.5 <5 2.5 <5 10 2.5 <5 2.5 <5 1 <2 2.5 <5 2.5 <5 5 2.5 <5 1 <2 18 2.5 <5 1 <2 2.5 <5 2.5 <5 2.5 <5 2.5 <5 Standard = ( 0,06 J µgA Dataset= DMR99 ModifiedDate Nondetects RESULTS 9 Std Dev. 6.330 15 <30 Mean 8.148 1 <2 C.V. 0.777 15 <30 Sample# 81.000 15 <30 15 <30 15 <30 1 <2 15 <30 15 <30 7 7 15 <30 15 <30 1 <2.0 1 <2.0 9 15 <30 15 <30 1 <2.0 15 <30 15 <30 6 15 <30 15 <30 1 <2 15 <30 15 <30 15 <30 1 <2 15 <30 15 <30 15 <30 1 <2 15 <30 15 <30 15 <30 15 <30 15 <30 1 <2 15 <30 15 <30 15 <30 1 <2 15 <30 15 <30 15 <30 1 <2 15 <30 15 <30 15 <30 15 <30 2.5 <5 1 <2.0 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.6 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 Mutt Factor = 1.777 Max. Value 15.000 µgA Max. Pred Cw 26.655 µgA Allowable Cw 0.072 µgA Parameter = Zinc (A.L.) Standard = 50 µgA Dataset= DMR99 (12/99-111") ModifiedData Nondetects RESULTS 97 Std Dev. 32.750 40 Mean 60.309 38 C.V. 0.543 46 Sample# 81.000 41 39 Mutt Factor 59 Max. Value 170.000 25 Max, Pred Cw 262.310 61 Allowable Cw 59.677 63 120 120 54 59 48 47 130 15 <30 40 36 36 36 170 31 37 37 15 <30 15 <30 41 62 60 48 57 45 53 58 64 67 76 71 43 87 15 <30 60 53 54 38 81 118 63 144 104 87 120 140 50 78 59 49 120 130 110 40 49 49 57 71 34 41 37 40 41 41 44 36 49 40 35 50 34 37 Parameter = Standard = Dataset= ModifiedData Nondetects 1.25 <2.5 2 2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 <2 <2.0 2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2.0 1 <2.0 1 <2.0 1 <2.0 3 1 <2.0 3 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 2.5 <5 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 1 <2.0 3 1 <2.0 1 <2.0 1 <2.0 1 <2.0 3 1 <2.0 1 <2.0 1 <2.0 1 <2.0 pgA RESULTS Std Dev. 0.509 Mean 1.170 C.V. 0.435 Sampled 75.000 Mult Factor = 1.435 Max. Value 3.000 pg/l Max. Pred Cw 4.305 pg/l Allowable Cw 5.968 pg/l Parameter = Standard = Dataset= ModMedData Nondetects 0.3 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.7 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.20 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 0.1 <0.2 RESULTS Std Dev. 0.098 Mean 0.121 C.V. 0.804 Sampled 42.000 Mult Factor = 2.200 Max. Value 0.700 pg/l Max. Pred Cw 1.540 pg/l Allowable Cw 0.014 pgA s Parameter = Molybdenum Standard = I Ng/l Dataset= DMR99 ModifiedData Nondetects RESULTS 3.6 Std Dev. 3.198 5 <10 Mean 4.663 10 C.V. 0.686 5 <10 Sample# 41.000 5 <10 12 Mult Factor = 1.970 14 Max. Value 14.000 pg/l 14 Max. Pred Cw 27.580 pg/l 5 <10 Allowable Cw 0.000 Ng/l j 5 <10 5 <10 11 5 <10 5 <10 5 <10 5 <10 5 <10 5 <10 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 7.1 7 2.5 <5 2.5 <5 2.5 <5 Parameter = Selenium Standard = 5 pg/l Dataset= DMR99 ModifiedData Nondetects RESULTS 0.3 Std Dev. 0.776 1 <2 Mean 1.861 1 <2 C.V. 0.417 1 <2 Sample# 41.000 1 <2 1 <2.0 Mult Factor 1 <2.0 Max. Value 2.500 1 <2.0 Max. Pred Cw 3.825 1 <2.0 Allowable Cw 5.968 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2 1 <2.0 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 2.5 <5 N c C 0 � r . '6!YJ 2, -D sc a fl �-, �C+ W S-1\J C� wA I'N C) Qoc- SS — 2 hnec-vn �a� scrRS o :?), SW s -P(2- C T X . 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P 'S c� h�lE (` CPllyv y�C.l Ll� -rjA W VyA-, --rb VYj OF ` " v II�SUN lh&l.L 5?,E 1�E—�112EZ-re71� rU I..GUZy i2t vev2 I N 200 'Fi bS i YZQ�-rvT wLA 19qs hg 3A S--� -)�), u cc-S w\d�-�tqI U `t Z �S-S 86 `a To Ot-( S -La, I tib US 1- c,� E-= 1� s � -�►',-�.! l C�� � � � , �. ��� .- �y sew > > � � u� , � '3 Tuw �xee `v • IrJ 1Q1` -mhr KaA-c �em21t Vap�p �CAI AA45 a t -vt>x Y � C) I . t°I`t rJ C l use via I 2 lo'D .n of `11icy z -� 0 NUS MP (It rati:- ., VLLt p�� r "W'.j 0'/-t/0 NPDES/Non-Discharge Permitting Unit Pretreatment Information Request Form NPDES OR NONDISCHARGE PERMITTING UNIT COMPLETES THIS PART: Date of Request 11 /6/00 Facility CMUD-McDowell Creek Permit # NCO036277 Region Mooresville Requestor Natalie Sierra Pretreatment A D Towns- Keyes McGee (ext. 580) Contact E-L Towns- Vacant Position M-R Towns- Dana Folley (ext. 523) S-Z Towns- Steve Amigone (ext 592) PRETREATMENT UNIT COMPLETES THIS PART: Status of Pretreatment Program (circle all that apply) 1) the facility has no SIU's and does have a Division approved Pretreatment Program that isINACTIVE 2) the facility has no SIU's and does not have a Division approved Pretreatment Program 3) the facility has (or is developing) a Pretreatment Program a) is Full Program with or 2b) is Modified Program with STMP 4 the facility MUST develop a Pretreatment Program - Full Modified 5) additional conditions regarding Pretreatment attached or listed below Flow Permitted Actual v STMP time fran e• % most recent u�A Industrial D • D S t7 D 2 `0 % Domestic �q - 0next cycle L Pollutant T Check List POC due to M NPDES/Non- STMP LTMP Discharge Required Required by Frequency at Frequency at P Permit Limit by EPA* 503 Sludge" POC due to SIU"' Site specific POC (Provide Explanation)••" effluent effluent BOD 4 Q M TSS 4 Q M NH3 4 Q M Arsenic 4 Q M Cadmium 4 Q M Chromium V 4 Q M Copper 4 Q 'M Cyanide 4 Q M 4JILead 4 Q M Mercury 4 Q M Molybdemum 4 Q M Nickel., 4 Q M Silver 4 Q M Selenium 4 Q M zinc 4 Q M itro 4 Q M o' uS 4 Q M 4 Q M 4 Q M 4 Q M 4 Q M 'Always in the LTMP "Only in the LTMP if the POTW land applies sludge Only in LTMP while the SIU is connected to the POTW "" Only in LTMP when the pollutant is a specific concem to the POTW (le -Chloride to a POTW who accepts Textile waste) 0= Ouarterly M=Monthly Comments: 5&f E M ATL FOY a eT 00% P ♦ w v-v- ".- wA- i ova . NPDES_PIRFform.000804.As Revised: August 4, 2000 Percent of Industrial Flow to Total Facility Flow NPDES # of all POTW Total Design Flow Total Actual Flow Industrial Flow Treatment Plants Receiving (Daily Average-MGD) (Daily Average-MGD) Recived Industrial Wastewater FY 2000 FY 2000 % of Actual FY 2000 Irwin Creek - NC0034945 15 10.184 11.83% Mallard Creek - NC0030210 8 5.587 0.20% McAlpine Creek - NC0024970 48 40.132 5.37% McDowell Creek - NC0036277 6 4.476 0.02% Sugar Creek - NC0024937 20 15.253 5.78% Industrial Users per Facility NPDES # of Major POTW's Number of Categorical Number of Significant Total Industrial Users (CIU's) Non -Categorical Industrial Users Irwin Creek- NC0034945 10 19 29 Mallard Creek - NC0030210 2 2 McAlpine Creek - NC0024970 10 30 40 McDowell Creek - NC0036277 1 1 Sugar Creek - NC0024937 11 14 25 Total 34 63 97 McDowell Creek Wastewater Treatment Plant NPDES Permit # NCO036277 Headworks Long Term Monitoring Plan Activated Sludge/Anaerobic Digester with Land Application of Biosolids A. Sampling Points (See Figure 1) 1. Influent 2. Effluent (after disinfection) 3. Primary Clarifier Influent @ DB 1 4. Primary Clarifier Effluent @ DB4 5. Final clarifier influent /Aeration Effluent @ DB9 6. Final clarifier effluent @ overflow out of final clarifier #2 (both final clarifier 1 & 2 discharge @ this point) 7. Sludge to digester @ digester influent (hand comp/ 3 grabs per shift) 8. Sludge to drying beds or filter press @ digester effluent (hand comp/3 grabs per shift) 9. Filter Press Filtrate (hand comp/3 grabs per shift) 10. Residuals Cake, off filter press and/or sludge drying beds 11. Permitted SIU a. There is one categorical SIU permitted to discharge to the McDowell Creek WWTP. The Charlotte - Mecklenburg Utilities -Industrial Waste Pretreatment Program (CMU-IWPP) permit to this facility identifies both location and frequency for monitoring. *B. Pollutants of Concern (P.O.C.) 1. Biochemical Oxygen Demand, Chemical Oxygen Demand, Total Suspended Solids, Oil and Grease, Ammonia -Nitrogen, Total Nitrogen (Total Kjeldahl Nitrogen and Nitrate and Nitrite), Total Phosphorus, Arsenic, Cadmium, Chromium, Copper, Lead, Mercury, Molybdenum, Nickel, Selenium, Silver, Zinc, Cyanide and percent solids of the sludge. C. Flow 1. Wastewater treatment plant (as measured at the location indicated in the enclosed diagram) 2. Sludge to disposal Flow will be calculated. D. SIU Monitoring 1. To be conducted as indicated in the permit. a. The Permittee is required to self -monitor at least four days every three months. b. Charlotte -Mecklenburg Utilities, System Protection Division monitors all SIU's at a minimum of four days every quarter (i.e. Jan.