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HomeMy WebLinkAboutWQ0040622_Application_20190212INITIAL REVIEW Reviewer Monday, Tessa R Project Number* WQ0040622 SUBMITTAL DATED: 1/31/2019 Project Contact Information Rease provide inforrration on the person to be contacted by MB Staff regarding electronic subnittal, confirmation of receipt, and other issues. ...................................................................................................................................................................................................................................................................................................................................................................................................... Name * Drew Matthews Email Address* Phone Number* dmatthews@soilplus.net 252-883-9301 Project Information Application Type* r New r Renewal r Annual Report Permit Type * r Wastewater Irrigation r Other Wastewater r Closed -Loop Recycle r Single -Family Residence Wastewater Irrigation Is a paper copy of the application being submitted?* r Yes r No (- N/A Permit Number currently has project Permittee * Atlantic OBX, Inc. Facility Name * N/A County* Dare r Modification (Major or Minor) r Additional Information r Other r High -Rate Infiltration r Reclaimed Water r Residuals r Other Please provide comments/notes on your current submittal below. Please attach all information required or requested for this submittal to be review here. Submission Letter.pdf 4.16MB Application Form Engineering Rans, Specifications, Calculations, Etc.) For nein and modification permit applications, the paper copy is required to be subrrutted to the Di, vision Be advised, applications ivill not be considered complete until both the paper and electronic applications have been received_ The paper copy shall include the follo-kAmig: • Application Farm • All relevant attachments (talcs, soils report, specs, etc_) • 1 full-size engineering plan set • 2 11-17" engineenng plan sets • 1 extra set of specifications (in addition to the set of specifications provided in the attachments) • Fee (if required) This shall be mailed to the following address: By U_S_ Postal Service: Division of Water Resources- Non -Discharge Branch 1617 Mail Service Center Raleigb_ NC 27699-1613 By CourieriSpecial Delivery: Division of Water Resources- Non -Discharge Branch Ag Nathaniel Thornburg- 9th Floor, Office #942WN 512 N_ Salisbury St_ Raleigh,NC 27604 For questions or problems contact Tessa Monday at: 919.7073660 or TessaMonday([ icdcur-goo or Sonia GraxTs at 919.747.3657 or Sonia Graves(dpc&au.gov. * I;W By checking this box I am acknowledging that I have read the above statement and agree to send these documents as required to one of the address given above. Signature Sign Submission Date 1/31/2019 ATLANTIC OBX, INC. 2019 NEW PERMIT APPLICATION DISTRIBUTION OF CLASS A RESIDUALS PERMIT Submitted by: Soil Plus P.O. Box 1396 Oxford, North Carolina 27565 January 11, 2019 SOIL PLUS SOIL PLUS January 11, 2019 NCDEQ-DWR Non -Discharge Branch 1617 Mail Service Center Raleigh, North Carolina 27699-1636 Attention: Mr. Nathaniel Thornburg Reference: NEW PERMIT APPLICATION Distribution of Class A Residuals Permit ( >3,000 DT/Year) Atlantic OBX, Inc. Residual Biosolids Program Soil Plus Project No. 201007.1316 Mr. Thornburg: Soil Plus, LLC (Soil Plus) is submitting one original and one electronic copy of this permit application package for Atlantic OBX, Inc. This package includes: 1. Completed Distribution of Class A Residuals Application 2. Completed Residual Source Certification Attachment and supporting documentation (Field Loading Calculations, Analytical, etc.) for the following sources: a. Elizabeth City WTP b. Elizabeth City WTP Residuals Storage Facility 3. O&M Plan The City of Elizabeth City currently holds a Class B Land Application permit for the WTP (WQ0002883) and a Surface Disposal Unit Permit for the Residuals Storage Facility (WQ0014808). This requested Distribution of Class A Residuals permit is not intended to replace either of those permits held by Elizabeth City, but would allow flexibility on the distribution of the residuals. A check for $1,310 is enclosed with this package per the NCDEQ-DWR Non -Discharge Branch's fee schedule for a new permit under the major classification. Soil Plus will be responsible for completing this permit application for the Atlantic OBX, Inc. If there is any further information required or questions regarding this permit application, please do not hesitate to contact me for assistance. Respectfully, PO Box 1396 Drew Matthews, Soil Plus Oxford, NC 27565 (252) 883-9301 J. Bryan Smith, Atlantic OBX, Inc. dmatthews@soilplus.net www.soilplus.net Atlantic OBX, Inc. New Permit Application Distribution of Class A Residuals Distribution of Class A Residuals Application DCAR Residual Source Certification Attachment Source Summary Form RSCA -Elizabeth City WTP Field Loading Calculations Analytical RSCA -Elizabeth City WTP Residuals Storage Facility Field Loading Calculations Analytical O&M Plan APPENDIX 1 2019 NEW PERMIT APPLICATION Atlantic OBX, Inc. Distribution of Class A Residuals Application DCAR State of North Carolina DWR Department of Environmental Quality Division of Water Resources Division of Water Resources 15A NCAC 02T.1100 — DISTRIBUTION OF CLASS A RESIDUALS FORM: DCAR 06-16 I. APPLICANT INFORMATION: 1. Applicant's name: Atlantic OBX, Inc. dba Atlantic Sewage Control Applicant type: ❑ Individual ® Corporation ❑ General Partnership Privately -Owned Public Utility ❑ Federal ❑ State ❑ Municipal ❑ County Signature authority's name per 15A NCAC 02T .0106: J. Bryan Smith Title: President Applicant's mailing address: P.O. Box 2560 City: Kitty Hawk State: NC Zip: 27949 - Telephone number: (252) 255-2030 Email Address: 2. Consultant's name: Drew Matthews License Number (for P.E.): _ Affiliation: ❑ On Staff ® Retained (Firm: Soil Plus, LLC) Consultant's mailing address: P.O. Box 1396 City: Oxford State: NC Zip: 27565 - 'up Telephone number: (252) 883-9301 Email Address: dmatthewsgsoilplus.net 3. Fee submitted: $1,310 (See Instruction B) IL PERMIT INFORMATION: 1. Application is for (check all that apply): ® new, ❑ modified, Q renewed permit 2. If this application is being submitted to renew or modify an existing permit, provide the following: Permit number: Date of most -recently issued permit: Date of most -recently certified Attachment A (if different than the permit): III. FACILITY INFORMATION: 1. Name of residuals processing facility: N/A City: --A State: Zip Coordinates: Latitude: _° Longitude: Datum: Level of accuracy: Method of measurement: County where facility is located: _ 2. Facility contact (person familiar with residuals preparation): Name: J. Bryan Smith Title: President Mailing address: P.O. Box 2560 City: Kitty Hawk State: Zip: 27949 - Telephone number: (252) 255-2030 E-mail address: FORM: DCAR 06-16 Page 1 of 3 3. Is the residual process facility also the generator? M Yes; ❑ No If No, please specify delivery frequency and quantity of residual to be processed: 4. Length of residuals storage at facility: See O&M Plan days (Note: the Division requires minimum 30 days storage in units that are separate from treatment system, i.e. not in clarifiers, aeration basins, etc.) IV. RESIDUALS QUALITY INFORMATION: 1. Specify how these residuals will be distributed: ❑ sold or given away in bags or other containers; ❑ lawn (bulk); ❑ home garden (bulk); other (explain); Bulk Land Application Note: Bulk residuals shall mean residuals that are transported and not sold or giving away in a bag or other receptacles with a load capacity of one metric ton or less. 2. Complete the following if residuals are to be mixed with other materials: Type of Materials Amounts to be added Der 1.0 dry ton of residuals (dry ton) 3. Approximate amounts of the residuals received and processed at the facility: See O&M Plan dry tons per year. 4. Approximate amounts of the final product (processed residuals) to be distributed: See O&M Plan dry tons per year. 5. Provide a description of the onsite storage management plan for the treated residuals (including estimated average and maximum storage times prior to distribution): See O&M Plan 6. Does the facility have a stormwater management plan? ❑ Yes; ❑ No Explain whether the treatment and storage areas are under roof or how stormwater runoff will be handled: V. RESIDUALS SOURCE INFORMATION: (Required for all new, renewed, or modified residuals source) Complete and submit the attached Residuals Source Certification and all associated documentation. Residuals Source Certification FORM: DCAR 06-16 Page 2 of 3 Professional Engineer's Certification: (Application Involving New or Changes to Treatment or Storage Units) attest that this application for has been reviewed by me and is accurate and complete to the best of my knowledge_ I further attest that to the best of my knowledge the proposed design has been prepared in accordance with the applicable regulations. Although certain portions of this submittal package may have been developed by other professionals, inclusion of these materials under my signature and seat signifies that I have reviewed this material and have judged it to be consistent with the proposed design. North Carolina Professional Engineers Seal, Signature, and Date: Applicant's Certification: The applicant or any affiliate has not been convicted of an environmental crime, has not abandoned a wastewater facility without proper closure, does not have an outstanding civil penalty where all appeals have been exhausted or abandoned, are compliant with any active compliance schedule, and do not have any overdue annual fees under Rule 15A NCAC 02T.0 105. ® Yes ❑ No, Explain, .. 1 J. Bryan Smith President (Signature Authority's Name — PLEASE PRINT) ('Title) attest that this application for Atlantic OBX, Inc. (Facility Name) has been reviewed by me and is accurate and complete to the best of my knowledge. I understand that the Division of Water Resources may not conduct a technical review of this program and approval does not constitute a variance to any rules or statutes unless specifically granted in the pen -nit. Further, any discharge of residuals to surface waters or the land will result in an immediate enforcement action, which may include civil penalties, injunctive relief, and/or criminal prosecution_ I will make no claim against the Division of Water Resources should a condition of this pen -nit be violated. I also understand that if all required parts of this application are not completed and that if all required supporting information and attachments are not included, this application package will he returned to me as incomplete. Note: In accordance with North Carolina General Statutes §143-215.6A and §143-215.6B, any person who knowingly makes any false statement, representation, or certification in any application shall be guilty of a Class 2 misdemeanor, which may include a fine not to exceed $10,000 as well as civil penalties up to $25,000 per violation. Signature: O Date: FORM: DCAR 06-16 Page 3 of 3 APPENDIX 2 2019 NEW PERMIT APPLICATION Atlantic OBX, Inc. Residual Source Certification Attachment Source Summary Form Q a� 0 li Q a� 73 C z 3 a a 0 0 H A 0 C:) U 0 � a o � � � z � o o 0 � 3 3 a a o U � � a cl a CG cC P- t tc Lt F'^ U U c x -a N a w w 0 0 w U U Q a� 0 li Q a� 73 C z 3 APPENDIX 3 2019 NEW PERMIT APPLICATION Atlantic OBX, Inc. Residual Source Certification Attachment Elizabeth City WTP Field Loading Calculations Analytical State of North Carolina DWR Department of Environment and Natural Resources Division of Water Resources DiivisIon of Water ResoUKes RESIDUALS SOURCE CERTIFICATION FORM: RSC 11-13 I. RESIDUALS SOURCE-GENERATING FACILITY INFORMATION (See Instruction B.): 1. Facility Name: Elizabeth Cites 2. Facility permit holder is: Federal, 0 State, 0 Local Government, or ❑ Private. Facility permit issued by: Div. of Water Resources, Div. of Environmental Health, or j Other (explain: �. 3. Facility contact person and title: Travis Tucker Complete mailing address: P.O. Box 347 City: Elizabeth Cit] State: NC Zip: 27907- Telephone number: (252) 335-2196 E-mail address: ttucker e cityofec.com 4. Facility physical address: I Wilson Street City: Elizabeth Citi State: TC Zip: _-R Coordinates: Latitude: 36° 18'47.1" Longitude: 76° 13'29.7" Datum: NAD 83 Level of accuracy: Sub-Meter Method of measurement: 5. Purpose of the facility: treatment of municipal wastewater, treatment of 100% domestic wastewater, treatment of potable water, treatment of 100% industrial wastewater, treatment of industrial wastewater mixed with domestic wastewater, (approximate percentages: _ % industrial and _ % domestic) other (explain: _ ). 6. Does the facility have an approved pretreatment program: Yes No 7. Facility permitted/design flow: 0 MGD and facility average daily flow: 2.4 MGD 8. Average amount of residuals being generated at this facility 2,164 (See O&M Plan) dry tons per year. 9. Specify the following regarding treatment and storage volumes available at the facility: Type and volume of residuals treatment: No residual Treatment Type and volume of residuals storage (i.e., outside of residuals treatment units): 274,000 Gallon above-ground concrete II. RESIDUALS QUALITY INFORMATION (See Instruction C.): 1. Specify if residuals are regulated under: 0 40 CFR Part 503 or 40 CFR Part 257. Note: Only residuals that are generated during domestic/municipal wastewater treatment processes are regulated under 40 CFR Part 503, otherwise, the residuals are regulated under 40 CFR Part 257. 2. Specify if residuals are defined under 15A NCAC 02T.1102(6) as: 0 Biological ® Non -Biological FORM: RSC 11-13 Page 1 of 5 Note: Biological residuals are residuals that have been generated during the treatment of domestic wastewater, animal processing wastewater, or the biological treatment of industrial wastewater (biological treatment is a system that utilizes biological processes including lagoons, activated sludge systems, extended aeration systems, and fixed film systems). 3. Hazardous Waste Determination: Complete the following to demonstrate that the residuals are non -hazardous under RCRA: (Note - this item does not have to be completed for facilities that are less than 0.5 MGD in design flow that treat 100% non -municipal, domestic wastewater only) a. Are the residuals listed in 40 CFR §261.31-§261.33: 0 yes no. If yes, list the number(s): _ b. Specify whether or not the residuals exhibit any of the characteristics defined by 40 CFR §261.21- 261.24: M yes 0 no. Fill in the following tables with the results of the latest toxicity characteristic leaching procedure (TCLP) analysis as well as those for corrosivity, ignitability, and reactivity: Laboratory: Mce Analytical and Date of analysis: 1/16/2018 Passed corrosivity test: ® yes no. pH: 9.7 s.u. (2 < pH < 12.5) Passed ignitability test: ® yes no. Flashpoint: >200 °F (> 140°F) Passed reactivity test: JU yes Ono. HCN: k 15.3 mg/kg (<250) & HzS: < 153 mg/kg (<500) TCLP Parameter Limit (Mg/1) Result (Mg/1) TCLP Parameter Limit (mg/l) Result (Mg/1) Arsenic 5.0 <0.05 Hexachlorobenzene 0.13 <0.05 Barium 100.0 <0.25 Hexachloro-1,3-Butadiene 0.5 <0.05 Benzene 0.5 <0.1 Hexachloroethane 3.0 <0.05 Cadmium 1.0 <0.005 Lead 5.0 <0.025 Carbon Tetrachloride 0.5 <0.1 Lindane 0.4 <0.0005 Chlordane 0.03 <0.003 Mercury 0.2 <0.0002 Chlorobenzene 100.0 <0.1 Methoxychlor 10.0 <1 Chloroform 6.0 <0.1 Methyl Ethyl Ketone 200.0 <0.2 Chromium 5.0 <0.05 Nitrobenzene 2.0 <0.05 m -Cresol 200.0 <0.05 Pentachlorophenol 100.0 <0.1 o -Cresol 200.0 <0.05 Pyridine 5.0 <0.05 p -Cresol 200.0 <0.05 Selenium 1.0 <0.10 Cresol 200.0 <0.05 Silver 5.0 <0.025 2,4-D 10.0 <0.2 Tetrachloroethylene 0.7 <0.1 1,4 -Dichlorobenzene 7.5 <0.1 Toxaphene 0.5 <0.003 1,2-Dichloroethane 0.5 <0.1 Trichloroethylene 0.5 <0.1 1,1-Dichloroethylene 0.7 <0.1 2,4,5 -Trichlorophenol 400.0 <0.05 2,4-Dinitrotoluene 0.13 <0.05 2,4,6 -Trichlorophenol 2.0 <0.05 Endrin 0.02 <0.0005 2,4,5 -TP (Silvex) 1.0 <0.2 Heptachlor and its Hydroxide 0.008 <0.0005 Vinyl Chloride 0.2 <0.1 4. Metals Determination: Complete one of the following tables (i.e., as applicable) to demonstrate that the residuals do not violate the ceiling concentrations for metals regulated under 15A NCAC 02T .1105. a. For Distribution/Land Application: Fill in the following table with the results of the latest analyses (i.e., on a dry weight basis) for the following metal parameters: Laboratory: Pace Anal =Anal and Date of analysis: =018 Parameter Ceiling Concentration Limits (ClassA & ClassB) (mg/kg) Monthly Average Concentration Limits (Class A Only) (mg/kg) Result (mg/kg) Arsenic 75 41 < 26.5 Cadmium 85 39 < 2.6 Copper 4,300 1,500 < 13.2 Lead 840 300 < 13.2 Mercury 57 17 0.089 Molybdenum 75 n/a < 13.2 Nickel 420 420 < 13.2 Selenium 100 100 < 26.5 Zinc 7,500 2,800 < 26.5 b. For Surface Disposal Unit (landrill): Fill in the following table with the results of the latest analyses (i.e., on a dry weight basis) for the following metal parameters: Laboratory: _ and Date of analysis: _ Distance from Disposal Unit to Boundary to Closest Property Line (meters, check one) Arsenic (mg/kg) Chromium (mg/kg) Nickel (mg/kg) > 0 but < 25 30 200 210 0 > 25 but < 50 34 220 240 > 50 but < 75 39 260 270 ❑ > 75 but < 100 46 300 320 > 100 but < 125 53 360 390 > 125 62 450 420 Result (mg/kg) 5. Nutrient/Micronutrient Determination: Complete the following: a. Total solids: 0 %. b. Fill in the following table with the results of the latest analyses (i.e., on a dry weight basis) for the following nutrient and micronutrient parameters: Laboratory: hce Analytical and Date of analysis: - Parameter Result (mg/kg) Aluminum 3,150 Ammonia -Nitrogen < 122 Calcium 62,300 Magnesium 3,600 Nitrate -Nitrite Nitrogen 32.6 pH (Standard Unit) 9.7 Phosphorus 721 Potassium < 13,200 Sodium < 13,200 Total Kjeldahl Nitrogen 487 c. Using the results listed in Item IL 5b. above, calculate the sodium adsorption ration (SAR): 1, 54 [Note: If residuals contain SAR of 10 or higher, the applicant shall obtain recommendations from the local Cooperative Extension Office, the Department of Agriculture and Consumer Services, the Natural Resource Conservation Service, a North Carolina Licensed Soil Scientist, or an agronomist, prior to land application of residuals. The recommendations shall address the sodium application rate, soil amendments (e.g., gypsum, etc.), or a mechanism for maintaining site integrity and conditions conducive to crop growth]. d. Specify the mineralization rate to be used in calculating the plant available nitro en (PAN) of the residuals: %. This rate is a (check one): N default value, or actually established. If the residuals are not generated from the treatment of municipal or domestic wastewater, ex lain or provide technical justification as to why the selected default value is appropriate to be applied to these residuals: ii e. Calculate the PAN for the residuals (i.e., on a dry weight basis) and fill the results in the following table: Application Method First (111) Year PAN Five -Year Maximum Adjusted PAN (mglkg) (mg/kg) Surface 94 94 Injection/Incorporation 155 155 6. Other Pollutants Determination: S eci whether or not there are any other pollutants of concern in the residuals and provide the results of the latest analyses: 7. Pathogen Reduction: Per 15A NCAC 02T.1106, specify how residuals will meet the pathogen reduction requirements: a. For Distribution/Land Application of Class A or Equivalent: A fecal coliform density that is demonstrated to be less than 1,000 MPN per gram of total dry solids, or A salmonella sp. density that is demonstration to be less than 3 MPN per 4 grams of total dry solids. AND one of the followings (except for non -biological residuals): 0 Alternative 1 [15A NCAC 02T. I 106(b)(3)(A)] - Time/Temperature Compliance. ❑ Alternative 2 [15A NCAC 02T.1106(b)(3)(B)] - Alkaline Treatment. ❑I Alternative 3 [15A NCAC 02T.I 106(b)(3)(C)] - Prior Testing for Enteric Virus/Viable Helminth Ova. J Alternative 4 [15A NCAC 02T.I 106(b)(3)(D)] - No Prior Testing for Enteric Virus/Viable Helminth Ova. Alternative 5 [15A NCAC 02T.1106b (3)(E) -(K)] - Process to Further Reduce Pathogens (PFRP). Specify one: E7 composting, i heat drying, ❑ heat treatment, ❑ thermophilic aerobic digestion, ❑ beta ray irradiation, ❑ gamma ray irradiation, or ❑ pasteurization. b. For Land Application of Class B: 11 Alternative 1 [15A NCAC 02T.I 106(c)(1)] - Fecal Coliform Density Demonstration. El Alternative 2 [15A NCAC 02T.I 106(c)(2 - Process to Significantly Reduce Pathogens (PSRP). Specify one: ❑ aerobic digestion, air drying, ❑ anaerobic digestion, ❑ composting, oi I lime stabilization. c. For Surface Disposal: Select One of the Class A or Equivalent Pathogen Reduction Alternatives in Item II. 7a. above. Select One of the Class B or Equivalent Pathogen Reduction Alternatives in Item II. 7b. above. ❑ Exempt -If Daily Cover Alternative is chosen in Item II.8. below [ 15A NCAC 02T.1 106(a)(2)]. ❑ Not Applicable - Non -Biological Residuals with NO Domestic Wastewater Contribution. 8. Vector Attraction Reduction (VAR): Per 15A NCAC 02T.1107, specify how residuals will meet the VAR requirements: ❑ Alternative 1 [15A NCAC 02T.1107(a)(1)] - 38% Volatile Solids Reduction (Aerobic/Anaerobic Digestion). ❑ Alternative 2 [15A NCAC 02T.I 107(a)(2)] - 40 -Day Bench Scale Test (Anaerobic Digestion). <QAlternative 3 [15A NCAC 02T.I 107(a)(3)] - 30 -Day Bench Scale Test (Aerobic Digestion). ❑ Alternative 4 [15A NCAC 02T.I 107(a)(4)] - Specific Oxygen Uptake Rate Test (Aerobic Digestion). ❑ Alternative 5 [15A NCAC 02T.I 107(a)(5)] - 14 -Day Aerobic Processes. ❑ Alternative 6 [ 15A NCAC 02T. 1107(a)(6)] - Alkaline Stabilization. Alternative 7 [15A NCAC 02T.I 107(a)(7)] - Drying of Stabilized Residuals. 0 Alternative 8 [ 15A NCAC 02T. 1107(a)(8)] - Drying of Unstabilized Residuals. ❑ Alternative 9 [15A NCAC 02T. 1 107(a)(9)] - Injection. ❑ Alternative 10 [15A NCAC 02T.1107(a)(10)] - Incorporation. Q Alternative for Surface Disposal Units Only - Soil/Other Material Cover [15A NCAC 02T.I 107(b)(2)]. Not Applicable - Non -Biological Residuals with NO Domestic Wastewater Contribution. Note: For animal processing residuals, only alternatives 9 or 10 may be chosen due to the nuisance conditions that typically occur when these residuals are applied and left on the land surface. NGMAN FIELD LOADING ESTIMATES Facility Elizabeth City WTP Sampling Date 11/16/2018 % Solids 6.5 Mineralization Rate 0 Gallons per DT 3,689.36 PH 9.7 Sodium Absorpotion 3.54 <5.0 Safe 5.0 - 10.0 Careful Management >15.0 Do Not Land Apply Ratio NITROGEN APPLICATION TKN (mg/Kg) 487 lbs./1,000 gal 0.26 Ammonia Nitrogen (mg/Kg) 122.00 lbs./1,000 gal 0.07 Nitrate -Nitrite (mg/Kg) 32.60 lbs./1,000 gal 0.02 PLANT AVAILABLE NITROGEN SURFACE APPLIED PAN (mg/Kg) 94 lbs./1,000 gal 0.05 PLANT AVAILABLE NITROGEN INJECTED/INCORPORATED APPLIED PAN (mg/Kg) 155 lbs./1,000 gal 0.08 Volatization Rate= 0.5 Surface Application 1.0 Injection/Incorporation EPA METAL LIMITS Class A Ceiling Class B Ceiling Limits (mg/Kg) Limits (mg/Kg) 41 75 39 85 1,500 4,300 300 840 17 57 420 420 100 100 2,800 7,500 1 st Year 2nd Year 3rd Year 4th Year 5th Year HEAVY METAL CONCENTRATION NUTRIENT APPLICATION Potassium lbs./1,000 gal 7.16 Phosphorus lbs./1,000 gal 0.39 Calcium lbs./1,000 gal 33.77 Magnesium lbs./1,000 gal 1.95 Manganese lbs./1,000 gal Sulfur lbs./1,000 gal Molybdenum lbs./1,000 gal 0.01 HEAVY METAL LOADING Arsenic (mg/Kg) 26.50 Arsenic lbs./1,000 gal 0.01 Cadmium (mg/Kg) 2.60 Cadmium lbs./1,000 gal 0.00 Copper (mg/Kg) 13.20 Copper lbs./1,000 gal 0.01 Lead (mg/Kg) 13.20 Lead lbs./1,000 gal 0.01 Mercury (mg/Kg) 0.09 Mercury lbs./1,000 gal 0.00 Nickel (mg/Kg) 13.20 Nickel lbs./1,000 gal 0.01 Selenium (mg/Kg) 26.50 Selenium lbs./1,000 gal 0.01 Zinc (mg/Kg) 26.50 Zinc lbs./1,000 gal 0.01 RESIDUAL NITROGEN CALCULATION 393 Total 94 0.19 Total 155 0.31 Equations I st Yr. PAN (mg/Kg)=(MR x (TKN-NH3))+(VR x NH3)+NOx 2nd Yr PAN (mg/Kg)= 2nd Yr. TKN x (MR/2) 3rd Yr PAN (mg/Kg)= 3rd Yr. TKN x (MR/4) 4th Yr PAN (mg/Kg)= 4th Yr. TKN x (MR/8) 5th Yr PAN (mg/Kg)= 5th Yr. TKN x (MR/16) Surface Application Injection/Incorporation Application Remaining Remaining Organic Organic PAN PAN Nitrogen PAN PAN Nitrogen TKN (mg/kg) (lbs/DT) (M9 Y_-) TKN (mg/kg) (lbs/DT) (mg/Kg) 487 94 0.19 393 487 155 0.31 332 393 0 0.00 393 332 0 0.00 332 393 0 0.00 393 332 0 0.00 332 393 0 0.00 393 332 0 0.00 332 393 0 0.00 393 332 0 0.00 332 Total 94 0.19 Total 155 0.31 Equations I st Yr. PAN (mg/Kg)=(MR x (TKN-NH3))+(VR x NH3)+NOx 2nd Yr PAN (mg/Kg)= 2nd Yr. TKN x (MR/2) 3rd Yr PAN (mg/Kg)= 3rd Yr. TKN x (MR/4) 4th Yr PAN (mg/Kg)= 4th Yr. TKN x (MR/8) 5th Yr PAN (mg/Kg)= 5th Yr. TKN x (MR/16) aceAnalytical —pacelabs.com December 17, 2018 Rececca Miller Elizabeth City 450 Knobbs Creek Elizabeth City, NC 27909 RE: Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 Dear Rececca Miller: Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Enclosed are the analytical results for sample(s) received by the laboratory on November 16, 2018. The results relate only to the samples included in this report. Results reported herein conform to the most current, applicable TNI/NELAC standards and the laboratory's Quality Assurance Manual, where applicable, unless otherwise noted in the body of the report. Some analyses have been subcontracted outside of the Pace Network. The subcontracted laboratory report has been attached. If you have any questions concerning this report, please feel free to contact me. Sincerely, a, +1, �a,i 0 Jt Angela Baioni angela.baioni@pacelabs.com (704)875-9092 Project Manager Enclosures cc: Accounts Payable, City of Elizabeth City Raymond Staten, City of Elizabeth City REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 1 of 39 aceAnalytical —pacelabs.com Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 CERTIFICATIONS Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 Atlanta Certification IDs 110 Technology Parkway Peachtree Corners, GA 30092 North Carolina Certification #: 381 Florida DOH Certification #: E87315 South Carolina Certification #: 98011001 Georgia DW Inorganics Certification #: 812 Texas Certification #: T104704397 -08 -TX Georgia DW Microbiology Certification #: 812 Virginia Certification #: 460204 Pennsylvania Certification IDs 1638 Roseytown Rd Suites 2,3&4, Greensburg, PA 15601 Missouri Certification #: 235 ANAB DOD-ELAP Rad Accreditation #: L2417 Montana Certification #: Cert0082 Alabama Certification #: 41590 Nebraska Certification #: NE -OS -29-14 Arizona Certification #: AZ0734 Nevada Certification #: PA014572018-1 Arkansas Certification New Hampshire/TNI Certification #: 297617 California Certification #: 04222CA New Jersey/TNI Certification M PA051 Colorado Certification #: PA01547 New Mexico Certification #: PA01457 Connecticut Certification #: PH -0694 New York/TNI Certification #: 10888 Delaware Certification North Carolina Certification #: 42706 EPA Region 4 DW Rad North Dakota Certification #: R-190 Florida/TNI Certification #: E87683 Ohio EPA Rad Approval: #41249 Georgia Certification #: C040 Oregon/TNI Certification #: PA200002-010 Guam Certification Pennsylvania/TNI Certification #: 65-00282 Hawaii Certification Puerto Rico Certification M PA01457 Idaho Certification Rhode Island Certification #: 65-00282 Illinois Certification South Dakota Certification Indiana Certification Tennessee Certification #: 02867 Iowa Certification #: 391 Texas/TNI Certification M T104704188-17-3 Kansas/TNI Certification #: E-10358 Utah/TNI Certification #: PA014572017-9 Kentucky Certification #: KY90133 USDA Soil Permit #: P330-17-00091 KY WW Permit #: KY0098221 Vermont Dept. of Health: ID# VT -0282 KY WW Permit #: KY0000221 Virgin Island/PADEP Certification Louisiana DHH/TNI Certification #: LA180012 Virginia/VELAP Certification #: 9526 Louisiana DEQ/TNI Certification #: 4086 Washington Certification #: C868 Maine Certification #: 2017020 West Virginia DEP Certification #: 143 Maryland Certification #: 308 West Virginia DHHR Certification #: 9964C Massachusetts Certification #: M-PA1457 Wisconsin Approve List for Rad Michigan/PADEP Certification #: 9991 Wyoming Certification #: 8TMS-L Charlotte Certification IDs 9800 Kincey Ave. Ste 100, Huntersville, NC 28078 South Carolina Certification #: 99006001 Louisiana/NELAP Certification # LAI 70028 Florida/NELAP Certification #: E87627 North Carolina Drinking Water Certification #: 37706 Kentucky UST Certification #: 84 North Carolina Field Services Certification #: 5342 Virginia/VELAP Certification #: 460221 North Carolina Wastewater Certification M 12 Asheville Certification IDs 2225 Riverside Drive, Asheville, NC 28804 North Carolina Wastewater Certification #: 40 Florida/NELAP Certification M E87648 South Carolina Certification M 99030001 Massachusetts Certification #: M-NC030 Virginia/VELAP Certification #: 460222 North Carolina Drinking Water Certification #: 37712 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 2 of 39 aceAnalytical —pacelabs.com SAMPLE ANALYTE COUNT Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: Pace Project No.: BiMonthly Residuals +Full TCLP 92407889 Analytes Lab ID Sample ID Method Analysts Reported Laboratory 92407889001 WTP Sludge EPA 8081 B PKS 9 PASI-C EPA 601 OD DS 14 PASI-A EPA 601 OD DS 7 PASI-A EPA 7470A JMW1 1 PASI-A EPA 7471B JMW1 1 PASI-A EPA 8270D PKS 18 PASI-C EPA 82608 CL 14 PASI-C SM 2540G-2011 KDF 1 PASI-C ASTM D2974-87 KDF 1 PASI-C EPA 1010A SMK 1 PASI-A EPA 9045D SMK 1 PASI-A EPA 350.1 Rev 2.0 1993 Mod. CJH1 1 PASI-A EPA 351.2 Rev 2.0 1993 MFO 1 PASI-A EPA 353.2 Rev 2.0 1993 MFO 3 PASI-A EPA 365.1 Rev 2.0 1993 MDW 1 PASI-A SM 4500 -CI -E-2011 MVC 1 PASI-A EPA 9014 LEP 1 PASI-PA SM4500S2F-00 PAS 1 PASI-PA EPA 9056A RLC 1 PASI-GA REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 3 of 39 aceAnalytical —pacelabs.com ANALYTICAL RESULTS Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 Sample: WTP Sludge Lab ID: 92407889001 Collected: 11/16/18 09:55 Received: 11/16/18 14:30 Matrix: Solid Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions. Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual 8081 TCLP Pesticides RVE Analytical Method: EPA 8081 B Preparation Method: EPA 3510C mg/kg 265 1 Leachate Method/Date: EPA 1311; 11/26/18 12:05 Initial pH: ; Final pH: 5 ND gamma -BHC (Lindane) ND ug/L 0.50 1 11/27/18 13:19 11/29/18 16:35 58-89-9 Chlordane (Technical) ND ug/L 3.0 1 11/27/18 13:19 11/29/18 16:35 57-74-9 Endrin ND ug/L 0.50 1 11/27/1813:19 11/29/1816:35 72-20-8 Heptachlor ND ug/L 0.50 1 11/27/1813:19 11/29/1816:35 76-44-8 Heptachlor epoxide ND ug/L 0.50 1 11/27/18 13:19 11/29/18 16:35 1024-57-3 Methoxychlor ND ug/L 1000 1 11/27/1813:19 11/29/1816:35 72-43-5 Toxaphene ND ug/L 3.0 1 11/27/1813:19 11/29/1816:35 8001-35-2 Surrogates 13.2 1 11/26/18 15:09 11/28/18 01:12 7439-98-7 Nickel ND Decachlorobiphenyl (S) 77 % 10-138 1 11/27/18 13:19 11/29/18 16:35 2051-24-3 Tetrachloro-m-xylene (S) 73 % 10-110 1 11/27/18 13:19 11/29/18 16:35 877-09-8 6010 MET ICP Analytical Method: EPA 6010D Preparation Method: EPA 3050B Aluminum 3150 mg/kg 265 1 11/26/18 15:09 11/28/18 01:12 7429-90-5 Arsenic ND mg/kg 26.5 1 11/26/18 15:09 11/28/18 01:12 7440-38-2 Cadmium ND mg/kg 2.6 1 11/26/18 15:09 11/28/18 01:12 7440-43-9 Calcium 62300 mg/kg 265 1 11/26/18 15:09 11/28/18 01:12 7440-70-2 Chromium ND mg/kg 13.2 1 11/26/18 15:09 11/28/18 01:12 7440-47-3 Copper ND mg/kg 13.2 1 11/26/18 15:09 11/28/18 01:12 7440-50-8 Lead ND mg/kg 13.2 1 11/26/18 15:09 11/28/18 01:12 7439-92-1 Magnesium 3600 mg/kg 265 1 11/26/18 15:09 11/28/18 01:12 7439-95-4 Molybdenum ND mg/kg 13.2 1 11/26/18 15:09 11/28/18 01:12 7439-98-7 Nickel ND mg/kg 13.2 1 11/26/18 15:09 11/28/18 01:12 7440-02-0 Potassium ND mg/kg 13200 1 11/26/18 15:09 11/28/18 01:12 7440-09-7 Selenium ND mg/kg 26.5 1 11/26/18 15:09 11/28/18 01:12 7782-49-2 Sodium ND mg/kg 13200 1 11/26/18 15:09 11/28/18 01:12 7440-23-5 Zinc ND mg/kg 26.5 1 11/26/18 15:09 11/28/18 01:12 7440-66-6 6010 MET ICP, TCLP Analytical Method: EPA 6010D Preparation Method: EPA 3010A Leachate Method/Date: EPA 1311; 11/29/18 21:42 Initial pH: 9.9; Final pH: 5 Arsenic ND mg/L 0.050 1 11/30/1819:12 12/02/1819:16 7440-38-2 Barium ND mg/L 0.25 1 11/30/1819:12 12/02/1819:16 7440-39-3 Cadmium ND mg/L 0.0050 1 11/30/1819:12 12/02/1819:16 7440-43-9 Chromium ND mg/L 0.050 1 11/30/1819:12 12/02/1819:16 7440-47-3 Lead ND mg/L 0.025 1 11/30/1819:12 12/02/1819:16 7439-92-1 Selenium ND mg/L 0.10 1 11/30/1819:12 12/02/1819:16 7782-49-2 Silver ND mg/L 0.025 1 11/30/1819:12 12/02/1819:16 7440-22-4 7470 Mercury, TCLP Analytical Method: EPA 7470A Preparation Method: EPA 7470A Leachate Method/Date: EPA 1311; 11/29/18 21:42 Initial pH: 9.9; Final pH: 5 Mercury ND mg/L 0.00020 1 12/01/18 22:26 12/03/18 10:49 7439-97-6 7471 Mercury Analytical Method: EPA 7471 B Preparation Method: EPA 7471 B Mercury ND mg/kg 0.089 1 11/28/1814:27 11/29/1812:55 7439-97-6 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 4 of 39 aceAnalytical —pacelabs.com ANALYTICAL RESULTS Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: WTP Sludge Lab ID: 92407889001 Collected: 11/16/18 09:55 Received: 11/16/18 14:30 Matrix: Solid Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions. Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual 8270 MSSV TCLP Sep Funnel Analytical Method: EPA 8270D Preparation Method: EPA 3510C Leachate Method/Date: EPA 1311; 11/26/18 12:05 Initial pH: ; Final pH: 5 1,4 -Dichlorobenzene ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 106-46-7 2,4-Dinitrotoluene ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 121-14-2 Hexachloro-1,3-butadiene ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 87-68-3 Hexachlorobenzene ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 118-74-1 Hexachloroethane ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 67-72-1 2-Methylphenol(o-Cresol) ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 95-48-7 3&4 -Methyl phenol (m&p Cresol) ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 15831-10-4 Nitrobenzene ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 98-95-3 Pentachlorophenol ND ug/L 100 1 11/27/18 08:36 11/27/18 17:38 87-86-5 Pyridine ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 110-86-1 2,4,5 -Trichlorophenol ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 95-95-4 2,4,6 -Trichlorophenol ND ug/L 50.0 1 11/27/18 08:36 11/27/18 17:38 88-06-2 Surrogates Nitrobenzene -d5 (S) 62 % 12-102 1 11/27/18 08:36 11/27/18 17:38 4165-60-0 2-Fluorobiphenyl (S) 64 % 13-107 1 11/27/18 08:36 11/27/18 17:38 321-60-8 Terphenyl-d14 (S) 76 % 21-132 1 11/27/18 08:36 11/27/18 17:38 1718-51-0 Phenol -d6 (S) 18 % 10-110 1 11/27/18 08:36 11/27/18 17:38 13127-88-3 2-Fluorophenol (S) 27 % 10-110 1 11/27/18 08:36 11/27/18 17:38 367-12-4 2,4,6-Tribromophenol (S) 45 % 27-108 1 11/27/18 08:36 11/27/18 17:38 118-79-6 8260 MSV TCLP Analytical Method: EPA 8260B Leachate Method/Date: EPA 1311; 11/28/18 08:35 Benzene ND ug/L 100 20 12/03/1817:53 71-43-2 2-Butanone (MEK) ND ug/L 200 20 12/03/18 17:53 78-93-3 Carbon tetrachloride ND ug/L 100 20 12/03/18 17:53 56-23-5 Chlorobenzene ND ug/L 100 20 12/03/1817:53 108-90-7 Chloroform ND ug/L 100 20 12/03/1817:53 67-66-3 1,4 -Dichlorobenzene ND ug/L 100 20 12/03/1817:53 106-46-7 1,2-Dichloroethane ND ug/L 100 20 12/03/1817:53 107-06-2 1,1-Dichloroethene ND ug/L 100 20 12/03/1817:53 75-35-4 Tetrachloroethene ND ug/L 100 20 12/03/1817:53 127-18-4 Trichloroethene ND ug/L 100 20 12/03/1817:53 79-01-6 Vinyl chloride ND ug/L 100 20 12/03/18 17:53 75-01-4 Surrogates 1,2-Dichloroethane-d4 (S) 104 % 70-130 20 12/03/18 17:53 17060-07-0 Toluene -d8 (S) 109 % 67-135 20 12/03/18 17:53 2037-26-5 4-Bromofluorobenzene (S) 107 % 70-130 20 12/03/18 17:53 460-00-4 254OG Total Percent Solids Analytical Method: SM 2540G-2011 Total Solids 6.5 % 0.000010 1 11/21/18 17:13 Percent Moisture Analytical Method: ASTM D2974-87 Percent Moisture 93.5 % 0.10 1 11/21/18 17:02 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 5 of 39 aceAnalytical —pacelabs.com ANALYTICAL RESULTS Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 Sample: WTP Sludge Lab ID: 92407889001 Collected: 11/16/18 09:55 Received: 11/16/18 14:30 Matrix: Solid Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions. Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual 1010 Flash poi nt,Closed Cup Analytical Method: EPA 1010A Flashpoint >200 deg F 70.0 1 11/25/18 13:13 9045 pH Soil Analytical Method: EPA 9045D pH at 25 Degrees C 9.7 Std. Units 0.10 1 11/26/18 13:31 H3 350.1 Ammonia Analytical Method: EPA 350.1 Rev 2.0 1993 Mod. Preparation Method: EPA 350.1 Rev 2.0 1993 Mod. Nitrogen, Ammonia ND mg/kg 122 1 12/01/18 09:31 12/02/18 16:02 7664-41-7 M1 351.2 Total Kjeldahl Nitrogen Analytical Method: EPA 351.2 Rev 2.0 1993 Preparation Method: EPA 351.2 Rev 2.0 1993 Nitrogen, Kjeldahl, Total 487 mg/kg 480 1 11/26/18 14:30 11/28/18 02:12 7727-37-9 353.2 Nitrogen, NO2/NO3 Analytical Method: EPA 353.2 Rev 2.0 1993 Preparation Method: EPA 353.2 Rev 2.0 1993 Nitrogen, NO2 plus NO3 32.6 mg/kg 30.3 1 12/03/18 11:57 12/04/18 05:55 Nitrogen, Nitrate 32.6 mg/kg 30.3 1 12/03/18 11:57 12/04/18 05:55 14797-55-8 Nitrogen, Nitrite ND mg/kg 15.2 1 12/03/18 11:57 12/04/18 05:55 14797-65-0 365.1 Phosphorus, Total Analytical Method: EPA 365.1 Rev 2.0 1993 Preparation Method: EPA 365.1 Rev 2.0 1993 Phosphorus 721 mg/kg 27.9 1 11/21/18 22:00 11/22/18 02:57 7723-14-0 4500 Chloride in Soil Analytical Method: SM 4500 -CI -E-2011 Preparation Method: SM 4500 -CI -E-2011 Chloride 525 mg/kg 152 1 11/28/18 17:30 11/29/18 00:11 16887-00-6 733C S Reactive Cyanide Analytical Method: EPA 9014 Preparation Method: SW -846 7.3.3.2 Cyanide, Reactive ND mg/kg 15.3 1 12/13/18 16:12 12/13/18 18:35 734S Reactive Sulfide Analytical Method: SM4500S2F-00 Preparation Method: SW -846 7.3.4.2 Sulfide, Reactive ND mg/kg 153 1 12/13/18 16:12 12/13/18 16:25 9056 IC Anions Analytical Method: EPA 9056A Preparation Method: EPA 9056A Sulfate 3470 mg/kg 765 1 11/29/1815:34 11/30/1812:39 14808-79-8 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 6 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 445096 Analysis Method: EPA 7470A QC Batch Method: EPA 7470A Analysis Description: 7470 Mercury TCLP Associated Lab Samples: 92407889001 METHOD BLANK: 2438760 Matrix: Water Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Mercury mg/L ND 0.00020 12/03/1810:20 METHOD BLANK: 2439289 Matrix: Water Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Mercury mg/L ND 0.00020 12/03/1810:25 LABORATORY CONTROL SAMPLE: 2440670 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Mercury mg/L 0.0025 0.0025 98 80-120 LABORATORY CONTROL SAMPLE: 2440671 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Mercury mg/L 0.0025 0.0024 97 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2440672 2440674 MS MSD 92407703001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Mercury mg/L ND 0.0025 0.0025 0.0024 0.0024 93 95 75-125 2 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 7 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 444462 Analysis Method: EPA 7471 B QC Batch Method: EPA 7471 B Analysis Description: 7471 Mercury Associated Lab Samples: 92407889001 METHOD BLANK: 2437624 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Mercury mg/kg ND 0.0060 11/29/18 09:51 LABORATORY CONTROL SAMPLE: 2437625 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Mercury mg/kg 0.083 0.091 109 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2437626 2437627 MS MSD 92408335001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Mercury mg/kg 174 0.061 0.064 213 206 65400 50900 75-125 3 H3,M6 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 8 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 443876 Analysis Method: EPA 6010D QC Batch Method: EPA 30508 Analysis Description: 6010 MET Associated Lab Samples: 92407889001 METHOD BLANK: 2435233 Associated Lab Samples: 92407889001 Parameter Units Matrix: Blank Result Solid Reporting Limit Analyzed Aluminum mg/kg ND 10.0 11/28/18 00:48 Arsenic mg/kg ND 1.0 11/28/18 00:48 Cadmium mg/kg ND 0.10 11/28/18 00:48 Calcium mg/kg ND 10.0 11/28/18 00:48 Chromium mg/kg ND 0.50 11/28/18 00:48 Copper mg/kg ND 0.50 11/28/18 00:48 Lead mg/kg ND 0.50 11/28/18 00:48 Magnesium mg/kg ND 10.0 11/28/18 00:48 Molybdenum mg/kg ND 0.50 11/28/18 00:48 Nickel mg/kg ND 0.50 11/28/18 00:48 Potassium mg/kg ND 500 11/28/18 00:48 Selenium mg/kg ND 1.0 11/28/18 00:48 Sodium mg/kg ND 500 11/28/18 00:48 Zinc mg/kg ND 1.0 11/28/18 00:48 Qualifiers LABORATORY CONTROL SAMPLE: Parameter 2435234 Units Spike Conc. LCS Result LCS % Rec % Rec Limits Aluminum mg/kg 500 498 100 80-120 Arsenic mg/kg 50 43.5 87 80-120 Cadmium mg/kg 50 45.9 92 80-120 Calcium mg/kg 500 502 100 80-120 Chromium mg/kg 50 48.7 97 80-120 Copper mg/kg 50 48.5 97 80-120 Lead mg/kg 50 45.0 90 80-120 Magnesium mg/kg 500 479 96 80-120 Molybdenum mg/kg 50 49.2 98 80-120 Nickel mg/kg 50 46.4 93 80-120 Potassium mg/kg 500 512 102 80-120 Selenium mg/kg 50 41.8 84 80-120 Sodium mg/kg 500 505 101 80-120 Zinc mg/kg 50 43.6 87 80-120 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Qualifiers MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2435235 2435236 MS MSD 92407749007 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Aluminum mg/kg 12200 1120 1040 23700 23500 1020 1080 75-125 1 E,M1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 9 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: Pace Project No.: BiMonthly Residuals +Full TCLP 92407889 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2435235 2435236 MS MSD 92407749007 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Arsenic mg/kg 1.2J 112 104 86.0 78.3 75 74 75-125 9 M1 Cadmium mg/kg 0.101 112 104 91.7 84.3 82 81 75-125 8 Calcium mg/kg 751 1120 1040 1760 1700 90 91 75-125 3 Chromium mg/kg 41.1 112 104 128 123 78 78 75-125 5 Copper mg/kg 14.9 112 104 122 115 96 96 75-125 6 Lead mg/kg 10 112 104 98.6 90.9 79 78 75-125 8 Magnesium mg/kg 322 1120 1040 1560 1500 110 113 75-125 4 Molybdenum mg/kg 0.501 112 104 93.7 86.0 83 82 75-125 9 Nickel mg/kg 3.9 112 104 98.2 90.6 84 83 75-125 8 Potassium mg/kg ND 1120 1040 1440 1360 103 104 75-125 6 Selenium mg/kg ND 112 104 81.9 75.3 73 72 75-125 8 M1 Sodium mg/kg ND 1120 1040 1040J 971J 91 91 75-125 Zinc mg/kg 10.7 112 104 106 97.8 85 83 75-125 8 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 10 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 445095 Analysis Method: EPA 6010D QC Batch Method: EPA 3010A Analysis Description: 6010 MET TCLP Associated Lab Samples: 92407889001 METHOD BLANK: 2438760 2440648 Matrix: Water Arsenic Associated Lab Samples: 92407889001 Barium mg/L Cadmium mg/L Chromium mg/L Blank Reporting Selenium Parameter Units Result Limit Analyzed Arsenic mg/L ND 0.050 12/02/1818:34 Barium mg/L ND 0.25 12/02/1818:34 Cadmium mg/L ND 0.0050 12/02/1818:34 Chromium mg/L ND 0.050 12/02/1818:34 Lead mg/L ND 0.025 12/02/1818:34 Selenium mg/L ND 0.10 12/02/1818:34 Silver mg/L ND 0.025 12/02/1818:34 METHOD BLANK: 2439289 2440648 Matrix: Water Arsenic Associated Lab Samples: 92407889001 Barium mg/L Cadmium mg/L Chromium mg/L Blank Reporting Selenium Parameter Units Result Limit Analyzed Arsenic mg/L ND 0.050 12/02/1818:41 Barium mg/L ND 0.25 12/02/1818:41 Cadmium mg/L ND 0.0050 12/02/1818:41 Chromium mg/L ND 0.050 12/02/1818:41 Lead mg/L ND 0.025 12/02/1818:41 Selenium mg/L ND 0.10 12/02/1818:41 Silver mg/L ND 0.025 12/02/1818:41 LABORATORY CONTROL SAMPLE: 2440648 Parameter Units Arsenic mg/L Barium mg/L Cadmium mg/L Chromium mg/L Lead mg/L Selenium mg/L Silver mg/L Qualifiers Qualifiers Spike Conc. LCS Result LCS % Rec % Rec Limits 2.5 2.4 98 80-120 2.5 2.4 96 80-120 2.5 2.4 96 80-120 2.5 2.5 98 80-120 2.5 2.3 91 80-120 2.5 2.4 97 80-120 1.2 1.2 99 80-120 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Qualifiers LABORATORY CONTROL SAMPLE: 2440650 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Arsenic mg/L 2.5 2.4 96 80-120 Barium mg/L 2.5 2.5 100 80-120 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 11 of 39 aceAnalytical -pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 LABORATORY CONTROL SAMPLE: 2440650 2440652 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Cadmium mg/L 2.5 2.4 97 80-120 Chromium mg/L 2.5 2.5 99 80-120 Lead mg/L 2.5 2.4 94 80-120 Selenium mg/L 2.5 2.5 98 80-120 Silver mg/L 1.2 1.2 99 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2440651 2440652 MS MSD 92403346001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Arsenic mg/L ND 2.5 2.5 2.4 2.4 96 97 75-125 1 Barium mg/L 1.2 2.5 2.5 3.6 3.6 97 94 75-125 2 Cadmium mg/L ND 2.5 2.5 2.4 2.4 95 96 75-125 1 Chromium mg/L ND 2.5 2.5 2.4 2.5 96 98 75-125 2 Lead mg/L ND 2.5 2.5 2.3 2.3 90 91 75-125 1 Selenium mg/L ND 2.5 2.5 2.4 2.4 96 96 75-125 0 Silver mg/L ND 1.2 1.2 1.2 1.2 98 99 75-125 1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 12 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 445234 Analysis Method: EPA 8260B QC Batch Method: EPA 82608 Analysis Description: 8260 MSV TCLP Associated Lab Samples: 92407889001 METHOD BLANK: 2435914 Associated Lab Samples: 92407889001 Parameter Units Matrix: Blank Result Water Reporting Limit Analyzed 1,1-Dichloroethene ug/L ND 5.0 12/03/1812:17 1,2-Dichloroethane ug/L ND 5.0 12/03/1812:17 1,4 -Dichlorobenzene ug/L ND 5.0 12/03/1812:17 2-Butanone (MEK) ug/L ND 10.0 12/03/18 12:17 Benzene ug/L ND 5.0 12/03/1812:17 Carbon tetrachloride ug/L ND 5.0 12/03/18 12:17 Chlorobenzene ug/L ND 5.0 12/03/1812:17 Chloroform ug/L ND 5.0 12/03/1812:17 Tetrachloroethene ug/L ND 5.0 12/03/1812:17 Trichloroethene ug/L ND 5.0 12/03/1812:17 Vinyl chloride ug/L ND 5.0 12/03/18 12:17 1,2-Dichloroethane-d4 (S) % 107 70-130 12/03/18 12:17 4-Bromofluorobenzene (S) % 120 70-130 12/03/18 12:17 Toluene -d8 (S) % 100 67-135 12/03/18 12:17 Qualifiers LABORATORY CONTROL SAMPLE: Parameter 2441182 Units Spike Conc. LCS Result LCS % Rec % Rec Limits 1,1-Dichloroethene ug/L 50 50.4 101 70-130 1,2-Dichloroethane ug/L 50 47.1 94 70-130 1,4 -Dichlorobenzene ug/L 50 44.2 88 70-130 2-Butanone (MEK) ug/L 100 103 103 64-135 Benzene ug/L 50 48.0 96 70-130 Carbon tetrachloride ug/L 50 47.1 94 70-130 Chlorobenzene ug/L 50 44.7 89 70-130 Chloroform ug/L 50 46.7 93 70-130 Tetrachloroethene ug/L 50 45.1 90 69-130 Trichloroethene ug/L 50 51.3 103 70-130 Vinyl chloride ug/L 50 49.6 99 70-131 1,2-Dichloroethane-d4 (S) % 105 70-130 4-Bromofluorobenzene (S) % 107 70-130 Toluene -d8 (S) % 94 67-135 Z,E,II BEI Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Qualifiers MS MSD 92407539001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual 1,1-Dichloroethene ug/L ND 400 400 262 271 66 68 81-154 3 M1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 13 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2441183 2441184 MS MSD 92407539001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual 1,2-Dichloroethane ug/L ND 400 400 224 276 56 69 73-137 21 M1 1,4 -Dichlorobenzene ug/L ND 400 400 207 260 52 65 70-133 23 M1 2-Butanone (MEK) ug/L ND 800 800 503 659 63 82 60-139 27 Benzene ug/L ND 400 400 233 295 58 74 72-151 24 M1 Carbon tetrachloride ug/L ND 400 400 243 288 61 72 70-143 17 M1 Chlorobenzene ug/L ND 400 400 213 262 53 66 70-138 21 M1 Chloroform ug/L ND 400 400 225 291 56 73 74-139 26 M1 Tetrachloroethene ug/L ND 400 400 207 245 52 61 59-143 17 M1 Trichloroethene ug/L ND 400 400 401 488 100 122 77-147 20 Vinyl chloride ug/L ND 400 400 239 228 60 57 70-156 4 M1 1,2-Dichloroethane-d4 (S) % 104 107 70-130 4-Bromofluorobenzene (S) % 103 98 70-130 Toluene-d8(S) % 102 101 67-135 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 14 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 444121 Analysis Method: EPA 8081 B QC Batch Method: EPA 351 OC Analysis Description: 8081 TCLP Pesticides RV Associated Lab Samples: 92407889001 METHOD BLANK: 2435309 Associated Lab Samples: 92407889001 Parameter Chlordane (Technical) Endrin gamma -BHC (Lindane) Heptachlor Heptachlor epoxide Methoxychlor Toxaphene Decachlorobiphenyl (S) Tetrachloro-m-xylene (S) Matrix: Water Units Blank Result Reporting Limit Analyzed ug/L ND 3.0 11/29/1819:34 ug/L ND 0.50 11/29/1819:34 ug/L ND 0.50 11/29/1819:34 ug/L ND 0.50 11/29/1819:34 ug/L ND 0.50 11/29/1819:34 ug/L ND 1000 11/29/1819:34 ug/L ND 3.0 11/29/1819:34 % 79 10-138 11/29/18 19:34 % 70 10-110 11/29/18 19:34 Qualifiers Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 LABORATORY CONTROL SAMPLE: Parameter 2436173 Units Spike Conc. LCS Result LCS % Rec % Rec Limits Qualifiers Endrin ug/L 1.2 0.93 74 20-134 gamma -BHC (Lindane) ug/L 1.2 0.88 70 20-118 Heptachlor ug/L 1.2 0.91 73 20-142 Heptachlor epoxide ug/L 1.2 0.88 71 22-133 Methoxychlor ug/L 3.8 ND 78 44-150 Decachlorobiphenyl (S) % 3.8 ND 79 10-138 Tetrachloro-m-xylene (S) % 60 10-110 MATRIX SPIKE SAMPLE: Parameter 2436174 Units 92408140003 Result Spike Conc. MS Result MS % Rec % Rec Limits Qualifiers Endrin ug/L ND 1.2 0.97 77 21-133 gamma -BHC (Lindane) ug/L ND 1.2 0.98 78 24-119 Heptachlor ug/L ND 1.2 1.2 96 16-128 Heptachlor epoxide ug/L ND 1.2 1.0 82 50-150 Methoxychlor ug/L ND 3.8 ND 79 50-150 Decachlorobiphenyl (S) % 186 10-138 SO Tetrachloro-m-xylene (S) % 60 10-110 SAMPLE DUPLICATE: 2436175 92408140004 Dup Parameter Units Result Result RPD Qualifiers Chlordane (Technical) ug/L ND ND Endrin ug/L ND ND Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 15 of 39 aceAnalytical —pacelabs.com Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 SAMPLE DUPLICATE: 2436175 Parameter gamma -BHC (Lindane) Heptachlor Heptachlor epoxide Methoxychlor Toxaphene Decachlorobiphenyl (S) Tetrachloro-m-xylene (S) QUALITY CONTROL DATA Units 92408140004 Result Dup Result ug/L ND ND ug/L ND ND ug/L ND ND ug/L ND ND ug/L ND ND % 757 1010 1590 2110 RPD Qualifiers 29 S3 28 S3 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 16 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 444067 Analysis Method: EPA 8270D QC Batch Method: EPA 3510C Analysis Description: 8270D TCLP MSSV Associated Lab Samples: 92407889001 METHOD BLANK: 2435309 Associated Lab Samples: 92407889001 Parameter Units Matrix: Blank Result Water Reporting Limit Analyzed 1,4 -Dichlorobenzene ug/L ND 50.0 11/27/1815:35 2,4,5 -Trichlorophenol ug/L ND 50.0 11/27/1815:35 2,4,6 -Trichlorophenol ug/L ND 50.0 11/27/1815:35 