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HomeMy WebLinkAboutWI0400526_DEEMED FILES_20191105~~.b. Cawinia~Department of Environmental Quality-Division of Water Resources INJECTION EVENT RECORD (I ER) NOV 05 2019 D~ Vll~t.eo o ~ Permit Number NCWC 4415-C I . Permit Information ERM Permittee Energizer Plant Facility Name 419 Art Brvan Dr, Asheboro. NC (Randolph County) Facility Address (include County) 2. Injection Contractor Information Zachary Poole I Redox Tech, LLC Injection Contractor/ Company Name Street Address ;:.2-"--00~O:..-=u=ad=e=-D=-r _____ _ NC 27513 City State Zip Code ( 919 ) 678-0140 Area code -Phone number 3. Well Information Number of wells used for injection ____ 2'--- Well IDs SVE -07 & AS-09 Were any new wells installed during this injection event? D Yes ■ No If yes, please provide the following information: Number of Monitoring Wells _____ _ Number oflnjection Wells. _______ _ Type of Well Installed (Check applicable type): D Bored D Drilled O Direct-Push D Hand-Augured O Other (specify) __ _ Please include a copy of the GW-1 form for each well installed. Were any wells abandoned during this injection event? D Yes ■ No If yes, please provide the following information: Number of Monitoring Wells _____ _ Number of Injection Wells _______ _ Please include a copy of the GW-30/or each well abandoned. 4. Injectaot Information Sodium Permanganate Injectant(s) Type (can use separate additional sheets if necessary Concentration 10% --~"-"--------- If the injectant is diluted please indicate the source dilution fluid. 40% ------'--"-'--''-------- Total Volume Injected (gal) __ _,2=·=2~00=---- Volume Injected per well (gal) 735( gal) for SVE-07 & l.465(gal) for AS-09 5. Injection History Injection date(s) ___________ _ Injection number (e.g. 3 of 5) ______ _ Is this the last injection at this site? 0 Yes D No I DO HEREBY CERTIFY THAT ALL THE INFORMATION ON THIS FORM IS CORRECT TO THE BEST OF MY KNOWLEDGE AND THAT THE INJECTION WAS PERFORMED WITHIN THE STANDARDS LAID OUT IN THE PERMIT. 10/25/19 SIGNATURE OF INJECTION CONTRACTOR DATE Submit the original of this form to the Division of Water Resources within 30 days of injection . Attn: UIC Program, 1636 Mail Service Center, Raleigh, NC 27699-1636, Phone No . 919-807-6464 Form UIC-IER Rev. 3-1-2016 Zach arv le PRINT NAME OF PERSON PERFORMING THE INJECTION Submit the original of this form to the Division of Water Resources within 30 days of injection. Attn: UIC Program, 1636 Mail Service Center, Raleigh, NC 27699-1636, Phone No. 919-807-6464 Form UIC-IER Rev. 3-1-2016 Permit Number Wl0400526 Program Category Deemed Ground Water Permit Type Injection Deemed In-situ Groundwater Remediation Well Primary Reviewer shristi.shrestha Coastal SWRule Permitted Flow Facility Facility Name Energizer Manufacturing Inc. Location Address 419 Art Bryan Dr Asheboro Owner Owner Name Energizer Manufacturing Inc Dates/Events NC Orig Issue 9/6/2019 App Received 8/26/2019 Regulated Activities Groundwater remediation Outfall Waterbody Name 27203 Draft Initiated Scheduled Issuance Public Notice Central Files: APS SWP 9/6/2019 Permit Tracking Slip Status Active Version 1.00 Project Type New Project Permit Classification Individual Permit Contact Affiliation Major/Minor Minor Region Winston-Salem Facility Contact Affiliation Scott Boyle 419 Art Bryan Dr Asheboro Owner Type Non-Government Owner Affiliation Steve Hall 419 Art Bryan Dr Asheboro County Randolph NC NC Issue 9/6/2019 Effective 9/6/2019 27203 27203308 Expiration Requested /Received Events Streamlndex Number Current Class Subbasin ERM August 20, 2019 Shristi Shrestha, Hydrogeologist NCDEQ DWR — U!C Program 1636 Mail Service Center Raleigh, NC 27699-1636 (919) 807-6464 Reference: 0498725 15720 Bnxham Hill Avenue Suite 120 Charlotte, NC 28277 Telephone: +1 704 