- Mar., Apr. - Jun.). 'F. Sampling Frequency For P.O.C. Sampling Point First Three Months Thereafter 1. Influent Monthly for an entire 7-day week and per NPDES requirements Monthly on alternating days of the week and per NPDES requirements 2. Effluent Monthly for an entire 7-day week and per NPDES requirements Monthly on alternating days of the week and per NPDES requirements 3. Primary Clarifier Influent Monthly for an entire 7-day week Monthly on alternating days of the week 4. Primary Clarifier Effluent Monthly for an entire 7-day week Monthly on alternating days of the week 5. Aeration effluent Monthly for an entire 7-day week Monthly on alternating days of the week 6. Final clarifier effluent Monthly for an entire 7-day week Monthly on alternating days of the week 7. Sludge to Digester Monthly for and entire 7-day week and er slud a permit and 503 regulations. Monthly on alternating days of the week and per sludge regulations 8. Sludge to drying beds or filter press Monthly for an entire 7-day week and per sludge permit and 503 regulations Monthly on alternating days of the week and per sludge regulations 9. Supernate out of the anaerobic digester or filter press filtrate Monthly for an entire 7-day week Monthly, on alternating days of the week 10. Residuals Cake Monthly for an entire 7-day week and per sludge permit and 503 regulations Monthly on alternating days of the week and per sludge regulations 11. Waste Activated Sludge Monthly for an entire 7-day week Monthly on alternating days of the week 12. SIU Per SIU Permit Per SIU Permit `G. Sampling Plan P. O. C. Pt. 1 Pt. 2 Pt. 3 Pt. 4 Pt. 5 Pt. 6 Pt. 7 Pt. 8 Pt. 9 Pt. 10 BOD x x x x x x COD X X X X X X TSS x x x x x x O&G X X X X NHYN x x x x x x Total Nitrogen x x x x x x x x x Total Phosphorus x x x x x x x x x As* x x x x x x x x x x Cd x x x x x x x x x x Cr x x x x x x x x x x Cu x x x x x x x x x x Pb x x x x x x x x x x Hg* x x x x x x x x x x Mo* x x x x x x x x x x Ni x x x x x x x x x x Se x x x x x x x x x x Ag x x x x x x x x x x Zn x x x x x x x x x x CN x x x x % solids x x x Flow x x x x H. Detection level and Sample Method P. O. C. Detection Level (m 1) Sam le Method BOD 2 24 hr Composite COD 50 24 hr Composite TSS 2 24 hr Composite NH3 0.1 24 hr Composite As 0.01 24 hr Composite Cd 0.002 24 hr Composite Cr 0.005 24 hr Composite Cu 0.002 24 hr Composite Pb 0.01 24 hr Composite Hg 0.0002 24 hr Composite Mo 0.1 24 hr Composite Ni 0.01 24 hr Composite Se 0.01 24 hr Composite Ag 0.005 24 hr Composite Zn 0.01 24 hr Composite CN 0.01 Grab Sampling, Preservation and analytical methods will conform with 40 CFR 136 requirements. RE: McDowell Creek WWTP Phase III Improvements Contract 2 -Quest ions C�YwI - Ncoo 3& Z77 Subject: RE: McDowell Creek WWTP Phase III Improvements Contract 2 - Quest ions Date: Mon, 16, Oct 2000 07:11:01 -0500 From: "Parker, David M. (Dave)" <ParkerDM@bv.com> To: "Becker, Maggie A." <BeckerMA@bv.com>, "Susan Wilson @ NC-DWQ" <susan.a.wilson @ncmail.net> Susan, The engineer's certification for the expansion to 6 mgd was sent to Dave Goodrich on April 28, 1999. The Authorization to Construct could be sent to either Doug Bean (Director) or Barry Gullet (Deputy Director). I think the last one we received was officially addressed to Doug Bean. Either way, can you please copy us also? Thanks for your help on this. David M. Parker, P.E. Black & Veatch 8604 Cliff Cameron Drive, Suite 164 Charlotte, North Carolina 28269 * Phone: (704) 510-8438 * Fax: (704) 548-8640 * E-mail: ParkerDM@bv.com > -----Original Message ----- > From: Becker, Maggie A. > Sent: Friday, October 13, 2000 5:21 PM > To: Parker, David M. (Dave) > Subject: FW: McDowell Creek WWTP Phase III Improvements Contract 2 - > Questions > Hi, Dave. Susan is asking questions that I don't have answers to - help! > -----Original Message ----- > From: Susan Wilson[SMTP:susan.a.wilson@ncmail.net] > Sent: Friday, October 13, 2000 4 : 41 PM > To: Becker, Maggie A. > Subject: Re: McDowell Creek WWTP Phase III Improvements Contract 2 - > Questions > Maggie, > Thanks for the info. Also, excuse my ignorance on this, but have you > ( they) > submitted their Engineer's Certification for completion of the project up > to 6 > MGD? I have some correspondence that indicates that they're at 6 MGD, but > I'm > not positive we've received the certification. > Is Mr. Bean the primary contact for an Authorization to Construct permit > letter? I know he's the contact for their NPDES permit, but didn't know > if he, > Barry or someone else was more appropriate for this letter. Thanks. I > was > hoping to get this out shortly after your response - but it should be > definitely out Monday (and I'll sign it today). > Have a great weekend. > "Becker, Maggie A." wrote: 1 of 2 10/16/00 9:58 AM RE: McDowell Creek WWTP Phase III Improvements Contract 2 - Quest ions • ` s > > > Hi, Susan. I have listed below the information you requested on Oct. 6, > > 2000. > > * The existing influent pumps have the following capacities: > > IP-2 3,150 gpm > > IP-3 2,900 gpm > > IP-4 2,900 gpm > > IP-5 3,150 gpm > > (Existing IP-1 is currently 600 gpm and will be replaced with a > > 3,150 gpm pump) > > * The loading rate for the dewatering system (including both > BFP's) > > under normal operating conditions is 600 lb/meter of belt/hour. The > system > > will operate in the range of 300 to 1000 lb/meter of belt/hour. > > Please let me know if you have any other questions! > > Maggie A. Becker > > Black & Veatch > > 8604 Cliff Cameron Drive, Suite 164 > > Charlotte, North Carolina 28269 > > * Phone: (704) 510-8439 > > * Fax: (704) 548-8640 > > * E-mail: beckerma@bv.com 2 of 2 10/16/00 9:58 AM SOC Priority Project: No To: Permits and Engineering Unit Water Quality Section Attention: Charles Weaver Date: August 24, 2000 NPDES STAFF REPORT AND RECOMMENDATION County: Mecklenburg MRO No.: 00-57 Permit No. NCO036277 PART I - GENERAL INFORMATION Facility and Address: Charlotte Mecklenburg Utilities McDowell Creek WWTP 5100 Brookshire Boulevard Charlotte, North Carolina 28216 2. Date of Investigation: 6-20-2000 3. Report Prepared by: Samar Bou-Ghazale, Env. Engineer I 4. Persons Contacted and Telephone Number: Ms. Maggie Becker with Black & Veatch, (704) 548- 8461 5. Directions to Site: From the intersection of SR 2128 (Beatties Ford Road) and SR 2074 (Neck Road), travel west on SR 2074 approximately 1.9 miles. The W WTP is located on the right side of SR 2074 after crossing McDowell Creek. R1 9 a Discharge Point(s), List for all discharge points: Latitude: 