2,4-Dinitrotoluene ug/L ND 50.0 11/27/1815:35 2-Methylphenol(o-Cresol) ug/L ND 50.0 11/27/1815:35 3&4 -Methyl phenol (m&p Cresol) ug/L ND 50.0 11/27/18 15:35 Hexachloro-1,3-butadiene ug/L ND 50.0 11/27/1815:35 Hexachlorobenzene ug/L ND 50.0 11/27/1815:35 Hexachloroethane ug/L ND 50.0 11/27/1815:35 Nitrobenzene ug/L ND 50.0 11/27/1815:35 Pentachlorophenol ug/L ND 100 11/27/1815:35 Pyridine ug/L ND 50.0 11/27/1815:35 2,4,6-Tribromophenol (S) % 59 27-108 11/27/18 15:35 2-Fluorobiphenyl (S) % 62 13-107 11/27/18 15:35 2-Fluorophenol(S) % 30 10-110 11/27/1815:35 Nitrobenzene -d5 (S) % 60 12-102 11/27/18 15:35 Phenol -d6 (S) % 18 10-110 11/27/18 15:35 Terphenyl-d14 (S) % 52 21-132 11/27/18 15:35 Qualifiers LABORATORY CONTROL SAMPLE: Parameter 2435945 Units Spike Conc. LCS Result LCS % Rec % Rec Limits 1,4 -Dichlorobenzene ug/L 500 257 51 10-110 2,4,5 -Trichlorophenol ug/L 500 336 67 39-108 2,4,6 -Trichlorophenol ug/L 500 334 67 40-104 2,4-Dinitrotoluene ug/L 500 418 84 42-109 2-Methylphenol(o-Cresol) ug/L 500 250 50 31-110 3&4 -Methyl phenol (m&p Cresol) ug/L 500 210 42 30-110 Hexachloro-1,3-butadiene ug/L 500 227 45 10-110 Hexachlorobenzene ug/L 500 395 79 39-121 Hexachloroethane ug/L 500 223 45 10-110 Nitrobenzene ug/L 500 292 58 32-101 Pentachlorophenol ug/L 1000 605 61 18-108 Pyridine ug/L 500 164 33 10-110 2,4,6-Tribromophenol (S) % 74 27-108 2-Fluorobiphenyl (S) % 61 13-107 2-Fluorophenol(S) % 30 10-110 Nitrobenzene-d5(S) % 55 12-102 Phenol -d6 (S) % 20 10-110 Terphenyl-d14 (S) % 68 21-132 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Qualifiers Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 17 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 MATRIX SPIKE SAMPLE: 2435946 92408140003 Spike MS MS % Rec Parameter Units Result Conc. Result % Rec Limits Qualifiers 1,4 -Dichlorobenzene ug/L ND 500 303 61 30-150 2,4,5 -Trichlorophenol ug/L ND 500 329 66 30-150 2,4,6 -Trichlorophenol ug/L ND 500 179J 36 30-150 2,4-Dinitrotoluene ug/L ND 500 305 61 30-150 2-Methylphenol(o-Cresol) ug/L ND 500 258 52 30-150 3&4 -Methyl phenol (m&p Cresol) ug/L ND 500 230J 34 30-150 Hexachloro-1,3-butadiene ug/L ND 500 273 55 30-150 Hexachlorobenzene ug/L ND 500 341 68 30-150 Hexachloroethane ug/L ND 500 280 56 30-150 Nitrobenzene ug/L ND 500 300 60 30-150 Pentachlorophenol ug/L ND 1000 475J 47 30-150 Pyridine ug/L ND 500 129J 26 30-150 M1 2,4,6-Tribromophenol (S) % 58 27-108 2-Fluorobiphenyl (S) % 66 13-107 2-Fluorophenol(S) % 32 10-110 Nitrobenzene -d5 (S) % 57 12-102 Phenol -d6 (S) % 21 10-110 Terphenyl-d14 (S) % 56 21-132 SAMPLE DUPLICATE: 2435947 92408140004 Dup Parameter Units Result Result RPD Qualifiers 1,4 -Dichlorobenzene ug/L ND ND 2,4,5 -Trichlorophenol ug/L ND ND 2,4,6 -Trichlorophenol ug/L ND ND 2,4-Dinitrotoluene ug/L ND ND 2-Methylphenol(o-Cresol) ug/L ND ND 3&4 -Methyl phenol (m&p Cresol) ug/L ND ND Hexachloro-1,3-butadiene ug/L ND ND Hexachlorobenzene ug/L ND ND Hexachloroethane ug/L ND ND Nitrobenzene ug/L ND ND Pentachlorophenol ug/L ND ND Pyridine ug/L ND ND 2,4,6-Tribromophenol (S) % 25 20 25 S2 2-Fluorobiphenyl (S) % 32 73 78 2-Fluorophenol(S) % 5 8 39 S2 Nitrobenzene -d5 (S) % 31 66 73 Phenol -d6 (S) % 8 8 1 S2 Terphenyl-d`14(S) % 31 71 80 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 18 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 443749 Analysis Method: ASTM D2974-87 QC Batch Method: ASTM D2974-87 Analysis Description: Dry Weight/Percent Moisture Associated Lab Samples: 92407889001 SAMPLE DUPLICATE: 2434754 92407909001 Dup Parameter Units Result Result RPD Qualifiers Percent Moisture % 28.0 28.3 1 SAMPLE DUPLICATE: 2434755 92408288006 Dup Parameter Units Result Result RPD Qualifiers Percent Moisture % 15.5 15.3 1 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 19 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 443832 Analysis Method: EPA 1010A QC Batch Method: EPA 1010A Analysis Description: 1010 Flash Point, Closed Cup Associated Lab Samples: 92407889001 SAMPLE DUPLICATE: 2435113 35431464001 Dup Parameter Units Result Result RPD Qualifiers Flashpoint deg F 177.00 179.00 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 20 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 443878 Analysis Method: EPA 9045D QC Batch Method: EPA 9045D Analysis Description: 9045 pH Associated Lab Samples: 92407889001 SAMPLE DUPLICATE: 2435238 Parameter pH at 25 Degrees C 92407889001 Dup Units Result Result RPD Qualifiers Std. Units 9.7 9.7 0 H3 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 21 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 445009 Analysis Method: EPA 350.1 Rev 2.0 1993 Mod. QC Batch Method: EPA 350.1 Rev 2.0 1993 Mod. Analysis Description: 350.1 Ammonia Associated Lab Samples: 92407889001 METHOD BLANK: 2439852 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Nitrogen, Ammonia mg/kg ND 9.1 12/02/18 15:59 LABORATORY CONTROL SAMPLE: 2439853 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Nitrogen, Ammonia mg/kg 472 451 96 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2439854 2439855 MS MSD 92407889001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Nitrogen, Ammonia mg/kg ND 7110 6990 5100 4850 72 69 90-110 5 M1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 22 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 443857 Analysis Method: EPA 351.2 Rev 2.0 1993 QC Batch Method: EPA 351.2 Rev 2.0 1993 Analysis Description: 351.2 TKN Associated Lab Samples: 92407889001 METHOD BLANK: 2435166 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Nitrogen, Kjeldahl, Total mg/kg ND 50.0 11/28/18 02:06 LABORATORY CONTROL SAMPLE: 2435167 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Nitrogen, Kjeldahl, Total mg/kg 741 705 95 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2435168 2435169 MS MSD 92406196001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Nitrogen, Kjeldahl, Total mg/kg 46700 970 887 46400 53400 -32 751 90-110 14 M6, R1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 23 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 445204 Analysis Method: EPA 353.2 Rev 2.0 1993 QC Batch Method: EPA 353.2 Rev 2.0 1993 Analysis Description: 353.2 Nitrate + Nitrite Associated Lab Samples: 92407889001 Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 METHOD BLANK: 2441026 2441028 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting MSD Parameter Units Result Limit Analyzed Qualifiers Nitrogen, Nitrate mg/kg ND 2.0 12/04/18 05:52 Nitrogen, Nitrite mg/kg ND 0.99 12/04/18 05:52 Nitrogen, NO2 plus NO3 mg/kg ND 2.0 12/04/18 05:52 LABORATORY CONTROL SAMPLE: 2441027 Result % Rec % Rec Limits RPD Qual Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Nitrogen, Nitrate mg/kg 15 15.6 104 90-110 Nitrogen, Nitrite mg/kg 10 10.2 102 90-110 Nitrogen, NO2 plus NO3 mg/kg 25 25.8 103 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2441028 2441029 MS MSD 92407889001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Nitrogen, Nitrate mg/kg 32.6 230 229 282 278 108 107 90-110 2 Nitrogen, Nitrite mg/kg ND 154 152 159 155 102 101 90-110 2 Nitrogen, NO2 plus NO3 mg/kg 32.6 384 381 441 433 106 105 90-110 2 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 24 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 443774 Analysis Method: EPA 365.1 Rev 2.0 1993 QC Batch Method: EPA 365.1 Rev 2.0 1993 Analysis Description: 365.1 Phosphorus, Total Associated Lab Samples: 92407889001 METHOD BLANK: 2434954 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Phosphorus mg/kg ND 1.9 11/22/18 02:09 LABORATORY CONTROL SAMPLE: 2434955 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Phosphorus mg/kg 49 49.7 101 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2434956 2434957 MS MSD 92407977001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Phosphorus mg/kg 203 95.6 93.9 281 315 82 120 90-110 12 M1,R1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 25 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 444558 Analysis Method: SM 4500 -CI -E-2011 QC Batch Method: SM 4500 -CI -E-2011 Analysis Description: 4500 Chloride Associated Lab Samples: 92407889001 METHOD BLANK: 2438026 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Chloride mg/kg ND 10.0 11/28/1823:16 LABORATORY CONTROL SAMPLE: 2438027 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Chloride mg/kg 200 203 102 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 2438028 2438029 MS MSD 92407239001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Chloride mg/kg 518 345 346 913 919 114 116 90-110 1 M1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 26 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 323851 Analysis Method: EPA 9014 QC Batch Method: SW -846 7.3.3.2 Analysis Description: 733C Reactive Cyanide Associated Lab Samples: 92407889001 METHOD BLANK: 1578532 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Cyanide, Reactive mg/kg ND 1.0 12/13/18 18:20 LABORATORY CONTROL SAMPLE: 1578533 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Cyanide, Reactive mg/kg 100 ND 0 0-8 SAMPLE DUPLICATE: 1578534 30274002001 Dup Parameter Units Result Result RPD Qualifiers Cyanide, Reactive mg/kg 0.99 U ND Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 27 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 323852 Analysis Method: SM4500S2F-00 QC Batch Method: SW -846 7.3.4.2 Analysis Description: 734S Reactive Sulfide Associated Lab Samples: 92407889001 METHOD BLANK: 1578535 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfide, Reactive mg/kg ND 10 12/13/18 16:25 LABORATORY CONTROL SAMPLE: 1578536 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Sulfide, Reactive mg/kg 200 43.9 22 0-52 SAMPLE DUPLICATE: 1578537 30274002001 Dup Parameter Units Result Result RPD Qualifiers Sulfide, Reactive mg/kg 9.9 U ND Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 28 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 QC Batch: 17906 Analysis Method: EPA 9056A QC Batch Method: EPA 9056A Analysis Description: 9056 IC Anions Associated Lab Samples: 92407889001 METHOD BLANK: 80463 Matrix: Solid Associated Lab Samples: 92407889001 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfate mg/kg ND 49.8 11/30/1810:43 LABORATORY CONTROL SAMPLE: 80464 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Sulfate mg/kg 99.7 108 109 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 80465 80466 MS MSD 2611783001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Sulfate mg/kg 6680 677 681 7020 7080 51 59 90-110 1 E Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 29 of 39 Pace Analytical Services, LLC ceAnalX cal ® 9800 Kiney Ave. Suite 100 Huntersville, NC 28078 www.pacelabs.com (704)875-9092 QUALIFIERS Project: BiMonthly Residuals +Full TCLP Pace Project No.: 92407889 DEFINITIONS DF - Dilution Factor, if reported, represents the factor applied to the reported data due to dilution of the sample aliquot. ND - Not Detected at or above adjusted reporting limit. TNTC - Too Numerous To Count J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. MDL -Adjusted Method Detection Limit. PQL - Practical Quantitation Limit. RL - Reporting Limit - The lowest concentration value that meets project requirements for quantitative data with known precision and bias for a specific analyte in a specific matrix. S - Surrogate 1,2-Diphenylhydrazine decomposes to and cannot be separated from Azobenzene using Method 8270. The result for each analyte is a combined concentration. Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values. LCS(D) - Laboratory Control Sample (Duplicate) MS(D) - Matrix Spike (Duplicate) DUP - Sample Duplicate RPD - Relative Percent Difference NC - Not Calculable. SG - Silica Gel - Clean -Up U - Indicates the compound was analyzed for, but not detected. Acid preservation may not be appropriate for 2 Chloroethylvinyl ether. A separate vial preserved to a pH of 4-5 is recommended in SW846 Chapter 4 for the analysis of Acrolein and Acrylonitrile by EPA Method 8260. N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for each analyte is a combined concentration. Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes. TNI -The NELAC Institute. LABORATORIES PASI-A Pace Analytical Services - Asheville PASI-C Pace Analytical Services - Charlotte PASI-GA Pace Analytical Services - Atlanta, GA PASI-PA Pace Analytical Services - Greensburg ANALYTE QUALIFIERS E Analyte concentration exceeded the calibration range. The reported result is estimated. H3 Sample was received or analysis requested beyond the recognized method holding time. M1 Matrix spike recovery exceeded QC limits. Batch accepted based on laboratory control sample (LCS) recovery. M6 Matrix spike and Matrix spike duplicate recovery not evaluated against control limits due to sample dilution. R1 RPD value was outside control limits. SO Surrogate recovery outside laboratory control limits. S2 Surrogate recovery outside laboratory control limits due to matrix interferences (confirmed by similar results from sample re -analysis). S3 Surrogate recovery exceeded laboratory control limits. Analyte presence below reporting limits in associated sample. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 12/17/2018 03:27 PM without the written consent of Pace Analytical Services, LLC. Page 30 of 39 aceAnalytical —pacelabs.com QUALITY CONTROL DATA CROSS REFERENCE TABLE Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: Pace Project No.: BiMonthly Residuals +Full TCLP 92407889 Analytical Lab ID Sample ID QC Batch Method QC Batch Analytical Method Batch 92407889001 WTP Sludge EPA 3510C 444121 EPA 8081 B 444746 92407889001 WTP Sludge EPA 3050B 443876 EPA 6010D 444044 92407889001 WTP Sludge EPA 3010A 445095 EPA 6010D 445097 92407889001 WTP Sludge EPA 7470A 445096 EPA 7470A 445146 92407889001 WTP Sludge EPA 7471 B 444462 EPA 7471 B 444512 92407889001 WTP Sludge EPA 3510C 444067 EPA 8270D 444185 92407889001 WTP Sludge EPA 8260B 445234 92407889001 WTP Sludge SM 2540G-2011 443923 92407889001 WTP Sludge ASTM D2974-87 443749 92407889001 WTP Sludge EPA 1010A 443832 92407889001 WTP Sludge EPA 9045D 443878 92407889001 WTP Sludge EPA 350.1 Rev 2.0 1993 445009 EPA 350.1 Rev 2.0 1993 445116 Mod. Mod. 92407889001 WTP Sludge EPA 351.2 Rev 2.0 1993 443857 EPA 351.2 Rev 2.0 1993 444057 92407889001 WTP Sludge EPA 353.2 Rev 2.0 1993 445204 EPA 353.2 Rev 2.0 1993 445273 92407889001 WTP Sludge EPA 365.1 Rev 2.0 1993 443774 EPA 365.1 Rev 2.0 1993 443795 92407889001 WTP Sludge SM 4500 -CI -E-2011 444558 SM 4500 -CI -E-2011 444577 92407889001 WTP Sludge SW -846 7.3.3.2 323851 EPA 9014 323927 92407889001 WTP Sludge SW -846 7.3.4.2 323852 SM4500S2F-00 323931 92407889001 WTP Sludge EPA 9056A 17906 EPA 9056A 17985 Date: 12/17/2018 03:27 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 31 of 39 Document Name: OocymentRevised: February7, 2016 g��,��+�_� Sample Condition Upon Receipt(SCUR Page 10 / f 2 { ,�'d�fl�Cj €}ocument No.: Issuing Authority: � F-CAR-05-033-Rev.05 Pace Carolinas QuOtV Office Laboratory receiving samples: Rales h Mechanit svilie❑ Asheville ❑ Eden❑ Greenwood F1Ht�ntersvllle ❑ 8 ❑ Client Name; Project ff: WO : 92407889 upon kecei0t Courier: ❑Fed Ex ❑UPS ❑USPS ❑Cdlent ❑ Commercial []Pace ❑Other: 92407889 Custody, Seal Present? []Yes Jo Seals Intact? ❑Y� �" n,4.l iial.% Parson Examining Contanw t ( I [:] 6thaOther"SiologtcalTissue Frozen? Packing Material: ❑Bubble Wrap ❑Bubble Sags E39one ❑yam ❑NoJ/A Thermometer: O� Type of lee:et ❑Blue []None ❑IR6un ID: Cooler Temp ('C); 1 1 Correction Factor: Add/Subtract ('C) -f o ' t Temp should be above freezing to 6'C Cooler Temp Corrected ('C): ❑samples out of temp criteria. Samples on lea, cooling process has begun USDA Regulated Soil (/A water sample} a foreign source Did samples originate in a quarantine zone within the United States: CA, NY, or SC (check maps)? ��ud nHawaii arll annd from Rim)? ©Yes (� ornat fly, Chain of Custody Present? Samples Arrived within Hold Short Hcld Time Analysis 1<: Rush Tura Around Time Req Sufficient Volume? Correct Containers Used? .Pace Cantainers Used? Sample Labels Match COC? -Includes Date/Time/tu/Anarys Headspace in VOA Vials (n5-6mm; Trip Blank Present? Trip Blank Custody Seals Present? COMMENTS/SAMPLE DISCREPANCY ctiENT NOTIFICATION/RESOLUTION Person contacted: es ❑Na N/A L es ❑No ❑NIA Z• 5 No ❑N/A 3. Yeso NIA 4. es No ❑NIA 5. LJTes ❑Na -F—INIA 6. No N/At ❑No ❑N/R Yes ❑No N/A 10. ❑Yes ❑No N/A 1 11. oate/Time: Lot ID of split containers: Field Data Required? []Yes ❑No � -Date: Project Manager SCilRF Review, �G Data: Project Manager SRF Review: Page 32 of 39 Document Name: Sample Coneliflan Upon Rec, aCE i Document Na: *Check mark tap half of box if pH and/or decfdorination is verified and within the acceptance range for preservation Exceptlans. VOA, Colifarrn, TOC, Oil and Grease, ORO/8015 (water) DCC, U,4g **Bottom half of box is to list number of bottle Document Revised: February 7, 2018 Page 1 of 2 Issuing Authority: Pace Carolinas Quality office Project # WO# : 92407889---- PM; AMB Clue Date: 12/04/18 CLIENT: 92 -Elizabeth y m Z m 4 C a n E N 7 a 'n z u 6 C 7 J E vvq�� 4 m y a 6 C a d E a a m ¢ Z C om. y a m u Nf`j v Q ey� N s a. V1 i n v Q T E o Z 4 m ¢ Z N a E N a m N n o 0 A = o. n a m U E 7J a tN�x y n ¢ w e7i l7 a a 4 ri C7 d U G o M O a y a y A 6 .