541 8345 Fax: +1 704 624 7928 www.em.com RE.CEIVIDINCEE0,113WR AUG 6 2 2019 W otsr Qua}ay Regional Opoarions Seaton Subject: Notice of Intent to Construct or Operate Injection Wells - ISCO Pilot Test Energizer Battery Manufacturing Inc. 419 Art Bryan Drive — Plant 11 Asheboro, Randolph County, North Carolina Site ID. NCD000822957 Dear Shristi: On behalf of Energizer, ERM NC, Inc. (ERM) is submitting this Notice of Intent (NOI) to Operate injection Wells for a pilot test injection operation for the purpose of groundwater remediation at the referenced site. Site remediation activities are being conducted in accordance with a NCDEQ approved workplan detailing the activities. This NOI is to cover a pilot study injection program that is to be conducted in two phases beginning in October 2019. In the first phase, a limited injection volume will be delivered to the pifot test area to evaluate the ability of the aquifer to accept a liquid amendment and to determine if precipitants from the oxidation reaction will adversely affect the permeability of saturated aquifer near the injection area. Slug testing will be conducted before and after the preliminary limited injection and the slug test results will be used to determine if an unacceptable change in permeability of the saturated aquifer in the injection area has occurred. If the preliminary limited injection does not result in an unacceptable change in permeability, a second injection event will be conducted which delivers the volume and mass of oxidant required to treat the contaminant mass present in the design pilot test treatment area. The pilot study will include 4 groundwater monitoring events of the treatment area including a baseline, 1 month, 3 month, and 6 month event. If you have any questions regarding this project please contact me at (704) 541-8345. Sincerefy, 112-k-L Alan Martin, P.G. Project Manager Enclosures cc: Scott Boyle. Energizer Torn Wilson, ERM ERM ERM 15720 Brixham Hill Avenue Suite 120 Charlotte, NC 28277 Telephone: +1 704 541 8345 Fax: +1 704 624 7928 www.erm.com August 20, 2019 Shristi Shrestha, Hydrogeologist NCDEQ DWR – UIC Program 1636 Mail Service Center Raleigh, NC 27699-1636 (919) 807-6464 Reference: 0498725 Subject: Notice of Intent to Construct or Operate Injection Wells - ISCO Pilot Test Energizer Battery Manufacturing Inc. 419 Art Bryan Drive – Plant II Asheboro, Randolph County, North Carolina Site ID: NCD000822957 Dear Shristi: On behalf of Energizer, ERM NC, Inc. (ERM) is submitting this Notice of Intent (NOI) to Operate Injection Wells for a pilot test injection operation for the purpose of groundwater remediation at the referenced site. Site remediation activities are being conducted in accordance with a NCDEQ approved workplan detailing the activities. This NOI is to cover a pilot study injection program that is to be conducted in two phases beginning in October 2019. In the first phase, a limited injection volume will be delivered to the pilot test area to evaluate the ability of the aquifer to accept a liquid amendment and to determine if precipitants from the oxidation reaction will adversely affect the permeability of saturated aquifer near the injection area. Slug testing will be conducted before and after the preliminary limited injection and the slug test results will be used to determine if an unacceptable change in permeability of the saturated aquifer in the injection area has occurred. If the preliminary limited injection does not result in an unacceptable change in permeability, a second injection event will be conducted which delivers the volume and mass of oxidant required to treat the contaminant mass present in the design pilot test treatment area. The pilot study will include 4 groundwater monitoring events of the treatment area including a baseline, 1 