350 22' 52" Longitude: 80° 56' 25" Attach a USGS map extract and indicate treatment facility site and discharge point on map. U.S.G.S. Quad No.: F15NW U.S.G.S. Quad Name: Lake Norman South, NC Site size and expansion area consistent with application? Yes. Topography (relationship to flood plain included): Slopes range from 2 to 4%, the W WTP is not in a flood plain. Location of nearest dwelling: None within 1000 feet. 10. Receiving stream or affected surface waters: McDowell Creek ^ III AUG 2 8 2000 OENR - W.AH OURLITY POINT SOURCE H;PNCN Rage Two a. Classification: WS-IV CA b. River Basin and Subbasin No.: Catawba 030833 C. Describe receiving stream features and pertinent downstream uses: Receiving stream is approximately 20 feet wide x 3-5 feet deep. A CMU water intake is located a few miles downstream on Mountain Island Lake. The lake is used for primary and secondary recreation as well as water supply source. PART II - DESCRIPTION OF DISCHARGE AND TREATMENT WORKS 1. a. Volume of wastewater to be permitted: 6.0 MGD (ultimate design capacity) b. Current permitted capacity of the wastewater treatment facility: 6.0 MGD C. Actual treatment capacity of the current facility (current design capacity): 6.0 MGD d. Date(s) and construction activities allowed by previous Authorizations to Construct issued in the previous two years: N/A e. Please provide a description of existing or substantially constructed wastewater treatment facilities: The existing WWT facilities consist of two mechanical bar screens, grit removal, influent pumping, three (3) primary clarifiers, two parallel BNR systems consisting of Oxic/Anoxic zones, two (2) final clarifiers, four (4) tertiary filters, 4 anaerobic sludge digesters and ultra -violet disinfection. f. Please provide a description of proposed wastewater treatment facilities: Two applications for Authorizations to Construct were submitted for construction at the subject facility. The first Authorization application (AC036277) was submitted on December 14, 1999 for the following additions: a) The conversion of an abandoned clarifier to a waste activated sludge storage tank. b) Gravity belt thickeners. c) The enclosure of outdoor blowers. d) The construction of a filtrate equalization basin and other upgrades to comply with electrical requirements for wastewater treatment facilities. The second application (AC036277ACC) was submitted on May 18, 2000 for the following additions: Two belt filter presses, a polymer feed system, a dewatered sludge conveyor, a filtrate equalization pumping station, and a biosolids storage basin; and miscellaneous improvements to the headworks structure, influent pumping station, final clarifiers, effluent filters and UV disinfection. g. Possible toxic impacts to surface waters: This facility has a good compliance history with toxicity testing results. h. Pretreatment Program (POTWs only): CMU has an approved pretreatment program. Page Three There are 3 significant industrial users permitted to discharge process wastewater to the WWTP. 2. Residuals handling and utilization/disposal scheme: a. Residuals are land applied. DWQ Permit No. WQ0000057. Residuals Contractor: BioGro, Inc. Telephone No.: (704) 542-0937. b. Residuals stabilization: PSRP C. Landfill: Waste from the grit chamber and bar screen are taken to Mecklenburg County landfill. 3. Treatment plant classification: Class IV 4. SIC Code(s): 4952 Wastewater Code(s) 01 Main Treatment Unit Code: 11113 5. Other Special Items: N/A PART III - OTHER PERTINENT INFORMATION 1. Is this facility being constructed with Construction Grant Funds or are any public monies involved (municipals only)? Public monies 2. Special monitoring or limitations (including toxicity) requests: None at this time. 3. Important SOC, JOC or Compliance Schedule dates (Please indicate): N/A 4. Alternative Analysis Evaluation: N/A 5. Air quality and/or groundwater concerns or hazardous materials utilized at this facility that may impact water quality, air quality, or groundwater: No AQ or GW concerns nor are hazardous materials utilized at this facility. PART IV - EVALUATION AND RECOMMENDATIONS The permittee, Charlotte -Mecklenburg Utilities, has applied for Permit renewal for the subject facility. The WWTP appeared in good operational condition at the time of the investigation. CMU requests the following changes: 1-Modify the whole effluent chronic toxicity provisions to reflect DENR's modifications described in an August 26, 1999, letter from Matt Mattews, Aquatic Toxicology Unit Supervisor, to Utilities Director Douglas Bean. Page Four 2- Allow a discharge of up to 6.0 mgd of effluent into Mcdowell Creek on an annual average basis with no single monthly average to exceed 7.6 mgd. 3- mass -based limits in lieu of concentration based requirements if request 2 above has not been granted. It should be noted that the chronic toxicity testing procedures mentioned above will be automatically implemented for all permits. The modeling group should provide comments regarding mass -based versus concentration based limits. The existing permitted flow is 6.0 mgd (monthly average). CMU is proposing to exceed 80/90% of the permitted discharge per request 2 above. A review of DMR' S for 6/99 thru 5/00 indicates that the effluent quality for this facility is excellent and, therefore, exceeding the design capacity during some months should not significantly degrade effluent quality. It is recommended that request (2) above be granted provided that CMU comply with 80/90% capacity policy. Pending review and approval by P& E, it is recommended that the permit be renewed. C l �Oki) � � ell. pct-A pro t a'0V..awPi' VA t,1� Ik VIA 41 ,Ali V ✓ � 100 1( � Water Quality ional Supervisor ate NOTES TO FILE 10/5/00 '� bn/ `*�o CMU/ McDowell Creek NCO036277 Current Limits: PF = 6 MGD, BOD5 = 5, NH3-N = 1 , Fecal coliform = 200#/ 100 ml, TR C1= 17 Proposed Units Capacity Design Load Peak Load Other Comments Mech. Bar 1 in. screens, 3 ` 17.6 mgd Should have - 3 ft/s based screen wide 3 ' depth min. vel of 2- on 17.6 MGD 3.25 ft/s OK - per M&E, . 448 Influent pump (1 3150 gpm = 5 influent Great (~3.7 x of 3) 4.5mgd 112 ft pumps design flow) TDH 15,250 gpm = 22 MGD Effluent trough N/A covers Filter no. 5 (for 5 9.5' x 53' 1.7 gpm/ft2 4.9 gpm/ft2 Design and peak OK, of 5) SA = 504 ` flow = 17.6 mgd using all cells M&E p. 676-678 Deep bed - 504*5 = 2520 SA=2500 ft2 Range - 2-10 denitrification gpm filters Depth - 72" Flow rates lower with deep bed UV disnfection 24.5'x32x86 in. Designed for 18 3 new OK New channel 6 mgd peak flow modules/chann Ref. specs modules/chann with a 3 el being added performance el; 40 channels to 1 &2 guarantee lamps/module operational 6*3*40 = 720 12 new modules Spec'd to meet lamps added 200/400 fecal specs p. 13700 coliform Proposed Units Capacity Design Load Peak Load Other Comments Digester 3 primary 48,000 gpd 68,000 gpd OK, plenty of reconflg. digester (sludge flow - (sludge flow - storage capacity 1 secondary annual avg) monthly max) (see talcs. Dia = 55' @3% TS @3% TS below) SAO = 27' Also, 503s Vol = 139,000 reviewed with ft3 any land = 2@ 1 MG app/composting = 2@ 0.5 permits MG Belt filter 2m Sludge/annual Avg. load = Typical rates: OK presses 20% dry solids - avg= 600 lb/m*hr 200-1500 M&E p.866 - reserved area dewatered 7816+4130+752 lb/m*hr for 3 Influent 7 = 2*600*2 