{ C.t' a N vQv}} rV E ua} m t7 a J7 a < d u O E T l� p N d > 'n C] L7 7 c Q ? d% @ z m 4 7 E 6d1 C7 Q \ ? O Y m w u, CS 7 y 0. N a t7 ¢ W y +v E ut N a vs t < v a+ E o res 6 us w O r� Z u of 0. m m ° C a � L ? w ¢ u G 4 O C m E E a o m• 1 ..� —11— ncuuKfl-tlan ofnce (i.e. 2 3 4 5 6 7 8 4 m 11 Q pH Adjustment Log for Preserved Samples Sample I0 Type of Preservativa pH upon receipt Cate preservation adjusted Time preservation adjusted Amount of Preservative added I nt ft ..� —11— ncuuKfl-tlan ofnce (i.e. Note: Whenever there is a d[screpancy amirting warm rHranna ComPua11« �= w,�,, art �• - - out of hold, Sncorrect preservative, out of temp, incorrect containers. ' Page 33 of 39 6E ;0 bE abed (WAS h - - — — p9julegdma V i �l CEJ Q ; � s luuS 4ojen 4BlaeS�vois�0 L L a UA)�I c ua pe,�e=op o � w 3 / (NUJ 8u1i414O lenplseM v 21 w C. dwef J9 o f� `V C� 0 a L L 70 _°,f ��Ix LL CL z mm :33 a L L% O o ,R 9� �( L .. r E 7 -. 01 YYJ x F rd Q X Sn d E � O rN1A j;58j S(S/LjE[Jb't ' i MID Iougl eW VSLBN a g HOUN l0H s a 2 l CONH > 'OS'H $ paruaseaduflX X X >C k 'G C3 N N N a a Sb3NftllNp� dp p v ` t9� ` N011'327100IVdN313ldvivs A T LL LU .Q y T 9 F f o x V ll! O O a 5� m ). _o y y5 {d =-O EMS=D) 3dAl OldW*IS m a I 12 Q o �Q � t2 rr pp flx �w w 2 � LU 5 t42 yp (31 z ' #� W3tE � t (A U d W a a' ANALYTICAL ENVIRONMENTAL SERVICES, INC. AES November 30, 2018 Angela Baioni Pace Analytical Services, Inc. 9800 KINCEY AVE STE 100 HUNTERSVILLE NC 28078-8400 RE: 92407889 Dear Angela Baioni: Order No: 1811K19 Analytical Environmental Services, Inc. received 1 samples on November 21, 2018 9:52 am for the analyses presented in following report. No problems were encountered during the analyses. Additionally, all results for the associated Quality Control samples were within EPA and/or AES established limits. Any discrepancies associated with the analyses contained herein will be noted and submitted in the form of a project Case Narrative. AES' certifications are as follows: -NELAP/Florida State Laboratory ID E87582 for analysis of Non -Potable Water, Solid & Chemical Materials, Air & Emissions for Organics, and Drinking Water Microbiology & Metals, effective 07/01/18-06/30/19. -North Carolina Certification number 562 for analysis of Surface Water, Groundwater, Effluent, effective until 12/31/18. -South Carolina Environmental Laboratory Certification number 98016003 effective until 6/30/19. These results relate only to the items tested. This report may only be reproduced in full and with written permission from the laboratory. If you have any questions regarding these test results, please feel free to call. Sincerely, Jessica Shilling Project Manager 3080 Presi4ential Drive • Atlanta, Georgia 30340 -Tel: 770.457.8177 • Fax: 770.457-S 188 • Toll F.,e:800.972.4889 www.aesatlanta.com Page 35 of 39 Page 1 of 5 m z L L CN * F, Fid y soon. ��'� ■iii■ �� ��� ■viii is NONE■ � ■■■■■ ■■■■■gi{p ME 000i■i■� a 1 n MEN",[ ■N■U `I q^F . —1L '5'f �r .� i1 r. �•.'µ� �µ� lai t'n a -ley 111rt .�,k xf'I'q RIt] ''a'7 lot I 7 i1 y 4i i cq 1 'J" 46 to 3 -X :{� {µreeea CO (LLI CD m a V O M co d ;L0 .o N Q) rn m 0- Analytical Environmental Services, Inc Date: 30 -Nov -18 Client: Pace Analytical Services, Inc. Client Sample ID: WTP SLUDGE Project Name: 92407889 Collection Date: 11/16/2018 9:55:00 AM Lab ID: 1811K19-001 Matrix: Solid Reporting Dilution Analyses Result Qual Units BatchID Date Analyzed Analyst Limit Factor HERBICIDES, TCLP SW1311/8151A 2,4,5 -TP (Silvex) BRL 0.20 2,4-D BRL 0.20 Surr: DCAA 76.6 49.4-120 Qualifiers: • value exceeds maximum contaminant level BRL Below reporting limit H Holding times for preparation or analysis exceeded N Analyte not NELAC certified B Analyte detected in the associated method blank > Greater than Result value (SW3510C) mg/L 270683 1 11/29/201812:48 UH mg/L 270683 1 11/29/201812:48 UH %REC 270683 1 11/29/201812:48 UH E Estimated (value above quantitation range) S Spike Recovery outside limits due to matrix Nan' See case narrative NC Not confirmed < Less than Result value J Estimated value detected below Reporting Limit Page 37 of 39 Page 3 of 5 U) m W ca Cl) Q Q z 0 z i U u 7 7 m is v v Q Q E E H F F- 0 o0 v v O O u U u O U G Q z z A sri O v u O ❑ ❑ Ou 0 c y U O -0 v E Y v H >_ N — - O + O O C a) V O C N C. 11 El C U O � Q sn d 'O C F � El n E (6 N -O > o 'v ° � � r+ � � � U a N ti H i u O N u C N E ti ti N N a a Y c � UO c Y a1U u cu L o Q N W IQ) � ® a o ❑ O 3 O y N U =p m M1in v T � r• N � � C b v C ro E o v U Q v • O OCCCO •• vs ^' U Ou rv• O U 2 c c c 6 Ou R Q M v c v v 0 • v •0 •• E C a) t CC O Q Ou r C p C. Oco N Y C E O > ciw(" j O L 7 Q C V al V � 0 _O aJ pQ u �u 3 Y Q E E v sti c f6 � a, L r. C O H a1 M N E :+ = sn O a � N c >C "O c o i p c aJ N C v v M1. _0O C �• c p v 6 n Op 'u LV F6 O u ou OV Cp ON C• O L 'O c Q Y Q C m O c v >to a v £ �• a t •a n. c N v� 3 $ a' L Q C E CL a E Q) p C o v r ^ - i °A Q v v ba> '� '� u O T O > 0 o a =o w Y 0 N > >_ a aci v -w v v m c p v Q w c v w r E w i v Q c N O O O E '6 r.N OV y a, w p cL O E O 7 7 E ro vs Y C -O -O W O O aJO f0 19 E CL a o o Q E O vp o E c m c m a m y F vti U u H U a0+ U U I v U u 7 7 m is v v Q Q E E H F F- 0 o0 v v O O u U u O U G Q z z 0) cqti N c c�c LOG G O 0) m N VI 10 N fa C C a! �C Y E Y to O m 'O U p N 2 M IL l0 00 N � N y OC O cz u � u v �v ate+ a0+ a -OC C: V ca (p V U� s �m y N E N M 0 Y O V M V — sn U m ai a/ Q U 4) Q E (Z O Q 7 O C a Q N z • • • > O m o O z 300 m s v > -o Y Q U m Q ■ 7 � E v 3 N V � O C C O U 2 9 a) Q N O O N i+ Q ti � E N w C O Q p_ ar M1' Echtw Q 0 E r U - O Q w C 6 N .O a N U C a) c E N CO (D v v h % fluo cz 0 ccz oYU) N N V Ol 1p E N v Np t L Zu H U V r a) L6 r --Z oo ai o r4 ry mi v ui is ri oo WENe 38 of 395 a -I c -I c -I c -I N N N N N N N N N u O ❑ ❑ Ou c y C N O > O -0 v N L Y v H >_ N — - O + O O C O C 11 El C U O .0 'O C El 0 > o 'v a N ti u N u C N E ti ti N N a a c EE0 o 0 IQ) ® o O 3 O 00000 M1in v T � r• N � � C C ro � v Q i N •• vs ^' U Ou rv• O U 2 c c c 6 Ou R Q M v c v v 0 o v E C a) t CC O Q Ou r C p s C O N Y C E O > = j O L 7 Q C V al V � 0 aJ pQ p Q 3 Y Q E E v ° H a1 C = 0 N c >C i p c v v v E r c c p v v N n v 'u > > v ou OC C• Q Y Q c v v Q v E c a m E? v a m M $ a' CL a E C. > o — Hi E O c f6 T O > 0 E �p c w Y v N > >_ a cu u u H O v Q w N 'O 0 w w w 0) cqti N c c�c LOG G O 0) m N VI 10 N fa C C a! �C Y E Y to O m 'O U p N 2 M IL l0 00 N � N y OC O cz u � u v �v ate+ a0+ a -OC C: V ca (p V U� s �m y N E N M 0 Y O V M V — sn U m ai a/ Q U 4) Q E (Z O Q 7 O C a Q N z • • • > O m o O z 300 m s v > -o Y Q U m Q ■ 7 � E v 3 N V � O C C O U 2 9 a) Q N O O N i+ Q ti � E N w C O Q p_ ar M1' Echtw Q 0 E r U - O Q w C 6 N .O a N U C a) c E N CO (D v v h % fluo cz 0 ccz oYU) N N V Ol 1p E N v Np t L Zu H U V r a) L6 r --Z oo ai o r4 ry mi v ui is ri oo WENe 38 of 395 a -I c -I c -I c -I N N N N N N N N N 00 0 0 0 N � 00 In C� It It Itt � �t O\ 06 06 0 0 0 O 0 0 0 0 0 0 n n n O O O M M OD N � N a3 CIO CIO d h O — O r - M M M O O O N un N N O O O 1 00 In In � � M M M O O O 0) M 0 M N O) Co LO a-- —O 0 LO Q) 0) co CL k .o y 0 Fa >, � k � o 0 �0 n m � o o a y .y .y o x � w x a APPENDIX 4 2019 NEW PERMIT APPLICATION Atlantic OBX, Inc. Residual Source Certification Attachment Elizabeth City WTP Residuals Storage Facility Field Loading Calculations Analytical State of North Carolina DWR Department of Environment and Natural Resources Division of Water Resources DiivisIon of Water ResoUKes RESIDUALS SOURCE CERTIFICATION FORM: RSC 11-13 I. RESIDUALS SOURCE-GENERATING FACILITY INFORMATION (See Instruction B.): 1. Facility Name: Elizabeth City WTP Residuals Storage Facility 2. Facility permit holder is: 0 Federal, M State, 0 Local Government, or ❑ Private. Facility permit issued by: ■ Div. of Water Resources, Div. of Environmental Health, or j Other (explain: �. 3. Facility contact person and title: Travis Tucker Complete mailing address: P.O. Box 347 City: Elizabeth Cit] State: NC Zip: 27907- Telephone number: (252) 335-2196 E-mail address: ttucker e cityofec.com 4. Facility physical address: Wellfield Rd. City: Elizabeth Citi State: NC Zip: 907- Coordinates: Latitude: 36° 18' 13" Longitude: 76° 17'27" Datum: NAD 83 Level of accuracy: Sub-Meter Method of measurement: 5. Purpose of the facility: treatment of municipal wastewater, treatment of 100% domestic wastewater, treatment of potable water, treatment of 100% industrial wastewater, treatment of industrial wastewater mixed with domestic wastewater, (approximate percentages: = % industrial and % domestic) other (explain: SDR Storage of Residuals Generated by the City of Elizabeth City WTP ). 6. Does the facility have an approved pretreatment program: ❑ Yes ® No 7. Facility permitted/design flow: E MGD and facility average daily flow: NA MGD 8. Average amount of residuals being generated at this facility Variable (See O&M Plan) dry tons per year. 9. Specify the following regarding treatment and storage volumes available at the facility: Type and volume of residuals treatment: No Treatment Provide'l Type and volume of residuals storage (i.e., outside of residuals treatment units): Two Surface Disposal Units with 2,558.000 (Primary) & 3,508.000 (Secondary) Gallons II. RESIDUALS QUALITY INFORMATION (See Instruction C.): 1. Specify if residuals are regulated under: 0 40 CFR Part 503 or 40 CFR Part 257. Note: Only residuals that are generated during domestic/municipal wastewater treatment processes are regulated under 40 CFR Part 503, otherwise, the residuals are regulated under 40 CFR Part 257. 2. Specify if residuals are defined under 15A NCAC 02T.1102(6) as: 0 Biological ® Non -Biological FORM: RSC 11-13 Page 1 of 5 Note: Biological residuals are residuals that have been generated during the treatment of domestic wastewater, animal processing wastewater, or the biological treatment of industrial wastewater (biological treatment is a system that utilizes biological processes including lagoons, activated sludge systems, extended aeration systems, and fixed film systems). 3. Hazardous Waste Determination: Complete the following to demonstrate that the residuals are non -hazardous under RCRA: (Note - this item does not have to be completed for facilities that are less than 0.5 MGD in design flow that treat 100% non -municipal, domestic wastewater only) a. Are the residuals listed in 40 CFR §261.31-§261.33: 0 yes no. If yes, list the number(s): _ b. Specify whether or not the residuals exhibit any of the characteristics defined by 40 CFR §261.21- 261.24: M yes 0 no. Fill in the following tables with the results of the latest toxicity characteristic leaching procedure (TCLP) analysis as well as those for corrosivity, ignitability, and reactivity: Laboratory: Merit and Date of analysis: 5/9/20 Passed corrosivity test: ® yes no. pH: s.u. (2 < pH < 12.5) Passed ignitability test: ® yes no. Flashpoint: Will Not Ignite OF (> 140°F) Passed reactivity test: JUyes Ono. HCN: .500 mg/kg (<250) & H2S: <10. mg/kg (<500) TCLP Parameter Limit (Mg/1) Result (Mg/1) TCLP Parameter Limit (mg/l) Result (Mg/1) Arsenic 5.0 < 0.010 Hexachlorobenzene 0.13 < 0.100 Barium 100.0 0.024 Hexachloro-1,3-Butadiene 0.5 < 0.100 Benzene 0.5 < 0.0100 Hexachloroethane 3.0 < 0.100 Cadmium 1.0 < 0.002 Lead 5.0 < 0.010 Carbon Tetrachloride 0.5 < 0.0100 Lindane 0.4 < 0.040 Chlordane 0.03 < 0.003 Mercury 0.2 < 0.02 Chlorobenzene 100.0 < 0.0100 Methoxychlor 10.0 < 1.00 Chloroform 6.0 < 0.0100 Methyl Ethyl Ketone 200.0 < 0.100 Chromium 5.0 < 0.005 Nitrobenzene 2.0 < 0.100 m -Cresol 200.0 < 0.200 Pentachlorophenol 100.0 < 0.500 o -Cresol 200.0 < 0.100 Pyridine 5.0 < 0.100 p -Cresol 200.0 < 0.200 Selenium 1.0 < 0.010 Cresol 200.0 < 0.300 Silver 5.0 < 0.005 2,4-D 10.0 < 1.0 Tetrachloroethylene 0.7 < 0.0100 1,4 -Dichlorobenzene 7.5 < 0.100 Toxaphene 0.5 < 0.050 1,2-Dichloroethane 0.5 < 0.0100 Trichloroethylene 0.5 < 0.0100 1,1-Dichloroethylene 0.7 < 0.0100 2,4,5 -Trichlorophenol 400.0 < 0.100 2,4-Dinitrotoluene 0.13 < 0.100 2,4,6 -Trichlorophenol 2.0 < 0.100 Endrin 0.02 < 0.002 2,4,5 -TP (Silvex) 1.0 < 0.10 Heptachlor and its Hydroxide 0.008 < 0.0008 Vinyl Chloride 0.2 < 0.0200 4. Metals Determination: Complete one of the following tables (i.e., as applicable) to demonstrate that the residuals do not violate the ceiling concentrations for metals regulated under 15A NCAC 02T .1105. a. For Distribution/Land Application: Fill in the following table with the results of the latest analyses (i.e., on a dry weight basis) for the following metal parameters: Laboratory: T eritech, In -7 and Date of analysis: 5/9/2017 Parameter Ceiling Concentration Limits (ClassA & ClassB) (mg/kg) Monthly Average Concentration Limits (Class A Only) (mg/kg) Result (mg/kg) Arsenic 75 41 < 0.780 Cadmium 85 39 < 0.156 Copper 4,300 1,500 2.22 Lead 840 300 < 0.780 Mercury 57 17 < 0.016 Molybdenum 75 n/a < 0.390 Nickel 420 420 3.23 Selenium 100 100 < 0.780 Zinc 7,500 2,800 10.7 b. For Surface Disposal Unit (landrill): Fill in the following table with the results of the latest analyses (i.e., on a dry weight basis) for the following metal parameters: Laboratory: _ and Date of analysis: _ Distance from Disposal Unit to Boundary to Closest Property Line (meters, check one) Arsenic (mg/kg) Chromium (mg/kg) Nickel (mg/kg) > 0 but < 25 30 200 210 > 25 but < 50 34 220 240 > 50 but < 75 39 260 270 ❑ > 75 but < 100 46 300 320 > 100 but < 125 53 360 390 > 125 62 450 420 Result (mg/kg) 3.0 7.0 5.0 5. Nutrient/Micronutrient Determination: Complete the following: a. Total solids: a%. b. Fill in the following table with the results of the latest analyses (i.e., on a dry weight basis) for the following nutrient and micronutrient parameters: Laboratory: 14eritech, Inc. and Date of analysis: 5/9/2017 Parameter Result (mg/kg) Aluminum 13,900 Ammonia -Nitrogen < 15.6 Calcium 240,250 Magnesium 9,700 Nitrate -Nitrite Nitrogen < 15.6 pH (Standard Unit) 9.1 Phosphorus 200 Potassium 353 Sodium 293 Total Kjeldahl Nitrogen < 31.2 c. Using the results listed in Item II. 5b. above, calculate the sodium adsorption ration (SAR): - [Note: If residuals contain SAR of 10 or higher, the applicant shall obtain recommendations from the local Cooperative Extension Office, the Department of Agriculture and Consumer Services, the Natural Resource Conservation Service, a North Carolina Licensed Soil Scientist, or an agronomist, prior to land application of residuals. The recommendations shall address the sodium application rate, soil amendments (e.g., gypsum, etc.), or a mechanism for maintaining site integrity and conditions conducive to crop growth]. d. Specify the mineralization rate to be used in calculating the plant available nitro en (PAN) of the residuals: %. This rate is a (check one): N default value, or actually established. If the residuals are not generated from the treatment of municipal or domestic wastewater, ex lain or provide technical justification as to why the selected default value is appropriate to be applied to these residuals: ii e. Calculate the PAN for the residuals (i.e., on a dry weight basis) and fill the results in the following table: Application Method First (111) Year PAN Five -Year Maximum Adjusted PAN (mglkg) (mg/kg) Surface 23 23 Injection/Incorporation 31 31 6. Other Pollutants Determination: S eci whether or not there are any other pollutants of concern in the residuals and provide the results of the latest analyses: 7. Pathogen Reduction: Per 15A NCAC 02T.1106, specify how residuals will meet the pathogen reduction requirements: a. For Distribution/Land Application of Class A or Equivalent: A fecal coliform density that is demonstrated to be less than 1,000 MPN per gram of total dry solids, or A salmonella sp. density that is demonstration to be less than 3 MPN per 4 grams of total dry solids. AND one of the followings (except for non -biological residuals): 0 Alternative 1 [15A NCAC 02T. I 106(b)(3)(A)] - Time/Temperature Compliance. ❑ Alternative 2 [15A NCAC 02T.1106(b)(3)(B)] - Alkaline Treatment. ❑I Alternative 3 [15A NCAC 02T.I 106(b)(3)(C)] - Prior Testing for Enteric Virus/Viable Helminth Ova. J Alternative 4 [15A NCAC 02T.I 106(b)(3)(D)] - No Prior Testing for Enteric Virus/Viable Helminth Ova. Alternative 5 [15A NCAC 02T.1106b (3)(E) -(K)] - Process to Further Reduce Pathogens (PFRP). Specify one: E7 composting, i heat drying, ❑ heat treatment, ❑ thermophilic aerobic digestion, ❑ beta ray irradiation, ❑ gamma ray irradiation, or ❑ pasteurization. b. For Land Application of Class B: 11 Alternative 1 [15A NCAC 02T.I 106(c)(1)] - Fecal Coliform Density Demonstration. El Alternative 2 [15A NCAC 02T.I 106(c)(2 - Process to Significantly Reduce Pathogens (PSRP). Specify one: ❑ aerobic digestion, air drying, ❑ anaerobic digestion, ❑ composting, oi I lime stabilization. c. For Surface Disposal: Select One of the Class A or Equivalent Pathogen Reduction Alternatives in Item II. 7a. above. Select One of the Class B or Equivalent Pathogen Reduction Alternatives in Item II. 7b. above. ❑ Exempt -If Daily Cover Alternative is chosen in Item II.8. below [ 15A NCAC 02T.1 106(a)(2)]. ❑ Not Applicable - Non -Biological Residuals with NO Domestic Wastewater Contribution. 