month, 3 month, and 6 month event. If you have any questions regarding this project please contact me at (704) 541-8345. Sincerely, Alan Martin, P.G. Project Manager Enclosures cc: Scott Boyle, Energizer Tom Wilson, ERM ERM Deemed Permitted GW Remediation NOI Rev. 3-21-2018 Page 1 North Carolina Department of Environmental Quality – Division of Water Resources Print Clearly or Type Information. Illegible Submittals Will Be Returned As Incomplete. DATE: August 16 , 2019____ PERMIT NO. (to be filled in by DWR) A. WELL TYPE TO BE CONSTRUCTED OR OPERATED (1)Air Injection Well……………………………..…Complete sections B through F, K, N (2)Aquifer Test Well……………………….………..Complete sections B through F, K, N (3)Passive Injection System…………………..……..Complete sections B through F, H-N (4)Small-Scale Injection Operation………………….Complete sections B through N (5) X Pilot Test………………………………………….Complete sections B through N (6)Tracer Injection Well………………………….….Complete sections B through N B.STATUS OF WELL OWNER: Business/Organization C.WELL OWNER(S) – State name of Business/Agency, and Name and Title of person delegated authority to sign on behalf of the business or agency: Name(s): Energizer Manufacturing, Inc. - Steve Hall, Plant Manager Mailing Address: 419 Art Bryan Drive City: Asheboro State: NC Zip Code: 27203-3089 County: United States Day Tele No.: 336-672-4501 Cell No.: EMAIL Address: SteveT.Hall@energizer.com Fax No.: NOTIFICATION OF INTENT (NOI) TO CONSTRUCT OR OPERATE INJECTION WELLS The following are “permitted by rule” and do not require an individual permit when constructed in accordance with the rules of 15A NCAC 02C .0200 (NOTE: This form must be received at least 14 DAYS prior to injection) AQUIFER TEST WELLS (15A NCAC 02C .0220) These wells are used to inject uncontaminated fluid into an aquifer to determine aquifer hydraulic characteristics. IN SITU REMEDIATION (15A NCAC 02C .0225) or TRACER WELLS (15A NCAC 02C .0229): 1) Passive Injection Systems - In-well delivery systems to diffuse injectants into the subsurface. Examples include ORC socks, iSOC systems, and other gas infusion methods (Note: Injection Event Records (IER) do not need to be submitted for replacement of each sock used in ORC systems). 2) Small-Scale Injection Operations – Injection wells located within a land surface area not to exceed 10,000 square feet for the purpose of soil or groundwater remediation or tracer tests. An individual permit shall be required for test or treatment areas exceeding 10,000 square feet. 3) Pilot Tests - Preliminary studies conducted for the purpose of evaluating the technical feasibility of a remediation strategy in order to develop a full scale remediation plan for future implementation, and where the surface area of the injection zone wells are located within an area that does not exceed five percent of the land surface above the known extent of groundwater contamination. An individual permit shall be required to conduct more than one pilot test on any separate groundwater contaminant plume. 4) Air Injection Wells - Used to inject ambient air to enhance in-situ treatment of soil or groundwater. Deemed Permitted GW Remediation NOI Rev. 3-21-2018 Page 2 D. PROPERTY OWNER(S) (if different than well owner/applicant) Name and Title: Same as well owner Company Name Mailing Address: City: State: _______Zip Code: County: Day Tele No.: Cell No.: EMAIL Address: Fax No.: E. PROJECT CONTACT (Typically Environmental Engineering Firm) Name and Title: Chris Means (Associate Geologist) Company Name ERM NC, Inc. Mailing Address: 15720 Brixham Hill Avenue, Suite 120 City: Charlotte State: NC Zip Code: 28277 County: Mecklenburg Day Tele No.: 704-541-8345 Cell No.: 336-406-7625 EMAIL Address: chris.means@erm.com Fax No.: F. PHYSICAL LOCATION OF WELL SITE (1) Facility Name & Address: 419 Art