flow=100 gpm = 19473 Ibs/day 2400 lb/hr hydraulic: = 811 lbs/hr 25-100 gpm/m Max. month= Reported range 10891 +6150+ 10 = 300 - 1000 438 lb/m*hr = 27479 lbs/day = 1145 lbs/hr Filtrate EQ Submersible OK - can be pump station @500 gpm each controlled 3 pumps 64' TDH Biosolids storage Est. 30 day ad w/roof storage capacity - all floor drains from belt filter area and biosolids storage diverted back to filtrate EQ Sludge digestion/storage: At 6 MGD, assume BOD in = 220 mg/1, BOD out = 5 mg/l, 0.77 lbs sludge/# BOD5 6.0 * 8.34 * 215 * 0.77 = 8284 lbs sludge/day At 3% solids, 8284/(0.03*8.34) = 33,110 gal/day sludge produced For 30 day capacity, need at least 33,110 gal/day * 30 days = 993,300 gallons storage (easily met at least through secondary digesters and even more so after belt presses). McDowell Creek WWTP Phase III Improvements Contract 2 - Questions ` Subject: McDowell Creek WWTP Phase III Improvements Contract 2 - Questions Date: Tue, 10 Oct 2000 09:26:47 -0500 From: "Becker, Maggie A." <BeckerMA@bv.com> To: Susan Wilson <susan.a.wilson @ncmail.net> Hi, Susan. I have listed below the information you requested on Oct. 6, 2000. * The existing influent pumps have the following capacities: IP-2 3,150 gpm IP-3 2,900 gpm IP-4 2,900 gpm IP-5 3,150 gpm (Existing IP-1 is currently 600 gpm and will be replaced with a 3,150 gpm pump) * The loading rate for the dewatering system (including both BFP's) under normal operating conditions is 600 lb/meter of belt/hour. The system will operate in the range of 300 to 1000 lb/meter of belt/hour. Please let me know if you have any other questions! Maggie A. Becker Black & Veatch 8604 Cliff Cameron Drive, Suite 164 Charlotte, North Carolina 28269 * Phone: (704) 510-8439 * Fax: (704) 548-8640 * E-mail: beckerma@bv.com 1 of 1 10/10/00 11:06 AM February 22, 2000 Note to File Subject Sites: Sugar Creek WWTP Irwin Creek WWTP McAlpine Creek WWTP Mallard Creek WWTP McDowell Creek WWTP NPDES PERMIT NCO024937 NPDES PERMIT NCO024945 NPDES PERMIT NCO024970 NPDES PERMIT NCO030210 NPDES PERMIT NCO036277 RE: Application of 1/2 FAV Calculation to the Subject Sites Joe has revised Maximum Daily Load effluent limits for only those parameters where values increased (i.e. became less stringent) applying the latest 1/2 FAV calculations (see Sue Wilson's memo dated January 2, 2000). Because this was "a minor mod at the request of the permittee for revision of cyanide only," parameter values that would have become more stringent, were not upgraded (per Dave Goodrich). Therefore upon renewal of these permits, the next permit writer must upgrade the other Daily Maximum parameters to the latest calculations. Joe Corporon NPDES Unit cc. to each subject permit file Division of Water Quality August 5, 1999 MEMORANDUM TO: Dave Goodrich THROUGH: Matt Matthews f^fj� FROM: Kristie Robeson VP — SUBJECT: NPDES Permit Modifications Revised Chronic Toxicity Language Due to recent discussions with EPA Region IV, the Division is further modifying its Whole Effluent Toxicity Enforcement Policy. Therefore, the -chronic toxicity language to be used in permits will once again change. Listed below are the nine facilities that currently have a Phase H chronic toxicity testing requirement in their NPDES permits. Our office previously sent you a memo dated 5/10/99 requesting modification of these nine permits to include the new chronic toxicity language. However, through discussions with EPA, our office was told that they would not approve permits which contained that toxicity language. The chronic language has since been revised and approved by EPA Region IV. Our office now recommends modifying the permits for the nine facilities listed below to include the revised permit language for chronic toxicity testing. CMUD-McAlpine WWTP NPDES Permit No. NC0024970 Mecklenburg County CMUD-Mallard Creek WWTP NPDES Permit No. NC0030210 Mecklenburg County CMUD-McDowell Creek WWTP NPDES Permit No. NC0036277 ;1 Mecklenburg County Concord Rocky River WWTP NPDES Permit No. NC0036269 Cabarrus County Delta Mills NPDES Permit No. NC0006190 Catawba County Duke Power -Lincoln Turbine NPDES Permit No. NC0080781 Lincoln County Takeda Chemical Products NPDES Permit No. NC0059234 New Hanover County Winston-Salem Archie Elledge WWTP NPDES Permit No. NC0037834 Forsyth County Winston -Salem -Lower Muddy Creek WWTP NPDES Permit No. NC0050342 Forsyth County Please find attached the appropriate chronic toxicity test condition language to be used in these nine permit modifications. You should also note that this language contains our new mailing address, which should be used in future toxicity permit language. Should you have any questions, please feel free to contact me or Matt Matthews at 733-2136. Attachment cc: Rex Gleason-MRO Rick Shiver-WIRO Larry Coble-WSRO Colleen Sullins Shannon Langley -Point Source Compliance/Enforcement Unit CHRONIC TOXICITY PERMIT LIMIT (QRTRLY) The effluent discharge shall at no time exhibit observable inhibition of reproduction or significant mortality to Ceriodaphnia dubia at an effluent concentration of %. The permit holder shall perform at a minimum, quarterly monitoring using test procedures outlined in the "North Carolina Ceriodaphnia Chronic Effluent Bioassay Procedure," Revised February 1998, or subsequent versions or "North Carolina Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised -February 1998) or subsequent versions. The tests will be performed during the months of . Effluent sampling for this testing shall be performed at the NPDES permitted final effluent discharge below all treatment processes. If the test procedure performed as the first test of any single quarter results in a failure or ChV below the permit limit, then multiple -concentration testing shall be performed at a minimum, in each of the two following months as described in "North Carolina Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised -February 1998) or subsequent versions. The chronic value for multiple concentration tests will be determined using the geometric mean of the highest concentration having no detectable impairment of reproduction or survival and the lowest concentration that does have a detectable impairment of reproduction or survival. The definition of "detectable impairment," collection methods, exposure regimes, and further statistical methods are specified in the "North Carolina Phase H Chronic Whole Effluent Toxicity Test Procedure" (Revised -February 1998) or subsequent versions. All toxicity testing results required as part of this permit condition will be entered on the Effluent Discharge Monitoring Form (MR-1) for the months in which tests were performed, using the parameter code TGP3B for the pass/fail results and TBP3B for the Chronic Value. Additionally, DWQ Form AT-3 (original) is to be sent to the following address: Attention: Environmental Sciences Branch North Carolina Division of Water Quality 1621 Mail Service Center Raleigh, North Carolina 27699-1621 Completed Aquatic Toxicity Test Forms shall be filed with the Environmental Sciences Branch no later than 30 days after the end of the reporting period for which the report is made. Test data shall be complete, accurate, include all supporting chemical/physical measurements and all concentration/response data, and be certified by laboratory supervisor and ORC or approved designate signature. 