8. Vector Attraction Reduction (VAR): Per 15A NCAC 02T.1107, specify how residuals will meet the VAR requirements: ❑ Alternative 1 [15A NCAC 02T. 1 107(a)(1)] - 38% Volatile Solids Reduction (Aerobic/Anaerobic Digestion). ❑ Alternative 2 [15A NCAC 02T.I 107(a)(2)] - 40 -Day Bench Scale Test (Anaerobic Digestion). ❑ Alternative 3 [15A NCAC 02T.I 107(a)(3)] - 30 -Day Bench Scale Test (Aerobic Digestion). ❑ Alternative 4 [15A NCAC 02T.I 107(a)(4)] - Specific Oxygen Uptake Rate Test (Aerobic Digestion). ❑ Alternative 5 [15A NCAC 02T.I 107(a)(5)] - 14 -Day Aerobic Processes. ❑ Alternative 6 [ 15A NCAC 02T. 1107(a)(6)] - Alkaline Stabilization. Alternative 7 [15A NCAC 02T.I 107(a)(7)] - Drying of Stabilized Residuals. 0 Alternative 8 [ 15A NCAC 02T. 1107(a)(8)] - Drying of Unstabilized Residuals. ❑ Alternative 9 [15A NCAC 02T. 1 107(a)(9)] - Injection. ❑ Alternative 10 [15A NCAC 02T.1107(a)(10)] - Incorporation. Q Alternative for Surface Disposal Units Only - Soil/Other Material Cover [15A NCAC 02T.I 107(b)(2)]. Not Applicable - Non -Biological Residuals with NO Domestic Wastewater Contribution. Note: For animal processing residuals, only alternatives 9 or 10 may be chosen due to the nuisance conditions that typically occur when these residuals are applied and left on the land surface. &AGMAN FIELD LOADING ESTIMATES Facility Elizabeth City WTP Lagoon Sampling Date 5/9/2017 % Solids 64.1 Mineralization Rate 0 Wet Tons per DT 1.56 pH 9.1 Sodium Absorpotion 0.13 <5.0 Safe 5.0 - 10.0 Careful Management >15.0 Do Not Land Apply Ratio NITROGEN APPLICATION TKN (mg/Kg) 31 lbs./WT 0.04 Ammonia Nitrogen (mg/Kg) 15.60 lbs./WT 0.02 Nitrate -Nitrite (mg/Kg) 15.60 lbs./WT 0.02 PLANT AVAILABLE NITROGEN SURFACE APPLIED PAN (mg/Kg) 23 lbs./WT 0.03 PLANT AVAILABLE NITROGEN INJECTED/INCORPORATED APPLIED PAN (mg/Kg) 31 lbs./WT 0.04 Volatization Rate= 0.5 Surface Application 420 1.0 Injection/Incorporation 100 EPA METAL LIMITS 2,800 Class A Ceiling Class B Ceiling Limits (mg/Kg) Limits (mg/Kg) 41 75 39 85 1,500 4,300 300 840 17 57 420 420 100 100 2,800 7,500 1 st Year 2nd Year 3rd Year 4th Year 5th Year NUTRIENT APPLICATION K20lbs./WT 0.54 P2051bs./WT 0.59 Calcium lbs./WT 308.00 Magnesium lbs./WT 12.44 Manganese lbs./WT 2.22 Sulfur lbs./WT 0.00 Molybdenum lbs./WT 0.00 HEAVY METAL CONCENTRATION HEAVY METAL LOADING Arsenic (mg/Kg) 0.78 Arsenic lbs./WT 0.00 Cadmium (mg/Kg) 0.16 Cadmium lbs./WT 0.00 Copper (mg/Kg) 2.22 Copper lbs./WT 0.00 Lead (mg/Kg) 0.78 Lead lbs./WT 0.00 Mercury (mg/Kg) 0.02 Mercury lbs./WT 0.00 Nickel (mg/Kg) 3.23 Nickel lbs./WT 0.00 Selenium (mg/Kg) 0.78 Selenium lbs./WT 0.00 Zinc (mg/Kg) 3.23 Zinc lbs./WT 0.00 RESIDUAL NITROGEN CALCULATION 8 0 0.00 Total 23 0.05 Total 31 0.06 Equations 1 st Yr. PAN (mg/Ig)=(MR x (TKN-NH3))+(VR x NH3)+NOx 2nd Yr PAN (mg/Kg)= 2nd Yr. TKN x (MR/2) 3rd Yr PAN (mg/Kg)= 3rd Yr. TKN x (MR/4) 4th Yr PAN (mg/Kg)= 4th Yr. TKN x (MR/8) 5th Yr PAN (mg/Kg)= 5th Yr. TKN x (MR/16) Surface Application Injection/Incorporation Application Remaining Remaining Organic Organic PAN PAN Nitrogen PAN PAN Nitrogen TKN (mg/kg) (lbs/DT) (mg/Kg) TKN (mg/kg) (lbs/DT) (mg/Kg) 31 23 0.05 8 31 31 0.06 0 8 0 0.00 8 0 0 0.00 0 8 0 0.00 8 0 0 0.00 0 8 0 0.00 8 0 0 0.00 0 8 0 0.00 8 0 0 0.00 0 Total 23 0.05 Total 31 0.06 Equations 1 st Yr. PAN (mg/Ig)=(MR x (TKN-NH3))+(VR x NH3)+NOx 2nd Yr PAN (mg/Kg)= 2nd Yr. TKN x (MR/2) 3rd Yr PAN (mg/Kg)= 3rd Yr. TKN x (MR/4) 4th Yr PAN (mg/Kg)= 4th Yr. TKN x (MR/8) 5th Yr PAN (mg/Kg)= 5th Yr. TKN x (MR/16) Contact: C. Scott Carpenter Client: Soil Plus P.O. Box 1396 Oxford, NC 27565 Meritech, Inc. Environmental Laboratory Laboratory Certification No. 165 Page 1 Report Date: 5/31/2017 Pr0)eCt: Elizabeth City 4VTP Lagoon Date Sample Rcvd: 5/9/2017 Meritech Work Order # 050917131 Sample: Lagoon Grab 5/8/2017 1311 - TCLP Metals Parameter Results Analysis Date Det. Limit Ree. Limit Method Arsenic <0.010 mg/L 5/18/2017 0.010 5.0 EPA 2003 Barium 0.024 mg/L 5/18/2017 0.005 100.0 EPA 2003 Cadmium <0.002 mg/L 5/18/2017 0.002 1.0 EPA 2003 Chromium <0.005 mg/L 5/18/2017 0.005 5.0 EPA 2003 Lead <0.010 mg/L 5/18/2017 0.010 5.0 EPA 200.7 Mercury <0.02 mg/L 5/16/2017 0.02 0.2 EPA 245.1 Selenium <0.010 mg/L 5/18/2017 0.010 1.0 EPA 200.7 Silver <0.005 mg/L 5/18/2017 0.005 5.0 EPA 200.7 TCLP Organics Parameter Results Analysis Date Reporting Limit Method Volatiles 8260 Attached 5/15/2017 8260 Semi Vol. 8270 Attached 5/30/2017 8270 Other Tests Parameter Results Analysis Date Reporting Limit Method % Total Solids 64.1 % 5/10/2017 0-100 % SM 2540B Cyanide, total <0.500 mg/kg 5/17/2017 0.500 mg/kg EPA 335.4 Sulfide <10.0 mg/kg 5/12/2017 10.0 mg/kg SW 846 9038 Ignitability Will Not Ignite 5/10/2017 EPA 1030 Corrositivity (pH) 9.1 S.U. 5/10/2017 1.0 - 14.0 S.U. SM 4500 HB 642 Tamco Road, Reidsville, North Carolina 27320 tel.(336)342-4748 fax.(336)342-1522 Contact: C. Scott Carpenter Client: Soil Plus P.O. Box 1396 Oxford, NC 27565 Meritech, Inc. Environmental Laboratory Laboratory Certification No. 165 Meritech Work Order # 050917131 Sample: Lagoon Grab Page 2 Report Date: 5/31/2017 PPOJ2CY: Elizabeth City WTP Lagoon Date Sample Rcvd: 5/9/2017 5/8/2017 13 11 ULP Pesticides &Herbicides Pesticide - SW -846 8O81A Parameter Results Analysis Date Det. Limil Ree. Limit Dilution Factor Endrin <0.002 mg/L 5/18-25/17 0.002 0.02 1 Chlordane <0.003 mg/L 5/18-25/17 0.003 0.03 1 Toxaphene <0.050 mg/L 5/18-25/17 0.050 0.5 1 Methoxychlor <1.00 mg/L 5/18-25/17 1.00 10.0 1 Heptachlor <0.0008 mg/L 5/18-25/17 0.0008 0.008 1 Lindane <0.040 mg/L 5/18-25/17 0.040 0.4 1 Herbicides - SW -846 8151A Parameter Results Analysis Date Det. Limit Ree. Limit Dilution Factor 642 Tamco Road, Reidsville, North Carolina 27320 tel.(336)342-4748 fax.(336)342-1522 <1.05/18-25/17 1.0 10.0 1 2,4,5 -TP (Silvex) <0.10 mg/L 5/18-25/17 0.10 1.0 1 642 Tamco Road, Reidsville, North Carolina 27320 tel.(336)342-4748 fax.(336)342-1522 COil tact: C. Scott Carpenter Client: Soil Plus P.O. Box 1396 Oxford, NC 27565 Meritech, Inc. Environmental Laboratory Laboratory Certification No. 165 Page 3 Report Date: 5/31/2017 PCO]eCt: Elizabeth City WTP Lagoon Date Sample Rcvd: 5/9/2017 Meritech Worlc Order # 050917131 Sample: Lagoon Grab 5/8/2017 Parameters Results <15.6 Analysis Date Reporting Limit Method %Total Solids 64.1 % 5/10/17 0-100 % SM 2540B Ammonia, Nitrogen <15.6 mg/kg 5/11/17 15.6 mg/kg EPA 350.1 TKN <31.2 mg/kg 5/16/17 31.2 mg/kg EPA 351.1 Nitrate/Nitrite, Nitrogen <15.6 mg/kg 5/11/17 15.6 mg/kg EPA 353.2 Aluminum, total 13,900 mg/Icg 5/23/17 2.50 mg/kg EPA 200.7 Arsenic, total <0.780 mg/kg 5/16/17 0.780 mg/kg EPA 200.7 Cadmium, total <0.156 mg/kg 5/16/17 0.156 mg/kg EPA 2003 Calcium, total 240,250 mg/kg 5/23/17 10.0 mg/kg EPA 200.7 Copper, total 2.22 mg/kg 5/16/17 1.00 mg/kg EPA 2003 Lead, total <0.780 mg/kg 5/16/17 0.780 mg/kg EPA 2003 Magnesium, total 9,700 mg/kg 5/23/17 10.0 mg/kg EPA 200.7 Mercury, total <0.016 mg/17g 5/16/17 0.016 mg/kg EPA 245.1 Molybdenum, total <0.390 mg/kg 5/16/17 0.390 mg/14:9 EPA 2003 Nickel, total 3.23 mg/kg 5/16/17 2.0 mg/kg EPA 2003 Phosphorus, total 200 mg/kg 5/16/17 2.00 mg/kg EPA 200.7 Potassium, total 353 mg/kg 5/16/17 20.0 mg/kg EPA 2003 Selenium, total <0.780 mg/kg 5/16/17 0.780 mg/kg EPA 2003 Sodium, total 293 mg/lcg 5/16/17 20.0 mg/kg EPA 2003 Zinc, total 10.7 mg/kg 5/16/17 0.500 mg/kg EPA 2003 pH 9.1 S.U. 5/10/17 1,0-14,0 S.U. SM 4500 -HB I hereby certify that I have reviewed and approve these data. Laboratory Representative 642 Tamco Road, Reidsville, North Carolina 27320 tel.(336)342-4748 fax.(336)342-1522 MERITECH, INC. Environmental Laboratories Laboratory Certificate #165 Client: Soil Plus Project: Elizabeth City WTP Lagoon Client Sample M: Lagoon Sample Collection: 05/08/17 Meritech Sample ID: 050917131 1311 - TCLP Oraanics Volatiles: SW -846 8260 Analysis: 05/15/17 Extracted: 05/11/17 Analyst: VWV Parameter Result Units Det. Limit Ree. Limit Dilution Factor Benzene Semi -Volatiles: SW <0.0100 Units mg/L 0.0100 5.00 10 Carbon Tetrachloride <0,0100 mg/L 0.0100 5.00 10 Chlorobenzene <0,0100 <0.100 mg/L 0.0100 100 10 Chloroform <0,0100 Hexachloro-1,3-butadiene mg/L 0.0100 6.0 10 1,2-Dichloroethane <0,0100 10 mg/L 0.0100 0.50 10 1,1-Dichloroethene <0.0100 3.00 mg/L 0.0100 0.70 10 Methyl Ethyl Ketone < 0.100 mg/L 0.100 200 10 Tetrachloroethylene <0.0100 0.200 mg/L 0.0100 0.70 10 Trichloroethene <0.0100 mg/L mg/L 0.0100 0.50 10 Vinyl Chloride <0.0200 mg/L 0.020 0.20 10 -846 8270 Analysis: 05/30/17 Extracted: 05/11/17 Analyst: PM Parameter Result Units Det. Limit Ree. Limit Dilufimr Factor 1,4 -Dichlorobenzene <0.100 mg/L 0.100 7.5 10 Hexachlorobenzene <0.100 mg/L 0.100 0.13 10 Hexachloro-1,3-butadiene <0.100 mg/L 0.100 0.5 10 Hexachloroethane <0.100 mg/L 0.100 3.00 10 o -cresol <0.100 mg/L 0.100 200 10 m&p-cresol <0.200 mg/L 0.200 200 10 Total cresols <0.300 mg/L 0.300 200 10 Nitrobenzene <0.100 mg/L 0.100 2.00 10 Pentachlorophenol <0.500 mg/L 0.500 100 10 Pyridine <0.100 mg/L 0.100 5.0 10 2,4,5 -Trichlorophenol <0.100 mg/L 0.100 400 10 2,4,6 -Trichlorophenol <0.100 mg/L 0.100 2.00 10 2,4-Dinitrotoluene <0.100 mg/l. 0.100 0.13 10 Ilrereby certify t/rat I have reviewed and approve these rinta. Laboratory Representative 642 Tamco Road *Reidsville, NC 27320 (336) 342-4748 Ph * (336) 342-1522 Fax C =i ' Y Y p d o C 0 O - a N _ - E z a £ E. 'O \ g p 00 Q Co F bD F N . 00 a c J O> U m N N O m U c III y r .c F R t� LO co N =m LO o x E L N Y N Q N O N W U n O x 00 W v "� 'm °' x L �� O N - PC f m E O Q H E Z= LL w a a Z o r, cr v C x_ Z a CO N O C p E 0 O VL O o Y N L E Z v N [mE T m N Z i� O Y Z CO N c0 m o ~ Q J6 a E M U a z a \p a z a N m c U) a a X U o Y O -EL v v p ca6 m0 N E 7 3: E ti z z v n`Ni Oc 3= 0 am O E '= IT :ae # U Z T N O u ~ F C f V m U Q a i=r r F E � N F a a C > c @ .p a E w u' N V Ln d. MIMEDN �"� f•' m m \J r. cc N ti 0O O N N O O O O cp 0 C O Z H m u O EN E o. 4001 pI,,dPPI,o U m ^' m s N G v E N o a V E W z N o .� aU p W ° w o a nom. �* EUAl W GJ� a a U @ EE c U = s C O Z i O w u O o > 3 O U m E a v s a a a w m O ", ', N •— Ln k APPENDIX 5 2019 NEW PERMIT APPLICATION Atlantic OBX, Inc. O&M Plan ATLANTIC OBX, INC. OPERATION AND MAINTENANCE PLAN DISTRIBUTION AND MARKETING OF CLASS A RESIDUAL BIOSIOLIDS Created October 2018 1.0 SUMMARY Atlantic OBX, Inc. (Atlantic) is a privately -owned company that is contracted to haul and land apply nutrient enriched by-products such as Biosolids from Wastewater Treatment Plants, Residuals from Water Treatment Plants, Domestic Septage, Portable Toilet Waste, and Grease Trap Pumpings. Atlantic is unique in that it does not participate in the generation or treatment of the by-products generated by any of the source types listed above. At times Atlantic is requested to provide lime stabilization of Biosolids by smaller operating facilities, but this quantity is normally very small. Atlantic's main role is to provide transportation and operational equipment to spread the nutrient enriched by-products listed above. Many of these Class A Sources have an independent operation schedule that they adhere to. This Operation and Maintenance Plan (O&M) addresses how Atlantic is able to manage by-products produced by multiple, independent generators and distributes the residuals under their own land application permit. Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals Analytical Requirements Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan 2.0 ANALYTICAL REQUIREMENTS Prior to the hauling and land application event being schedule the generator must provide analytical results documenting that all parameters listed in Condition IV. 2 — 4 and at the frequency listed in most recent copy of this permit. If Atlantic does not collect the sample then it does not own the responsibility of the integrity of the sample and the method it was collected, transported, submitted, and analyzed. Should the generating source elect to have Atlantic collect the sample prior to land application, then it will be done in the following manner: Four factors that may ultimately affect the integrity of reported data include: 1) obtaining a representative sample, 2) preventing contamination of the sample, 3) providing legal documentation of the sampling event, and 4) protecting the sample from chemical, physical or biological change prior to analysis. A sample will be collected according to the schedule provided in the most recent copy of the Attachment of this permit and prior to land application one composite sample should be pulled from a designated location from the generating source. Atlantic has identified Meritech, Inc. out of Reidsville, NC to be used as the Certified Laboratory. The composite sample should be analyzed for: • % Solids, • Nitrogen Series (TKN, Ammonia, Nitrate, Nitrite, and Organic Nitrogen), • Phosphorus, • Potassium, • Sulfur, • Calcium, • Magnesium, • Sodium, • Iron, • Aluminum, • Manganese, • Copper, • Zinc, • and Remaining 503 Metals (i.e. Arsenic, Cadmium, Chromium, Mercury, Molybdenum, Lead, Nickel, Selenium) Approximately 2 quarts of residual should be collected. The sample containers should be clean and sterile. They should also be labeled so that they are easily identifiable in the lab. The samples should be pulled using the method listed below: Collect one sample from each digester/ storage tank/lagoon from which the material will be land applied using a "swing sampler" o The swing sampler must be used with a sterile, plastic 960 ml container Combine each sample in a stainless-steel bucket Mix thoroughly using a fiberglass rod •:' Collect each sample from the top of the access point at each digester/ storage tank/lagoon. Created October 2018 CAtlantic OBX, Inc. Operation and Maintenance Plan Once the sample is pulled, it should be placed in medium size cooler packed with ice. The sample should be collected with an enough time so that it can be delivered to the laboratory. Once per calendar year a sample should be collected and submitted to Meritech, Inc in Reidsville, North Carolina. This sample should be analyzed for: • Full TCLP • Ignitability, Corrosivity, and Reactivity • Requires 4 Quarts (In Opac Glass Bottles) A third should be submitted (If Required) to Meritech, Inc. for a 30 -Day Scale Bench test and Fecal Coliform Density Test. The 30 -Day Scale Bench Test also requires 1 quart of "clear" water from the Clarifier for Dilution if necessary. This sample would be analyzed for: • 30 -Day Scale Bench Test (4 Quarts of Residuals and 1 Quart of Clarifier water) • Fecal Coliform Density Test The contact information for the lab is: Mailing Address Meritech, Inc. 642 Tamco Rd Reidsville, NC 27320 (336) 342-4748 (Phone) Sampling frequency will be conducted in accordance with the Table listed in the most recent Attachment A of this permit. The sample will be collected by a representative of Soil Plus, LLC. For further information please contact: Drew Matthews P.O. Box 1396 Oxford, NC 27565 252-883-9301 Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals Citi of Elizabeth City Water Treatment Plant Sampling Plan Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan SAMPLING PLAN ELIZABETH CITY WTP Using a clean and appropriate sampling device (i.e. swing sampler) collect the residuals from the 200,000 gallon holding tank place them into a stainless steel container for blending with all samples. Once a representative sample has been collected put enough of the residuals in (2) quart containers (wide mouth bottles, collapsible bottles, etc.) for nutrient, pH, 503 metals, CCE, and sieve analysis as shown on the two Chain of Custody forms. The frequency of collection of the fore mentioned material should be based upon the volume produced and identified in the permit issued by the Division of Water Quality. Collected enough residuals to fill (4) glass quart containers for a Full TCLP (Should only collect 1 per year; shown on permit). Place all samples and Chain of Custodies in a cooler and fill with ice. Overnight the cooler to Meritech Laboratories in Reidsville, NC for analysis. Ensure the cooler arrives no later than 10:30 am the next day. It is best to chill the samples prior to shipping to ensure the least amount of water is produced from the ice in the cooler. For best results collect the samples in the morning, place in a cooler with ice or refrigerator, and ship as late as possible the same day. Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals City of Elizabeth City Water Treatment Residual Storage F�acilit Sampling Plan Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan SAMPLING PLAN ELIZABETH CITY WTP LAGOON Using a clean shovel or auger collect a representative sample from the area(s) (1 — 3 feet bgs) in which are scheduled to be land applied. Upon collection of the residuals from each location, place them into a stainless steel container for blending with all samples. Once a representative sample has been collected put enough residuals to fill (2) quart containers (baggies, wide mouth bottles, collapsible bottles, etc.) for nutrient, pH, 503 metals, CCE, and sieve analysis as shown on the two Chain of Custody forms. The frequency of collection of the fore mentioned material should be based upon the volume produced and identified in the permit issued by the Division of Water Quality. Collected enough residuals to fill (4) glass quart containers for a Full TCLP (Should only collect 1 per year; shown on permit). Place all samples and Chain of Custodies in a cooler and fill with ice. Overnight the cooler to Meritech Laboratory in Reidsville, NC for analysis. Ensure the cooler arrives no later than 10:30 am the next day. It is best to chill the samples prior to shipping to ensure the least amount of water is produced from the ice in the cooler. For best results collect the samples in the morning, place in a cooler with ice or refrigerator, and ship as late as possible the same day. Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals Transportation, Applies, Prevention, & Corrective Action Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan 3.0 BIOSOLIDS REMOVAL, TRANSPORT, AND APPLICATION Biosolids will be transported from the generators to suitable, permitted land application sites. Transport equipment will be inspected, licensed and appropriately marked, as required, for the purpose of transporting biosolids. Biosolids will be delivered to the application sites between sunrise to sunset. Liquid, cake and heat dried biosolids will be applied uniformly across the application area. To ensure adequate control of the application rate for each site, the equipment used for spreading the sludge will be calibrated by measuring the amount handled on a known square footage. While the rate of discharge from the application vehicle is fixed, the speed of the equipment can be adjusted to maintain the flow rate needed to achieve specific application rates. Spreading operations will be discontinued during periods of inclement weather and will not be resumed until sufficient drying of the fields has occurred. This allows equipment access without causing excessive soil compaction or rutting. To prevent adherence of the biosolids, transport vehicles will be equipped with rear mud flaps, thereby preventing biosolids from being tracked onto roadways. Biosolids adhering to the mud flap will be scraped off in the field before the truck returns to the roadway. Examples of our application tracking and summary form/reports can be provided upon request. 4.0 SITE OPERATION Biosolids will be surface applied at the properly -calculated agronomic rate and in strict accordance with any state and federal regulations for the land application of the biosolids. Buffer zone distances will be observed in accordance with applicable state and federal regulations. Buffer zones will be flagged and no biosolids will be applied within those areas. The most restrictive buffer will apply in combined situations. Operational provisions will be taken to prevent soil loss through erosion. Provisions will include contour application and avoidance of areas where surface drainage patterns result in concentrated flow of runoff from rainfall. In accordance with sound, industry standard agronomic practice, areas which are unseasonably wet (and would produce rutting or damage to the field) will not be utilized for biosolids application operations during those periods. Operations will be discontinued when soils are saturated and will not be resumed until the field has sufficient dried. The amount of biosolids applied will not exceed the hydraulic capacity of the soil at the time of each application. If a subsequent pass across a field is necessary to achieve the desired application rate, sufficient drying time will be allowed between passes. 5.0 TRANSPORTATION SYSTEM ROUTING Transportation routes will follow primary highways and avoid residential areas where possible. Designated routes are followed unless a detour is specified. In the event of a detour route, it shall be taken as specified by the detour authority. There shall be no unscheduled stops when loaded. Transportation vehicles will be inspected, licensed and appropriately marked as required with identification numbers for the purpose of this contract. All units will be equipped with spill guards and full mud flaps. This will prevent the biosolids from adhering to the tires and undercarriage of the transport vehicle, thereby preventing biosolids from being tracked onto roadways. Biosolids adhering to the mud flap will be scraped off in the field before the truck returns to the roadway. All federal OSHA and DOT laws and regulations are complied with for the protection of our clients, the community and our drivers. Examples of vehicle and driver transportation logs and inspection forms can be provided upon request. 6.0 DEWATERED & HEAT DRIED BIOSOLIDS Dewatered & Heat Dried Biosolids will be transported in standard end dump trailers with a capacity of 22 wet tons. The tankers will be loaded per the generator's specifications and standard protocols. The aluminum dump trailers used for transportation of dewatered cake and heat dried biosolids will be equipped with sealed tailgates and will be completely sealed to prevent leakage. All trucks will be fully covered and will be fitted with positive lock tailgates. Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan 7.0 LIQUID BIOSOLIDS Liquid biosolids will be transported using 6,500 gallon capacity liquid tankers, pulled by standard road tractors, for liquid biosolids transportation. The tankers will be loaded per the generator's specifications and standard protocols. The tractor/tanker unit will transport its load to a designated staging area inside the buffered area of a permitted land application site. 8.0 APPLICATION (SPREADING) — DEWATERED BIOSOLIDS At the staging area each load will be unloaded in a designated area within the land application site. Biosolids will be loaded into our Side Slinger cake box or a standard fertilizer spreader using a front-end loader. These units are capable of delivering an accurate, calibrated application of dewatered and heat dried biosolids over the application site. The uniform spread pattern ensures that biosolids are applied at proper agronomic (nutrient) and hydraulic loading rates. The application rates for each site, and its corresponding crop, will be determined based on the Plant Available Nitrogen (PAN) content of the biosolids, or other limiting factors. Typical applications will deliver between 75 and 100 percent of a crop's annual PAN requirement. 9.0 APPLICATION (SPREADING) — LIQUID BIOSOLIDS At the staging area each load will be transferred into a 4,000 gallon capacity pull behind subsequent land application. This unit is capable of delivering an accurate, calibrated application of liquid biosolids over the application site. The uniform spread pattern ensures that biosolids are applied at proper agronomic (nutrient) and hydraulic loading rates. The application rates for each site, and its corresponding crop, will be determined based on the Plant Available Nitrogen (PAN) content of the biosolids, or other limiting factors. Typical applications will deliver between 75 and 100 percent of a crop's annual PAN requirement. 10.0 SPILL AND EMERGENCY RESPONSE PROGRAM In the unlikely event of a spill, the following actions will occur immediately. • Halt Source of Spill. Use of any leaking or damaged unit which is causing the spill will cease immediately. The unit will be repaired before resuming its use. • Contain Spill. In the event large quantities of biosolids have been spilled, straw bales will be used where available and as necessary to either form a barrier or absorb biosolids. • Clean -Up. Depending on the type and amount of biosolids spilled, a variety of equipment may be used to remove the biosolids: front-end loader, shovels and brooms and vacuum equipment of a liquid biosolids applicator. Any biosolids removed from the spill site will be spread on an approved application site, returned to the WWTP, or disposed of in an approved landfill. • Final Clean -Up. Flush roadways with water or sweep as necessary to clean. Allow to dry and incorporate if spill occurs on non -paved and tillable area. In the event a spill occurs on private property, final clean-up should be completed immediately to the satisfaction of the owner. • Management of Clean -Up Efforts. The Operations Manager will take immediate charge and initiate clean-up activities. Atlantic labor will be used, with additional labor secured as needed. The Operations Manager will also communicate with the public on the scene, answering questions and advising of clean-up activities. • Reporting. All spills will be reported immediately to Atlantic offices and the client. State and local agencies will be notified in accordance with their notification requirements. Within 24 hours of the spill, the Operations Manager will send Atlantic office a written report detailing how the spill occurred and remedial action taken. This report will be provided using the enclosed Spill Report form. • Spill Prevention. The Operations Manager will implement the following spill prevention measures: o Ensure truck drivers watch trailer while loading and do not overload; Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan o Ensure trailer hatches are closed and latched while transporting; o Ensure trailer seals are inspected on a daily basis and replaced as necessary; and o Ensure unloading operations in the field are conducted to minimize any potential runoff or tracking. 11.0 PREVENTION The goal of a compliance assurance system is to prevent compliance issues from occurring. Prevention involves: • Ensuring personnel understand their role in assuring compliance; • Identifying compliance requirements at the federal, state and local levels; • Implementing a system where compliance tasks are scheduled, assigned and tracked to completion; • Developing standard operating procedures where appropriate; and • Reviewing the compliance task list and standard operating procedures on an ongoing basis and modifying them as appropriate to account for changes in regulations/requirements and operating methods, and to address compliance deficiencies. 12.0 ASSESMENT To help ensure compliance requirements are being met and the compliance assurance system is implemented and working, periodic, consistent, objective and documented assessments of a project/facility's compliance status are conducted. Atlantic personnel have clearly-defined compliance assessment responsibilities and time to conduct such assessments. Atlantic conducts informal site inspections and formal audits on an ongoing basis. 13.0 CORRECTIVE ACTION Once compliance issues have been identified during the course of day to day business and through internal audits and inspections a system must be in place which ensures that appropriate and timely corrective action is taken, the cause of the compliance issue is identified and actions are taken to prevent recurrence of the issue. Atlantic's goal is to have no instances of non-compliance. However, issues and incidents may occur and when this happens employees work to correct the incident in a timely and thorough manner. When compliance issues are identified, the situation is examined to determine the root cause of the problem and the corrective and preventive action that must be taken. The preventive action must address the root cause with the goal of preventing a recurrence. Depending on the nature of the compliance issue, it is assigned to one or more responsible parties to ensure that the corrective and preventive actions are implemented. A deadline for completion of the task is assigned and the issue is tracked to completion by regional and corporate compliance personnel. Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals Citi of Elizabeth Cites Process Diagram/Narrative, Volume justification, Storage Information & Vicinity Map Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan City of Elizabeth City Water Treatment Facility PWSID 04-70-010 Treatment Process The City of Elizabeth City uses groundwater drawn from the Upper Yorktown aquifer. Currently the city has 10 wells located on 400 acres of land located in Pasquotank County. These wells range in depth from 87 to 140 feet deep. Production from these wells range from 50 to 450 gallons per minute. Water is pumped from the wells to a central reservoir at the well field complex; from there the water is transported via pipelines to a 3 MG reservoir at the treatment facility. The current treatment process is conventional lime softening. Water is drawn from the raw reservoir to the head of the treatment facility where it is aerated to strip out carbon dioxide. As the water travels to the upflow clarifier, aluminum sulfate and an anionic polymer are added for coagulation. Hydrate Lime is then added for softening. As the lime increases the pH, hardness is precipitated out as calcium carbonate and magnesium hydroxide. Water then enters the flocculation basin where it is recarbonated to lower the pH to an acceptable level from drinking purposes. After leaving the flocculation basin, the water enters the sedimentation basins where larger suspended particles are allowed to settle out. Any remaining particles are filtered out through the use of dual media rapid sand filters. Once the water is filtered, sodium hexametaphosphate is added for corrosion control. Fluoride is also added to aid in the prevention of dental caries. A combination of chlorine and ammonia is added for disinfection and to prevent the formation of THM's. The finished product is stored in ground level clearwells with a capacity of 4 MG on the facility site. There are 3 elevated storage tanks located within the distribution system with a combined storage capacity of 2 MG. N W, U O CL H z Lu. F- LU oc w Q CrJ m 4 LO o � ra 9A U? Itv ue w Cc La. u a+ C 1J N r Y as as i17 CL _ _ 1 — 47 E r x u a+ C 1J N r RESIDUAL VOLUME JUSTIFICATION ELIZABETH CITY WATER TREATMENT PLANT Avg. Total Gallons Produced from 2016 To 2017: 3,657,500 Gallons (Includes Class A Distribution, Class B Land Application, and Residual Storage Facility) Increase in Production: 3,657,500 x 1.5 = 5,486,250 Gallons Per Year or 15,031 Gallons Per Day Percent Solids: 13.04 % Solids (2017 Average from WTP) Conversion: 8.34 lbs/gallon 2,000 lbs/ton Daily Production Rate: _ (15,031 gallons x (% Solid /100) x 8.341bs./gallon) / 2,000 lbs./ton _ (15,031 gallons x (13.04 /100) x 8.34 lbs./gallon) / 2,000 lbs./ton _ (15,031 gallons x 0.1304 x 8.34 lbs./gallon) / 2,000 lbs./ton = 16,347 lbs / 2,000 lbs./ton = 8.18 Dry Tons per Day or approx. 3,000 Dry Tons per Year EC WTP Residual Volume Justification © 2018 Soil Plus, LLC RESIDUAL STORAGE JUSTIFICATION ELIZABETH CITY WATER TREATMENT PLANT Sludge Holding Tank: 200,000 Gallons Converted Gravity Thickener to Holding Tank: 74,000 Gallons Total Sludge Holding: 200,000 + 74,000 = 274,000 Daily Production: 5,486,315 gallons (Includes Class A Distribution, Class B Land Application, and Residual Storage Facility) 5,486,315 gallons per year / 365 days per year 15,031 Gallons per Day Maximum Storage: = Volume of Storage / Daily Production Volume = 274,000 Gallons / 15,031 Gallons / Day = 18 Days EC WTP Residual Storage Justification © 2018 Soil Plus, LLC -, /i - N O Iso 1302 l \1360 1300 S 2 - - ?A 365 _ 1363 - _ 1457 1459.Q, i 1366 s iT6] - 1 60 Q / 145 e ML 1356 ' rieaaaa ,t 1361 . ? n °h. w1461 1460 0^ 456 .