Bryan Drive City: Asheboro County: Randolph Zip Code: 27203 (2) Geographic Coordinates: Latitude**: o ′ _____″N or 35 o. 769492 Longitude**: o ′ _____″W or -79 o. 817961 Reference Datum: Accuracy: Method of Collection: Google Earth Pro **FOR AIR INJECTION AND AQUIFER TEST WELLS ONLY: A FACILITY SITE MAP WITH PROPERTY BOUNDARIES MAY BE SUBMITTED IN LIEU OF GEOGRAPHIC COORDINATES. G. TREATMENT AREA Land surface area of contaminant plume: 3,659,040 square feet (84 acres) Land surface area of inj. well network: 5,000 square feet (< 10,000 ft2 for small-scale injections) Percent of contaminant plume area to be treated: 0.137% (must be < 5% of plume for pilot test injections) H. INJECTION ZONE MAPS – Attach the following to the notification. (1) Contaminant plume map(s) with isoconcentration lines that show the horizontal extent of the contaminant plume in soil and groundwater, existing and proposed monitoring wells, and existing and proposed injection wells; and (2) Cross-section(s) to the known or projected depth of contamination that show the horizontal and vertical extent of the contaminant plume in soil and groundwater, changes in lithology, existing and proposed monitoring wells, and existing and proposed injection wells. (3) Potentiometric surface map(s) indicating the rate and direction of groundwater movement, plus existing and proposed wells. Deemed Permitted GW Remediation NOI Rev. 3-21-2018 Page 3 I. DESCRIPTION OF PROPOSED INJECTION ACTIVITIES – Provide a brief narrative regarding the purpose, scope, and goals of the proposed injection activity. This should include the rate, volume, and duration of injection over time. The preliminary scope of work for the pilot test injection includes the following:  ERM, on behalf of Energizer, will conduct a source area injection of sodium permanganate for pilot test treatment of a dissolved contaminant plume containing primarily PCE and TCE. Two injection events will comprise the pilot test. The initial treatment event will involve injecting a sodium permanganate solution (up to 10% wt/wt) into one existing air sparge well AS-09 to treat the source area of the dissolved contaminant plume. During the initial injection event, the injection location will receive approximately 1,100 gallons of the 10% solution. The targeted injection zone is between 31 and 36 feet below ground surface (bgs). The initial injection is to be completed by the low pressure gravity feeding method if possible. A diaphragm pump will be added to assist the injection process if necessary.  The supplemental injection event will include injecting 1,100 gallons of 10% sodium permanganate into existing air sparging well AS-10 and existing soil vapor extraction (SVE) well SVE-7. The targeted injection zone for the supplemental injection event is between 28 and 33 feet bgs in AS-10 and between 7 and 22 feet bgs in SVE-7. A total of 3,300 gallons of sodium permanganate solution will be injected into the formation. Injection pressures in the treatment zone are expected to be less than 40 psi, if pumping into the formation is required. The anticipated injection rate is between 1 and 5 gallons per minute, although field conditions may vary. The injection events are anticipated to be completed in 5 days total for both events. Based on the results of the injection activities described above, up to two additional pilot test injections may be conducted to further evaluate the efficacy of ISCO for treatment of 1,4-dixoane in the pilot test area. J. APPROVED INJECTANTS – Provide a MSDS for each injectant (attach additional sheets if necessary). NOTE: Only injectants approved by the NC Division of Public Health, Department of Health and Human Services can be injected. Approved injectants can be found online at