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 Branch at the address cited above. Should the permittee fail to monitor during a month in which toxicity monitoring is required, monitoring will be required during the following month. Should any test data from this monitoring requirement 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. NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum control organism survival, minimum control organism reproduction, 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. QCL Version 5199 March 31, 2000 • CHARLOTTE. Mr. Charles H. Weaver, Jr. NC DENR / Water Quality / NPDES Unit 1617 Mail Service Center -- Raleigh, NC 27699-1617 Ls I' u' r: Subject: NPDES Permit Renewal r J McDowell Creek WWTP Permit No. NCO036277 I Mecklenburg County J Dear Mr. Weaver: This cover letter and attached NPDES Permit Application constitute our request to renew the subject NPDES Permit which expires on September 30, 2000. We are sending the original letter and completed application form and two additional copies of each as directed. The application form includes an attachment with the required narrative description of the sludge management plan for the facility (See Attachment 5). We understand from your February 10, 2000, letter that no renewal fee payment is required as part of this application and that this package includes all that is required by us to apply for this renewal. The McDowell Creek WWTP currently operates under a phased NPDES Permit that became effective November 1, 1995. That permit provides for the operation of the facility at 3.0 mgd, expansion to 3.5 mgd, and expansion to 6.0 mgd, all subject to NC DENR's issuance of appropriate approvals and authorizations of construction. Each phase of the permitted expansion has been successfully completed and is now in operation. The most recent was certified complete by our consulting engineer (Black & Veatch) by letter to DENR's Dave Goodrich dated April 28, 1999, which includes the Engineer's Certification by David Parker dated April 26, 1999. The facility is currently performing and operating in compliance with all permit requirements. Mecklenburg County has implemented an aggressive "Surface Water Improvement Management" (S.W.I.M.) Program since the last renewal of the McDowell Creek Permit. The S.W.I.M. Program has a number of components that are to be implemented over time. One that has already been implemented and adopted by the County Commission, Town of Huntersville, Town of Cornelius, and Town of Davidson establishes stream buffers to reduce non -point source pollution. The buffer widths vary according to the size of the drainage area. While this is not directly a change at the McDowell Creek WWTP, it is a change that is expected to have a positive impact on the basin. It is also an example of the voluntary commitment and cooperation of the several agencies who have jurisdiction or operations that can impact the environment. Another component of the County's S.W.I.M. Program, Phase I, is the development of a watershed based management program focusing on both point and non -point sources of pollution with the overall goal of restoring water quality conditions in Mecklenburg County's streams. A key part of this process is the involvement of the community in proactive measures to improve water quality conditions. This initiative is being launched by Mecklenburg County as a pilot in the McDowell Creek basin beginning in 2000 and is Administrative Division 5100 Brookshire Blvd. Charlotte, NC 28216 Phone: 704/399-2221 Fax: 704/393-2219 Charlotte -Mecklenburg Utilities being called "Water Improvements Now," or WIN. The plan is to use WIN as a spring board to develop the techniques necessary to carry this watershed based/community involvement approach forward into the rest of the County as part of Phase II of S.W.I.M This effort has already begun in the McDowell basin through conducting over 30 presentations to community groups and launching volunteer efforts such as Adopt -A - Stream, Storm Drain Stenciling and volunteer monitoring. A kick off meeting for the community involvement campaign is being planned for April 2000. A comprehensive water quality model will be developed through the WIN project which will be used as a planning tool for future development and will also act to identify water quality problem areas and the appropriate best management strategies to reduce non - point sources of pollution. Mecklenburg County has allocated $100,000 toward this effort and is in the process of contracting with a private consulting firm for development of the model. The development of this model is being coordinated with Utilities as part of our study of the McDowell basin for future sewer needs. Mecklenburg County's water quality model will be expanded to included the rest of the County as part of S.W.I.M. Phase II and the expansion of the watershed based management strategy county -wide which is planned for 2002. We request that the renewal of the subject permit include two changes from the current permit. First, please modify the whole effluent chronic toxicity provisions to reflect DENR's modifications described in an August 26, 1999, letter from Matt Matthews, Aquatic Toxicology Unit Supervisor, to Utilities Director Douglas Bean. These modifications provide for an initial quarterly test (either pass/fail or multiple concentration (ChV)). In the event of failure of that test, the permittee is required to perform additional multiple concentration tests in the two months following the failure. Second, we request that the permit should allow a discharge of up to 6.0 mgd of effluent into McDowell Creek on an annual average basis with no single monthly average to exceed 7.6 mgd. This change more accurately reflects the design of the facility approved by NC DENR and NC DENR's methods for consideration of water quality impacts and therefore does not constitute an increased discharge. Alternatively, we would be interested in receiving a mass -based permit in lieu of concentration based requirements. We believe that either scenario will provide excellent protection of the receiving waters and allow the plant to perform up to the design criteria used to establish the limits. Please let me know immediately if this application package is incomplete or if you need additional information. We are available to meet with you as needed to clarify the application package or to provide additional information. We look forward to hearing from you. Sincerely, CHARLOTTE MECKLENBURG UTILITIES Douglas BQn Key Business Executive NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs SECTION 111. INDUSTRIAL WASTE CONTRIBUTION TO MUNICIPAL SYSTEM Submit a separate Section III for each Significant Industrial User. 1. Significant Industrial User (SIU) An SIU has (or could have) significant impact on the POTW receiving the wastewater or upon the quality of effluent from the receiving POTW. Specifically, an SIU: • has a flow of 50,000 gallons or more per average workday; • has a flow greater than 5 percent of the total flow carried by the municipal system m receiving the waste, or • has a toxic material in its discharge. It may be necessary to alter these administrative criteria in certain cases, such as an instance where two or more contributing industries in combination can produce an