� Lynch3 Cro01363 ,1432 13 1417 s s Morgans Comer 32g , - - .2 1354 z y 1357 m "4 155 1359 m /� v 9`s9 1301 w=� 13580 100 � � 1353 „ GOT9 146 / y�r 1300 1357 X1352 \ 1416 1455 / / >0 56 / 465 / 1419 4 15 1450 1354 �� ' ' .p 1451 '418 1354 ' n e 1469 L i 114 114.1 1416 . \ 135 a� 48 —a 1485 1388 �+`, - 7471 1470 'A' 11472 D G R E A T /14M �� 46 5 z e it o @M 14661415 1351 \ 2 X133 %1 e 420 3 z 1464 1467 1414 1 9 - — - a 350 1402 0 t 1350 9 1469 1338 a •z D 1 S M A L \ sszo•\ 1333 1337 W 20. R1VER _ 1449 336 — wm wA EC WTP 1 \ I p S W A ELIZABETH TY M P _ -EC Lagoon,09 - - POP. 18,414 j1 ^g �1] 1469 ? �1 au - 1152 .s a ✓��'`/is� y 1303 � 1303 (- 1 471 > 115 e 0 130 1488 .1 � 303 _ ,I,t 1 144 ,? , %• 1145° • ;---- Elizgle tity, 130 J SdY unid III �yrp 116 �y .8 441140 - - L zs Pasqudtank m e �� 1223 l _-- c`,, • >m ` • (� - 1 Okisko Nle 1219 °mss m 1144 1145 1183 11831169 ^ 1139 1101 R 1250 zz I tot 1144 1.1 �l— 1253 '4fi 113 ,1476 1141 e 0 3W 15• �' I \ \ 1143 - m 126 m 11b1 0 - 113d 125 ,1227 1260 11 41 e 1142 1 1185 1134 ` xa 1243 1t169 n < .2 /T .0 -�'^ /112 1101 'yo v° s9A - 12371132 147 1244 1140 1245)\- 1 aA 1217 '1132 - 1236 119 3 1124 1101 E-1181 1125, 3 1136 1169 1182 1140 1265 1 N ._ I v 1100 1264 2 1 0 2 !67 263 — 1169 o n O / 3 Miles .�i r z Scale: 1 inch = 2 miles LOCATION MAP Figure Drawn by: SOIL PLUS Granville Farm Class A (WQ0033587) Reviewed by: CSC Elizabeth City, North Carolina Date: Sept 15 Soil Plus Project # 200705.B10 OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals Citi of Elizabeth City Water Treatment Residual Storage F�acili't Process Diagram /Narrative, Volume justification, Storage Information & Vicinity _� Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan City of Elizabeth City Water Treatment Lagoon WQ0014808 Process The City of Elizabeth City uses groundwater drawn from the Upper Yorktown aquifer. Currently the city has 10 wells located on 400 acres of land located in Pasquotank County. These wells range in depth from 87 to 140 feet deep. Production from these wells range from 50 to 450 gallons per minute. Water is pumped from the wells to a central reservoir at the well field complex; from there the water is transported via pipelines to a 3 MG reservoir at the treatment facility. The current treatment process is conventional lime softening. Water is drawn from the raw reservoir to the head of the treatment facility where it is aerated to strip out carbon dioxide. As the water travels to the upflow clarifier, aluminum sulfate and an anionic polymer are added for coagulation. Hydrate Lime is then added for softening. As the lime increases the pH, hardness is precipitated out as calcium carbonate and magnesium hydroxide. Water then enters the flocculation basin where it is recarbonated to lower the pH to an acceptable level from drinking purposes. After leaving the flocculation basin, the water enters the sedimentation basins where larger suspended particles are allowed to settle out. Any remaining particles are filtered out through the use of dual media rapid sand filters. Once the water is filtered, sodium hexametaphosphate is added for corrosion control. Fluoride is also added to aid in the prevention of dental caries. A combination of chlorine and ammonia is added for disinfection and to prevent the formation of THM's. The finished product is stored in ground level clearwells with a capacity of 4 MG on the facility site. There are 3 elevated storage tanks located within the distribution system with a combined storage capacity of 2 MG. Once the water residuals have been processed at the City of Elizabeth City Water Treatment Plant they are either land applied on agricultural fields or taken to a surface disposal unit (lagoon). The residuals taken to the lagoon are loaded into a liquid tanker and transported on public roads to the lagoon using diesel trucks. The residuals are removed from the tanker trucks into one of the two primary lagoons. Once the residuals enter one of the two primary lagoons the saturated water (approximately 17% solids and 83% water) is removed from the solids by gravity and exits the bottom of the lagoon into the surficial aquifer (unconfined). The water -residual relationship remains at field capacity (approximately 50% solids and 50% water) until it is loaded into a dump trailer using a back hoe. Once the residuals are loaded into the dump trailer they are transported to an agricultural field on public roads using diesel trucks. The residuals are then removed from the dump trailer and loaded into a rear discharging slinger. The residuals are then land applied at agronomic rates. 5 G°1 W ^j W m U E ku it.tto Ui �yLL_ _ m y U U t" Li it +h Ul - .. TIE �p pp,iJTJ rY � 2 u�i U nt a�,_•{�I•a-�F-� �x ll Y' GA[.Ca u '` t� Jam. -_. r, y.� f - J_ �F� + A• , r�P .. I _.x 7i? A510 .�.^wry o `.Yl til, a,1 'ht rf��[•-1=,.ti- A -h: °' r� n . "" � � � � i! �. m ;- ':t 4,.C1Lni IK r 01 1 (Z) Rio lu t• t � �`�° r` �n jyl 4 m Lu � U � 4 � SU I inf'4% - IL ` s ►� � �-`cJ��:�[jlri�s co z V) z 0 0 M a Q :.7= RESIDUAL VOLUME JUSTIFICATION ELIZABETH CITY WTP LAGOON Total Gallons in Avg. 2016 to 2017 by WTP: Daily Increased Production Rate at WTP: Daily Production Per Business Week: Required Period Hauling to Lagoon Lagoon from WTP: Hauling Period directly from WTP to Agricultural Fields: Conservative Non - Land Application Period: Total # of Days Hauling from WTP To Lagoon: Total # of Gallons Hauled to Lagoon: Conversion: 3,657,500 Gallons 3,657,500 Gallons x 1.5 = 5,486,250/365 =15,031 Gallons Per Day (Per WTP Residual Volume Justification) 105,217 gallons divided by 5 days per business week 21,044 gallons per business day June 15`x' to September 15'x' (65 Business Days) due to agricultural crops are in fields September 15' to June 15' (195 Business Days) 40% of days can not haul from WTP to Agricultural Fields (i.e. wet fields, broken equipment, logistical problems, etc.) 65 Business Days + (40% x 195 Business Days) 143 Business Days Total # of Business Days x 21,044 Gallons Per Day 3,009,292 Gallons @ 13.04 % Solids (Per 2017 Average) 8.34 lbs/gallon 2,000 lbs/ton Daily Production Rate: _ (21,044 gallons x (% Solid /100) x 8.341bs./gallon) / 2,000 lbs./ton _ (21,044 gallons x (13.04 /100) x 8.34 lbs./gallon) / 2,000 lbs./ton _ (21,044 gallons x 0.1304 x 8.34 lbs./gallon) / 2,000 lbs./ton = 22,887 lbs / 2,000 lbs./ton = 11.45 Dry Tons per Day or 1,638 Dry Tons per Year (@ 143 days /yr.) Percent Solids: 65.8 % Solids (2017 % Solids Avg. at Lagoon) Estimated Wet Tons = 11.45 Dry Tons per Day / (% Solids/ 100) (Stored at Lagoon) = 11.45 Dry Tons per Day / (65.80 / 100) = 11.45 Dry Tons Per Day / 0.658 =17.4 Wet Tons Per Day or 2,488 Wet Tons per Year (@ 143 days/yr.) EC Lagoon Residual Volume Justification © 2018 Soil Plus, LLC Lagoon Cleanout (Approximately Once/3 years): 1,638 Dry Tons per Year Hauled to Lagoon x 3 Years = 4,914 Dry Tons stored in lagoon at time of clean out RESIDUAL STORAGE JUSTIFICATION ELIZABETH CITY WTP LAGOON Approximate Holding Lagoon # 1 Size: 250 feet x 140 feet x 10 feet = 350,000 ft' (Per Quible Survey) Approximate Holding Lagoon # 2 Size: Area 1 = 110 feet x 80 feet x 10 feet = 88,000 ft' Area 2 = 140 feet x 260 feet x 10 feet = 364,000 ft' Area 1 + Area 2 = 88,000 ft' + 364,000 ft' = 452,000 ft' (Per Quible Survey) Total Holding Capacity: Lagoon 1 + Lagoon 2 = 802,000 ft' Estimated Daily Wet Tons: 17.4 Wet Tons per Day (Per Lagoon Volume Justification) Bulk Density (Db) 78.16 lbs./ft' (Per A&L Eastern) Daily Production Volume: _ (Wet Tons per Day x 2,000) / Db _ (17.4 Wet Tons per Day x 2,000 lbs per Ton) / 78.16 lbs / ft' = 34,800 Wet lbs. per Day / 78.16 lbs / ft' = 446 ft3 per Day Maximum Storage: = Volume of Lagoons/ Daily Production Volume = 802,000 ft' / 535 ft3 / Day = 1,798 Days or 4.9 years EC Lagoon Residual Storage Justification © 2018 Soil Plus, LLC -, /i - N O Iso 1302 l \1360 1300 S 2 - - ?A 365 _ 1363 - _ 1457 1459.Q, i 1366 s iT6] - 1 60 Q / 145 e ML 1356 ' rieaaaa ,t 1361 . ? n °h. w1461 1460 0^ 456 .� Lynch3 Cro01363 ,1432 13 1417 s s Morgans Comer 32g , - - .2 1354 z y 1357 m "4 155 1359 m /� v 9`s9 1301 w=� 13580 100 � � 1353 „ GOT9 146 / y�r 1300 1357 X1352 \ 1416 1455 / / >0 56 / 465 / 1419 4 15 1450 1354 �� ' ' .p 1451 '418 1354 ' n e 1469 L i 114 114.1 1416 . \ 135 a� 48 —a 1485 1388 �+`, - 7471 1470 'A' 11472 D G R E A T /14M �� 46 5 z e it o @M 14661415 1351 \ 2 X133 %1 e 420 3 z 1464 1467 1414 1 9 - — - a 350 1402 0 t 1350 9 1469 1338 a •z D 1 S M A L \ sszo•\ 1333 1337 W 20. R1VER _ 1449 336 — wm wA EC WTP 1 \ I p S W A ELIZABETH TY M P _ -EC Lagoon,09 - - POP. 18,414 j1 ^g �1] 1469 ? �1 au - 1152 .s a ✓��'`/is� y 1303 � 1303 (- 1 471 > 115 e 0 130 1488 .1 � 303 _ ,I,t 1 144 ,? , %• 1145° • ;---- Elizgle tity, 130 J SdY unid III �yrp 116 �y .8 441140 - - L zs Pasqudtank m e �� 1223 l _-- c`,, • >m ` • (� - 1 Okisko Nle 1219 °mss m 1144 1145 1183 11831169 ^ 1139 1101 R 1250 zz I tot 1144 1.1 �l— 1253 '4fi 113 ,1476 1141 e 0 3W 15• �' I \ \ 1143 - m 126 m 11b1 0 - 113d 125 ,1227 1260 11 41 e 1142 1 1185 1134 ` xa 1243 1t169 n < .2 /T .0 -�'^ /112 1101 'yo v° s9A - 12371132 147 1244 1140 1245)\- 1 aA 1217 '1132 - 1236 119 3 1124 1101 E-1181 1125, 3 1136 1169 1182 1140 1265 1 N ._ I v 1100 1264 2 1 0 2 !67 263 — 1169 o n O / 3 Miles .�i r z Scale: 1 inch = 2 miles LOCATION MAP Figure Drawn by: SOIL PLUS Granville Farm Class A (WQ0033587) Reviewed by: CSC Elizabeth City, North Carolina Date: Sept 15 Soil Plus Project # 200705.B10 OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals City of Elizabeth City WTP Product Label & Marketability Statement Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan ELIZABETH CITY WATER TREATMENT PLANT RESIDUAL LABEL I. CONTACT INFORMATION Name: Mr. J. Bryan Smith Mailing PO Box 2560 Address: Kitty Hawk, North Carolina 27949 Telephone #: (252) 255-2030 II. OPERATION AND MAINTENANCE REQUIREMENTS For land onto which bulk residuals are applied, the following shall apply: 1. Bulk residuals shall not be applied to the land under the following conditions: a. if the application causes prolonged nuisance conditions; b. if the land fails to assimilate the bulk residuals or the application causes the contravention of surface water or groundwater standards; c. if the land is flooded, frozen, or snow-covered or is otherwise in a condition such that runoff of the residuals would occur; d. within the 100 -year flood elevation unless the bulk residuals are injected or incorporated e. within a 24-hour period following the residuals land application event; f. during precipitation events or within 24 hours following a rainfall event of 0.5 inches or greater in a 24-hour period; g. if the slope of the land is greater than 10 percent when bulk liquid residuals are surface applied, and if the slope of the land is greater than 18 percent when bulk liquid residuals are injected or incorporated; h. if the land does not have an established vegetative cover crop unless the bulk residuals are incorporated within a 24-hour period following the residuals land application event or inj ected; i. if the vertical separation of the seasonal high water table and the depth of residuals application is less than one foot; j. if the vertical separation of the depth to bedrock and the depth of residuals application is less than one foot; or 2. Include exceptions when receive permit III. SETBACKS Applicable setbacks in accordance with 15A NCAC 02T .1108(b): Description of Setback Setback by type of application (feet) Liquid Residuals Cake Residuals Private or public water supply 100 100 Surface Waters (streams — intermittent and perennial, perennial waterbodies, and wetlands) 100 25 Surface water diversions (ephemeral streams, waterways, ditches) 25 0 Groundwater lowering ditches (where the bottom of the ditch intersects the SHWT 25 0 Wells with exception to monitoring wells 100 1 100 Bedrock outcrops 25 1 0 IV. APPLICATION RATES Application Rates should not exceed the calculated Calcium Carbonate Equivalency or the Agricultural Lime Equivalency based Lime Recommendation from the most recent Soil Nutrient Analysis for the area in which the soil sample was collected. Marketability Statement: These residuals are generated as part of the water treatment process at the Elizabeth City Water Treatment Plant in Elizabeth City, North Carolina. The treatment process uses raw ground water from the Upper Yorktown Aquifer and hydrated lime to soften the water for potable uses. The generated residuals are a by-product of the remaining solids separated from the treated water. The distributed material is classified as "Exceptional Quality" or a "Class A" product. A "Class A" product is a more stable state, contains less Fecal Coliform, and contains a smaller quantity of regulated metals (e.g. Zinc, Copper, Lead, etc.) than traditional "Class B" residuals. The residuals are also a comparable substitute for agricultural lime and are intended to be used as a supplement for agriculture lime. It is estimated that approximately 2,000 to 2,500 acres will be required to reuse the material annually for agronomic uses. There are a few applicable setbacks to some relevant site features when using these residuals. These setbacks will be listed in a copy of the issued permit and the issued label prior to distribution. OPERATION & MAINTENANCE PLAN Atlantic OBX, Inc. Distribution and Marketing of Class A Residuals City of Elizabeth City Water Treatment Residual Storage Facility Product Label & Marketability Statement Created October 2018 ©Atlantic OBX, Inc. Operation and Maintenance Plan ELIZABETH CITY WATER TREATMENT PLANT LAGOON RESIDUAL LABEL I. CONTACT INFORMATION Name: Mr. J. Bryan Smith Mailing PO Box 2560 Address: Kitty Hawk, North Carolina 27949 Telephone #: (252) 255-2030 H. OPERATION AND MAINTENANCE REQUIREMENTS For land onto which bulk residuals are applied, the following shall apply: 1. Bulk residuals shall not be applied to the land under the following conditions: a. if the application causes prolonged nuisance conditions; b. if the land fails to assimilate the bulk residuals or the application causes the contravention of surface water or groundwater standards; c. if the land is flooded, frozen, or snow-covered or is otherwise in a condition such that runoff of the residuals would occur; d. within the 100 -year flood elevation unless the bulk residuals are injected or incorporated e. within a 24-hour period following the residuals land application event; f. during precipitation events or within 24 hours following a rainfall event of 0.5 inches or greater in a 24-hour period; g. if the slope of the land is greater than 10 percent when bulk liquid residuals are surface applied, and if the slope of the land is greater than 18 percent when bulk liquid residuals are injected or incorporated; h. if the land does not have an established vegetative cover crop unless the bulk residuals are incorporated within a 24-hour period following the residuals land application event or inj ected; i. if the vertical separation of the seasonal high water table and the depth of residuals application is less than one foot; j. if the vertical separation of the depth to bedrock and the depth of residuals application is less than one foot; or 2. Include exceptions when receive permit III. SETBACKS Applicable setbacks in accordance with 15A NCAC 02T .1108(b): Description of Setback Setback by type of application (feet) Liquid Residuals Cake Residuals Private or public water supply 100 100 Surface Waters (streams — intermittent and perennial, perennial waterbodies, and wetlands) 100 25 Surface water diversions (ephemeral streams, waterways, ditches) 25 0 Groundwater lowering ditches (where the bottom of the ditch intersects the SHWT 25 0 Wells with exception to monitoring wells 100 1 100 Bedrock outcrops 25 1 0 IV. APPLICATION RATES Application Rates should not exceed the calculated Calcium Carbonate Equivalency or the Agricultural Lime Equivalency based Lime Recommendation from the most recent Soil Nutrient Analysis for the area in which the soil sample was collected. Marketability Statement: These residuals are generated as part of the water treatment process at the Elizabeth City Water Treatment Plant in Elizabeth City, North Carolina. The treatment process uses raw ground water from the Upper Yorktown Aquifer and hydrated lime to soften the water for potable uses. The generated residuals are a by-product of the remaining solids separated from the treated water. The distributed material is classified as "Exceptional Quality" or a "Class A" product. A "Class A" product is a more stable state, contains less Fecal Coliform, and contains a smaller quantity of regulated metals (e.g. Zinc, Copper, Lead, etc.) than traditional "Class B" residuals. The residuals are also a comparable substitute for agricultural lime and are intended to be used as a supplement for agriculture lime. It is estimated that approximately 2,000 to 2,500 acres will be required to reuse the material annually for agronomic uses. There are a few applicable setbacks to some relevant site features when using these residuals. These setbacks will be listed in a copy of the issued permit and the issued label prior to distribution.