http://deq.nc.gov/about/divisions/water- resources/water-resources-permits/wastewater-branch/ground-water-protection/ground-water-approved-injectants. All other substances must be reviewed by the DHHS prior to use. Contact the UIC Program for more info (919- 807-6496). Injectant: Sodium Permanganate - RemOx L Carus Corporation Volume of injectant: Up to 10,000 gallons Concentration at point of injection: up to 12% by weight (mixed with water) Percent if in a mixture with other injectants: Not applicable Injectant: Volume of injectant: Concentration at point of injection: Percent if in a mixture with other injectants: Deemed Permitted GW Remediation NOI Rev. 3-21-2018 Page 4 K. WELL CONSTRUCTION DATA (1) Number of injection wells: Proposed 3 Existing (provide GW-1s) (2) For Proposed wells or Existing wells not having GW-1s, provide well construction details for each injection well in a diagram or table format. A single diagram or line in a table can be used for multiple wells with the same construction details. Well construction details shall include the following (indicate if construction is proposed or as-built): (a) Well type as permanent, Geoprobe/DPT, or subsurface distribution infiltration gallery (b) Depth below land surface of casing, each grout type and depth, screen, and sand pack (c) Well contractor name and certification number L. SCHEDULES – Briefly describe the schedule for well construction and injection activities. The initial injection is scheduled to occur starting in late September 2019. The work should take approximately 3 days to complete. The secondary injection schedule is based on the initial results of the first injection and anticipated to occur in November 2019. Additional pilot test injection events would be conducted as needed based on the data collected from the pilot test area within 6 months of injection activities. M. MONITORING PLAN – Describe below or in separate attachment a monitoring plan to be used to determine if violations of groundwater quality standards specified in Subchapter 02L result from the injection activity. Prior to and immediately following ISCO implementation, groundwater samples will be collected from nearby existing monitoring and observation wells. Additional groundwater monitoring events will be conducted 1 month, 3 month, and 6 months following the injection. A summary of the scheduled performance monitoring from the ISCO Pilot Workplan (ERM) submitted to NCDEQ in July 2019 and approved by NCDEQ in August 2019 is attached. N. SIGNATURE OF APPLICANT AND PROPERTY OWNER Well Owner/Applicant: "1 hereby certii5), under penalty of law, that 1 am familiar with the information submitted in this document and all attachments thereto and that, based on my inquiry of those individuals immediately responsible for obtaining said information, 1 believe that the information is true, accurate and complete. 1 am aware that there are significant penalties, including the possibility of fines and imprisonment, for submitting false information. 1 agree to construct, operate, maintain, repair; and if applicable, abandon the injection well and all related appurtenances in accordance with the 15A NCAC 02C 0200 Rules." .5' i + tiziA 'i, 1A'tr+-1„ ' LI\ sST y"' A R, Signa it o Applicant Print or Type Full Name and Title Property Owner (if the property is not owned by the Well Owner/Applicant): "As owner of the property on which the injection well(s) are to be constructed and operated, I hereby consent to allow the applicant to construct each injection well as outlined in this application and agree that it shall be the responsibility of the applicant to ensure that the injection well(s) conform to the Well Construction Standards (15A NCAC 02C .0200)." "Owner" means any person who holds the fee or other property rights in the well being constructed. A well is real property and its