undesirable effect on either the municipal facility or the quality of its effluent. Name of SIU Ingersoll Rand Company Street address 800-A Beatty Street City Davidson County Mecklenburg State NC Zip Code 28036 Telephone Number ( 704 ) 896-4750 Fax Number ( 704 ) 896-4606 e-mail address 2. Primary Product or Raw Material Specify either the principal product or the principal raw material and the maximum quantity per day produced or consumed. Quantities are to be reported in the units of measurement for each SIC category at the facility. SIC categories should use the units of measurement normally used by that industry. Product Raw Material Quantity Units Air Compressors 1. Tubing & small machine components 2. Phosphate bath & acid rinse (tube cell washer) 3. Paint in paint booth 4. Aqueous cleaner in the cabinet washers 500 — 600 unitslmonth Max production is 700 un'dslmonth 3. Flow Indicate the volume of water discharged into the POTW and whether this discharge is intermittent or continuous 0.0016 MGD n Intermittent X Continuous SIU is permitted to discharge 0.007 mgd daily maximum flow, 0.005 mgd average monthly flow Pretreatment consists of 1-5,000 gallon flow equalizationtank,1-oil/water separator,1-1,000 gallon treatment tank, 1- ultra filtration unit 4of16 McDowell Creek WWTP NPDES Permit No. NCO036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MOD or with pretreatment programs Attachment 1 Facility Description Present Operating Status McDowell Creek VW TP provides advanced wastewater treatment to serve northern Mecklenburg County. While a complete description is provided below, in summary the plant includes influent pumping, screening, grit removal, primary clarification, biological treatment through activated sludge and biological nutrient removal (BNR) processes, secondary clarification, effluent filtration, and ultraviolet (UV) disinfection. Solids are anaerobically digested. The plant has sand drying beds available for solids dewatering, but is currently using a mobile belt filter press to perform this operation. Solids are land applied. The design hydraulic flows for the plant are: Average day 6.0 mgd Maximum Month 7.6 mgd Peak (all pumps) 17.6 mgd The current process train consists of: 1. Liquid train ❑ Influent Pumping ❑ Mechanical bar screens ❑ Aerated grit removal ❑ Primary Clarifiers o Trickling filters (Not used during BNR) ❑ Anaerobic basins ❑ Anoxic Basins ❑ Oxic Basins ❑ Final Clarifiers ❑ Deep bed effluent filters w/ de -nitrification capability ❑ Ultraviolet Disinfection 2. Solids Train ❑ Two anaerobic digesters o Sand drying beds Headworks Wastewater enters the plant through a 36 inch gravity sewer line. Upon entering the headworks area, the flow is screened by a mechanical bar screen with 1-inch openings. Flow is then measured by an ultrasonic flow meter over the 24-inch parshall flume before being pumped to the preliminary treatment structure. ❑ Mechanical bar screen -1 ❑ Hydraulic capacity, mgd -17.6 Influent Pump Station The Influent Pump Station has 5 lift pumps with a total pumping capacity of 13,400 gpm (19.3mgd). 5 of 16 McDowell Creek WWTP NPDES Permit No. NCO036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs ❑ Pump 1, gpm - 600 ❑ Pump 2, gpm - 3500 ❑ Pump 3, gpm - 2900 ❑ Pump 4, gpm - 2900 ❑ Pump 5, gpm - 3500 ❑ Pumps no. 2 and no. 5 are immersible with AFD control. Preliminary Treatment structure The preliminary Treatment structure consists of the following equipment: ❑ One mechanical bar screen with a hydraulic capacity of 17.6 mgd ❑ Two aerated grit chambers with a volume of 4500 cubic feet and a total hydraulic capacity of 17.6 mgd ❑ Equipment associated with preliminary treatment including an air lift grit pump, blowers, dewatering screws and a belt conveyor. Primary Clarifiers There are three primary clarifiers with a total volume of 619,200 gallons. Primary Volume (gallons) Design Hydraulic Design Hydraulic Clarifier Loading (Avg Day, Loading (Max Day, No. mgd) mgd) ❑ 2 133,000 1.65 4.85 ❑ 3 352,600 2.70 7.9 Solids are removed to the anaerobic digesters by 5 positive displacement diaphragm pumps. Tricklinq Filters Under normal operating conditions the filters are not used because of their detrimental effect on the BNR process. o Two filters with rock media - total design capacity of 17.6 mgd. Anaerobic, Anoxic, and Oxic Basins McDowell Creek WWTP was originally constructed to provide two -stage activated sludge treatment with intermediate clarification. During the 1995-1998 expansion, it was converted to use a single stage process and to provide BNR. The original sequential aeration basins were re -configured to become parallel trains and the intermediate, circular clarifiers were converted into aeration basins. The result is that there are currently 4 rectangular basins with anoxic and anaerobic zones, and 3 circular aerobic basins. In addition, new basins were constructed to provide anaerobic zones for BNR. The tables below describe the current configurations and design criteria. 6of16 McDowell Creek WWTP NPDES Permit No. NCO036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs Parameter Anaerobic detention time, hr Anoxic detention time, hr Oxic detention time, hr Solids retention time, days MLSS, mg/I Total RAS flow @ 0.6% TS, mgd Design criteria @ design Average day flow (6.0 mgd) 1.5 hr 2.1 hr 8.6 hr 11 hr 1,850 mg/I 2.5 mgd The circular and rectangular aeration basins provide a total detention time of 12 hours at 6.0 mgd average day flow and 9.5 hours at 7.6 mgd max. month flow. Basins 1.1 and 2.1 (the rectangular basins) are partitioned to provide approximately 20 percent anoxic detention leaving the remainder for oxic (aerated) detention. Basin 1.1 Anaerobic Anoxic Basin 2.1 Anaerobic Anoxic Number of cells per zone 4 4 4 4 Nominal cell size, ft 21 x 21 28 x 23.5 21 x 21 28 x 22 Sidewater depth, ft 14 14 14 14 Cell volume, cu ft 6,170 99200 6,170 8,620 Hydraulic Loading Per Basin Annual Avg Flow, mgd 3.0 3.0 3.0 3.0 Max Month Flow*, mgd 6.8 21.5 6.8 21.5 *Includes RAS recycle, oxic recycle, and internal (anoxic) recycle for UCT BNR mode. Basin 1.1 Basin 2.1 Anaerobic Anoxic Anaerobic Anoxic Mixing intensity (bhp/1000 cu ft) 0.75 0.75 0.75 0.75 No. of mixers per cell 1 1 1 1 Motor horsepower, hp each 7.5 7.5 7.5 7.5 Motor rpm 385 385 385 385 No. of anoxic recycle pumps n/a 2 n/a 2 Flow rate range per pump, gpm n/a 500-1,320 n/a 500-1,320 Motor horsepower, hp each n/a 1.5 n/a 1.5 OXIC RECYCLE 7 of 16 McDowell Creek WWTP NPDES Permit No. NC0036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs Submersible pumps mounted in the circular aeration basins are used to return oxic MLSS from the circular aeration basins to either the first or second cell of the anoxic zones of basins 1.1 and 2.1. The pumps are equipped with adjustable frequency drive control to provide a pumping range of 6.0 -15.2 mgd. Number of pumps 4 Type Submersible centrifugal Location Aeration basins 1.2, 1.3, 2.2 Rated capacity, gpm each ORP-1.1 5,500 ORP-1.2 51500 ORP-2.1 5,500 ORP-2.2 5,500 Capacity range, gpm each 21625-5,500 Pumping capacity, gpm Installed 11,000 Firm 5,500 Rated head, ft 32 Horsepower, each pump ORP-1.1 75 ORP-1.2 75 ORP-2.1 75 ORP-2.2 75 Drives Adjustable speed Control Local HO Blower No. SUM Motor HP B-1 29100 150 B-2 21100 150 B-3 3,148 200 B-4 3,148 200 Total Capacity (all units in service) 