construction on land shall be deemed to vest ownership in the land owner, in the absence of contrary agreement in writing. Signature* of Property Owner (if different from applicant) Print or Type Full Name and Title *An access agreement between the applicant and property owner may be submitted in lieu of a signature on this form. Please send 1 (one) hard color copy of his NOI along with a copy on an attached CD or Flash Drive at least two (2) weeks prior to injection to: DWR— UIC Program 1636 Mail Service Center Raleigh, NC 27699-1636 Telephone: (919) 807-6464 Deemed Permitted GW Remediation NO1 Rev. 3-21-2018 Page 5 INJECTION POINT BORING LOGS Concrete Gravel Reddish orange clayey SILT Tan fine sandy clayey SILT Brown Sandy SILT (PWR Auger refusal at 36) 38 36 34 32 30 28 26 24 22 20 18 16 14 12 10 8 6 4 2 0 Flushmount Steel Vault Portland/Bentonite Grout 8.25" Diameter Borehole 2" Stainless Steel Casing Bentonite Seal Well Sand Filter Pack #3 2" Stainless Steel 0.010" Slot Screen End Cap - -- ML ML MH Drilling Method: Drilling Contractor: Responsible Professional: Borehole Diameter: Drilling Equipment: Total Depth (ft): Elevation (msl): Screened Interval: Outer Casing Depth: Depth to Water (Final): Hollow Stem Auger Geoprobe 7822DT Chris Lacko (NC Driller #3516) 8.25" TBD 36 31' - 36' NA TBD ARS Technologies Client: Project:Date Started: Date Completed: Boring ID: Logged By: Project Number: Site Location: Energizer Asheboro Plant II 0314524 AS-9 Tom Naumann 10/6/15 10/8/15 DepthLithologic Description Well Construction Well Construction Details Energizer Latitude: Longitude: TBD TBD Lithology ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ....... ........ ......... . ..... . . ...... .. . ..... . . ...... .. . ..... . . ...... .. . ..... . . ...... .. --...... . . ...... .. . ..... . . ...... .. --...... . . ...... .. . ..... . . ...... .. . ..... . . ...... .. . ..... . __ ....... .. . ..... . . ...... .. . ..... . ___ _. .... .. . ..... . . ...... .. . ..... . --....... .. . ..... . . ...... .. . ..... . . ...... .. . ..... . ERM Concrete Gravel Reddish orange clayey SILT Tan fine sandy clayey SILT 24 22 20 18 16 14 12 10 8 6 4 2 0 Flushmount Steel Vault 4" Stainless Steel Casing Portland/Bentonite Grout Bentonite Seal 10.25" Diameter Borehole Well Sand Filter Pack #1 4" Stainless Steel 0.005" Slot Screen End Cap - -- ML ML Drilling Method: Drilling Contractor: Responsible Professional: Borehole Diameter: Drilling Equipment: Total Depth (ft): Elevation (msl): Screened Interval: Outer Casing Depth: Depth to Water (Final): Hollow Stem Auger Geoprobe 7822DT Chris Lacko (NC Driller #3516) 10.25" TBD 22 7' - 22' NA TBD ARS Technologies Client: Project:Date Started: Date Completed: Boring ID: Logged By: Project Number: Site Location: Energizer Asheboro Plant II 0314524 SVE-7 Tom Naumann 10/7/15 10/9/15 DepthLithologic Description Well Construction Well Construction Details Energizer Latitude: Longitude: TBD TBD Lithology ERM Concrete Gravel Reddish orange clayey SILT Tan fine sandy clayey SILT Brown Sandy SILT (PWR Auger refusal at 33) 34 32 30 28 26 24 22 20 18 16 14 12 10 8 6 4 2 0 Flushmount Steel Vault Portland/Bentonite Grout 8.25" Diameter Borehole 2" PVC Casing 2" Stainless Steel Casing Bentonite Seal Well Sand Filter Pack #3 2" Stainless Steel 0.010" Slot Screen End Cap - -- ML ML MH Drilling Method: Drilling Contractor: Responsible Professional: Borehole Diameter: Drilling Equipment: Total Depth (ft): Elevation (msl): Screened Interval: Outer Casing Depth: Depth to Water (Final): Hollow Stem Auger Geoprobe 7822DT Chris Lacko (NC Driller #3516) 8.25" TBD 33 28' - 33' NA TBD ARS Technologies Client: Project:Date Started: Date Completed: Boring ID: Logged By: Project Number: Site Location: Energizer Asheboro Plant II 0314524 AS-10 Tom Naumann 10/6/15 