10,496 Firm capacity (largest unit out of service) 71348 Discharge Pressure, psi 7.5 Control Automatic Final Clarifiers 2 - Flocculating type final clarifiers with the following characteristics: Hydraulic Loading: Flow per basin (mgd) Surface Loading Rate (gpd/sq ft) Detention Time Flocculation Well (min) Total (hrs) 8 of 16 Design Peak 3 8.8 380 1,120 35 12 7.1 2.4 McDowell Creek WWTP NPDES Permit No. NCO036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs Effluent Filters Effluent filtration consists of deep bed, sand filters with denitrification capability. Acetic acid is provided as a carbon source to promote biological denitrification within the filters as needed. Filter effluent flows into a clearwell and then to the ultraviolet disinfection system. Submersible pumps located in the clearwell provide backwash water to the filters. The submersible pumps are also used periodically to "bump" the filters with backwash water to release nitrogen gas bubbles formed by denitrification. Dirty backwash water flows into a mudwell, which drains by gravity to the plant influent pump station. Blowers located adjacent to the effluent filters are used for air scour of the filters. Physical Dimensions Number of cells Cell size (width x length), each (ft) Sidewall depth, ft Depth of mono -media, ft Effective size of media, mm Surface area per, cell, ft' Loading Criteria Flow (mgd) Filtration rate Each cell, gpm/ft2 All cells, gpm/ft2 Ultraviolet Disinfection n 91- 6" x 531- 0" 20'- 8" 6 2.3 500 Average Day Peak 6.0 17.6 1.7 4.9 2.1 6.1 Disinfection is provided by parallel banks of vertical ultraviolet light modules. Two channels housing six UV modules are located at the effluent end of the filter structure. One future channel will be used for six future UV modules. The system is designed to disinfect a flow of 6.0 mgd to a coliform level of less than 200 organisms/100 ml. The UV lamp cleaning system includes a jib crane for removing the modules from the channels and a cleaning tank with an air mixing system. Number of channels 2 + 1 future Channel width, inches 24.5 Channel length, ft 321- 0" Channel depth, inches 86 Number of modules 6 Lamps/module 40 Reaeration A cascade type reaeration structure is provided to increase the effluent dissolved oxygen to at least 6 mg/L. The reaeration structure consists of flow over horizontal 9of16 McDowell Creek WWTP NPDES Permit No. NCO036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs fixed weirs onto a vertical succession of aluminum steps 10 of 16 McDowell Creek WWTP NPDES Permit No. NCO036277 ' NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs Attachment 2 Potential Facility Changes Charlotte Mecklenburg Utilities has several projects currently underway at the McDowell Creek WWTP. Here is a synopsis of the current work and other projects anticipated over the next five years. Sludge Thickening & Improvements This project scope includes: o Improvements to digester complex electrical system to meet NFPA 820 and NEC requirements ❑ Gravity belt thickeners for waste activated sludge (WAS) thickening o Waste sludge holding basin with aeration ❑ Enclosing effluent filter backwash blowers for noise control This project has been submitted to NC DENR for review and an authorization to construct has been issued. Construction bids are expected by May 2000. Potable Water Service The McDowell Creek WWTP currently obtains potable water from an on -site well. It is planned to extend approximately 10,000 feet of water main to provide public water supply for potable and fire protection services. Solids Dewatering & Miscellaneous Improvements Currently in design, this project scope includes: o Construction of dewatering building o Installation of 2 belt filter press units for dewatering anaerobically digested biosolids ❑ Construction of covered storage area for dewatered biosolids ❑ Improvements to the anaerobic digesters and sludge heaters, including the addition of a third primary digester and a covered sludge/gas storage basin. ❑ New bar screen facilities ❑ Replacement of influent pump No. 1 with larger capacity pump to increase firm pumping capacity to 17.6 mgd ❑ Up -fitting effluent filter cell no. 5 (shell constructed during last expansion) ❑ Addition of UV disinfection modules to increase disinfection capacity This project is projected to begin construction during calendar year 2000. Stand-by Power Improvements This project will replace the existing plant generator system with a new system rated for heavier service. The new system will be capable of powering the entire plant in the event of a power outage and for power peak shaving. The project is currently being designed and should be in service in late 2000 or early 2001. 11 of 16 McDowell Creek WWTP NPDES Permit No. NC0036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs Effluent Reuse Project Charlotte Mecklenburg Utilities is negotiating a contract with an area golf course that will provide treated effluent to them for irrigation. This would replace the well system that they currently use. Efforts are underway to identify and add other customers. The project will provide for supplemental disinfection, pumping facilities, controls, and pipeline from the McDowell Creek WWTP to the customer. The facilities are being designed at this time. Utilities anticipates a subsequent permit modification request to include designation of the McDowell Creek plant as a Water Reclamation Facility and to provide for the additional discharge point(s). McDowell Creek Basin Study The McDowell Creek basin is one of the fastest growing areas of Mecklenburg County. Utilities has initiated a planning study to project the future wastewater treatment needs for the basin. The study departs from traditional planning studies by including strong participation by the Town of Huntersville and the Town of Cornelius who control most of the land use planning for the basin and by addressing the watershed protection issues presented by potential plant expansion. Both towns are involved in progressive and innovative land use planning activities. Their involvement will help synchronize the development and growth plans for the area with the wastewater treatment needs. With this information as input, the study will evaluate short term and long term watershed management and wastewater treatment and disposal/reuse alternatives including non - discharge options. A stakeholders group has been established to provide input to Utilities in the evaluation of alternatives identified. The stakeholders group includes representatives from the development community, environmental interests, neighborhood associations in the basin and on Mountain Island Lake, neighbors of the plant, owners of significant property in the basin, Mecklenburg County, and the NC DENR Regional Office. The Study will produce a plan for comprehensive wastewater management within the watershed that is in agreement with current land use plans, meets community needs, and that is focused on protecting the environment. The study is to be completed in the fall of 2000 and Utilities expects to act quickly on the recommendations. Rocky River Regional Outfall Project Several years ago, Charlotte Mecklenburg Utilities entered into a regional agreement with the Water and Sewer Authority of Cabarrus County (WSACC) to provide sewer service to the Northeast part of Mecklenburg County and to the Northwest part of Cabarrus County. The pipelines required to consummate the agreement are currently under construction. One of the results of the agreement is that all of the wastewater flow from the Town of Davidson will be re -directed away from the McDowell Creek WWTP into the Rocky River Regional Wastewater Treatment Plant in Cabarrus County. It is estimated that this will be reduce flows into the McDowell Creek WWTP by about 750,000 gallons/day starting in 2001. Although there is not a direct impact on the McDowell Creek WWTP, it is worth noting that this project will also eliminate an existing, private WWTP discharge into the Rocky River. 12 of 16 McDowell Creek WWTP NPDES Permit No. NCO036277 PRELIMINARY TREATMENT AVE: 6.0, PEAK: 17.6 MECHANICAL AERATED BAR SCREEN GRIT CHAMBER ALUM PRIMARY PRIMARY PRIMARY CLARIFIER NO. 1 CLARIFIER NO. 2 CLARIFIER NO. 3 AVE: 1.7 AVE: 1.7 AVEt 2.7 PEAKt 4.9 PEAK: 4.9 PEAK: 7.9 NOTEs ALL FLOWS ARE IN MILLION GALLONS PER DAY ANAEROBIC ANOXIC/OXIC AERATION AERATED BASIN 1.1 BASIN 1.1 BASIN 1.3 GRIT CHAMBER LIME AVE: 3.0 AVE: 3.0 AVE: 1.5 PEAK: 9.8 PEAKs 8.8 PEAKs 4.4 BYPASS AN AX OX ED TRICKLING F I LTER RECYCLE OX ACETIC AERATION ACID BASIN 1.2AVE: GRIT TO PRIMARY SLUDGE 1.5 5 OUMPSTER TO ANAEROBIC PEAKS 4 DIGESTERS RECYCLE INFLUENT PUMPING TRICKLING ANAEROBIC ANOXIC/OXIC AERATION STATION HEADYIORKS FILTER BASIN 2.1 BASIN 2.1 BASIN 2.2 AVE: 3.0 AVE: 3.0 AVE: 3.0 PEAK: 8.9 PEAK: 8.8 PEAK: 8.8 MECHANICAL BAR SCREEN AN AX OX l_____j OX - ---*- \`\\\ AVE: 6.0do PEAK: 17.6 RFCyr_i a CASCADE EFFLUENT FILTER REAERATION STRUCTURE PLANT AVE: 6.0 AVE: 1.5/FILTER INFLUENT PEAK: 17.6 6.0 TOTAL AVE: 6.0 PEAKS 4.4/FILTER PEAK: 17.6 17.6 TOTAL umu ACETIC ACID/ 1R G METHANOL UV DISINFECTION T AVE: 6.0 PLANT PEAK: 17.6 EFFLUENT AVE : 6.0 PEAK: 17.6 MCDOWELL CREEK FINAL CLARIFIER NO. 1 AVE: 3.0 PEAKt 8.8 FINAL CLARIFIER NO. 2 AVE: 3.0 PEAKt 8.8 ALUM Ot/6225 MCKER NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs Attachment 5 — Description of Sludge Management Plan The sludge management plan for the McDowell Creek VW1 TP is documented in the "Engineering Design Report, Civil/Mechanical Design Memorandum, McDowell Creek Wastewater Treatment Plant Facilities Improvements," prepared by Black & Veatch for the 1995 expansion of the plant. In addition, Charlotte Mecklenburg Utilities has a long- term contract in place with a private firm that guarantees beneficial re -use / disposal of all biosolids produced at McDowell and our other facilities. Sludge stabilization is currently provided through a system of four anaerobic digesters. Two of the digesters are covered and operate as primary digesters. The third and fourth are open and are used for sludge storage. The primary digesters are heated and mixed. The heaters can be fueled by either recovered methane gas from the digesters or by fuel oil. Once digested, the biosolids can be discharged to sand drying beds for dewatering. During the last expansion of the McDowell Creek WWTP, upgrades to the digesters disrupted normal sludge stabilization processes and resulted in the production of a higher volume of thinner than normal sludge. The sludge drying beds did not have enough capacity to handle this increased volume. Utilities contracted for temporary dewatering with a service provider who used a mobile, belt filter press. Even though the digesters are now performing well, utilities has continued this practice and plans to do so until the permanent mechanical dewatering facilities are complete. Dewatered cake from the belt press may be loaded directly into trucks for removal to land application sites or to storage at other facilities (see below) or can be stored on - site in dedicated sand drying beds. Biosolids cake dried and removed from the sand filter beds is currently stored in three of the sand drying beds that have been dedicated to this purpose. Covered storage has also been designed and is planned to be constructed at the McDowell Creek WWTP in conjunction with the dewatering facility. To address the long term reuse/disposal requirements for the residuals produced at all of our wastewater and water treatment plants, Utilities conducted an industry -wide, experience and qualifications based procurement process to select a firm that could provide the needed services. A ten-year contract was established effective July 1, 1999, that provides for guaranteed beneficial reuse / disposal for all of the residuals produced during the term of the agreement. The selected firm will use a combination of land application, lime stabilization, and composting for beneficial reuse. In the event that these options should become unfeasible and/or unavailable, the firm has committed to landfill disposal and has guaranteed that the designated landfill will take the material. The contract establishes a pricing structure for the entire term for all options. The contractor makes the decision as to how much material is processed through each option. The contract is secured by a corporate guarantor as well as a performance bond. Utilities has provided substantial covered sludge storage facilities at the Mallard Creek and the Irwin Creek VWVTP's and a lesser amount (in terms of days of production) of storage at the McAlpine Creek WWTP. The contractor is required to manage and maintain these facilities. The management requirements include a guarantee that there is always a minimum amount of space (typically 25% of the total floor space) open for Utilities' staff to deposit dewatered biosolids cake. Utilities is responsible for putting the biosolids into the storage facility. The contractor is responsible for managing the 15 of 16 McDowell Creek WWTP NPDES Permit No. NCO036277 NC DENR / DWQ / NPDES PERMIT APPLICATION - STANDARD FORM A Municipal Facilities with permitted flows > 1 MGD or with pretreatment programs material in storage and for removal of the material to its final disposition. The contractor has the option to store material from any of the plants within the storage space provided. A provision of the contract states that Utilities will provide covered storage at McDowell Creek with a minimum floor area equivalent to the dedicated sand drying beds currently being used for that purpose. Again, the contract requires them to manage the proposed storage facility and to always maintain open space for new material. The contractor is also required to identify and obtain permits for all required land application sites and/or other reuse/disposal alternatives. The current mode of operation of the contractor is that storage sites are well managed according to the contract requirements and that all suitable material is land applied for agricultural benefit. The contractor has modified our Residuals Management Facility (RMF) (operation and maintenance of which is within the scope of their contract) at McAlpine Creek UW TP and will soon begin lime stabilization and composting operations there. It is anticipated that most, if not all, of the biosolids processed through that facility will be from McAlpine's production. However, the contractor will decide how much and which material is used at the RMF. It is therefore possible that some material from McDowell could be used for composting or lime stabilization. 16 of 16 McDowell Creek WWTP NPDES Permit No. NC0036277