10/8/15 DepthLithologic Description Well Construction Well Construction Details Energizer Latitude: Longitude: TBD TBD Lithology ERM Table 1Energizer Asheboro Facility ‐ Source Area ISCO Pilot Treatment TestAddress: 419 Art Bryan Drive, Asheboro, North CarolinaDescripionNo. of Injection Points ConstructionDepth of Grout, Screen, and CasingTotal Depth(ft bgs)Injection Zone(ft bgs)Diameter(inch)Injection MethodAir Sparge Well AS‐9(Initial Pilot Injection Event)1 Permanent WellGrout = 0.5‐27Bentonite = 27‐29Sand = 29‐36Casing ‐ 0‐31Screen = 31‐36 36 31‐362Gravity Feed/PressurizedSoil Vapor Extraction Well SVE‐7(Supplemental Pilot Injection Event)1 Permanent WellGrout = 0.5‐3Bentonite = 3‐5Sand = 5‐22Casing ‐ 0‐7Screen = 7‐22 22 7‐22 4Gravity Feed/PressurizedAir Sparge Well AS‐10(Supplemental Pilot Injection Event)1 Permanent WellGrout = 0.5‐24Bentonite = 24‐26Sand = 26‐33Casing ‐ 0‐28Screen = 28‐3333 28‐33 2Gravity Feed/PressurizedObservation Well MW‐23Observation OnlyExisting Permanent WellGrout = 0.5‐7Bentonite = 7‐10Sand = 10‐27Casing ‐ 0‐12Screen = 12‐27 23Observation Only 2Observation OnlyObservation Wells OB‐5 A/B and OB‐6 A/BObservation OnlyProposed Permanent WellsGrout = 0.5‐10 & 0.5‐30Bentonite = 10‐13 & 30‐33Sand = 13‐25 & 33‐40Casing ‐ 0‐15 & 0‐35Screen = 15‐25 & 35‐40A ‐ 25B ‐ 40Observation Only2Observation OnlyNotes:bgs = below ground surface FIGURES Copyright:© 2013 National Geographic Society, i-cubed 02,000 Feet 1:24,000 Legend D:\00GIS\EnergizerGIS\MXD\201703_GWRpt\F1_SLM.mxd, REVISED: 01/03/2017, SCALE: 1:24,000 when printed at 8.5x11DRAWN BY: A Freeman02,000 Feet ¯ 1 inch = 2,000 feet Source: Esri - World Topoographic Map ERM Environmental Resources Management www.erm.com Figure 1 Site Location Map Energizer Battery - Plant II 419 Art Bryan Drive Asheboro, Randolph County North Carolina ¯ ZZZZ ZZZZZZZZZZZ ZZ Z&, &, &, &, &, &,&, &, &, &, &,&, &, &, &,&, &, &, &, &,&, &, &, &, &,&, &, &, &, &,&,&, :9 :9 :9 :9 :9X MW-25 OB-2 MW-1 MW-2 MW-3 MW-4 MW-5 MW-6 MW-7D MW-8D MW-9D MW-10D MW-11 MW-12D MW-13 MW-14D MW-15MW-16D MW-17D MW-18D MW-19 MW-20 MW-21D MW-22 MW-23 MW-24 MW-26D MW-27D MW-28 MW-29D OB-1 OB-3 Martin Marietta Quarry Starpet Inc. SD FibersStarpet Inc. Energizer Battery Site Weeks Construction Covanta (Formerly Garco) Hamlet HaskettsCreek ¯ Legend Site Wells &,Saprolite Monitor Well &,Bedrock Monitor Well &,Observation Well &,Abandoned Monitor Well Remediation System Wells &%Vapor Extraction Well &.Air Sparge Well Supply Wells :9 Private Supply Water Well (Active) :9X Private Supply Water Well (Inactive) Potential Source Area Energizer Battery Property Z Stream (arrow indicates flow direction) Intermittent Stream 0 250 500 Feet Basemap NCCGIA. ERM NC, Inc. 3/28/2017A FreemanAS SHOWN DATE:DRAWN:SCALE: Figure 2 Site Map Energizer Battery - Plant II 419 Art Bryan Drive Asheboro, Randolph County North Carolina &, &, &, &, &,&, &, &, &, &,&, &% &% &%&% &% &% &% &% &% &% &% &% &% &%&% &% &,&. &. &. &. &. &.&. &. &.&. &.&. &. Western Sump Northwest Storage Shed Tank Farm Solidified Bad Anode Storage Former Degreaser System Area (2) Former Virgin TCE ASTs Former Solvent Vapor Recovery Area MW-1 MW-22 MW-23 MW-24 MW-25 MW-26D OP-1 OP-2 OB-1 OB-2OB-3 VE-2 VE-3 VE-4 SVE-5 SVE-6 SVE-7 SVE-8 SVE-9 SVE-10 SVE-11 SVE-12 SVE-13 SVE-14SVE-15 SVE-16 AS-1 AS-1D AS-2 AS-3 AS-4 AS-5 AS-6 AS-7 AS-8 AS-9 AS-10 AS-11 AS-12 AS-13 02550Feet Quarry Floor Elevation 410 ft. (est) F2_SL.mxd D:\00GIS\EnergizerGIS\MXD\201703_GWRpt\ C II ERM CJ CJ ZZZZZZZZZZZZZZZZZZZZZZZZZZZZZZZ ZZZZZZZZZZZZZZZZZZZZZZZZZ ZZZZ Z ZZZZZZZZZZZZZZZZZZZZ ZZ Z ZZZZZZZZZZZZZZZZ Z ZZZZZZZZZZZZZZZ ZZZZ Z ZZZZ ZZ ZZ Z Z ZZ ZZ ZZZZZ Z ZZ ZZZZZZZZZZ ZZ Z&, &, &, &, &, &,&, &, &, &, &,&, &, &, &,&, &, &, &, &,&, &, &, &, &,&, &, &, &, &,&,&, :9 :9 :9 :9 :9X MartinMariettaQuarry Starpet Inc. SD FibersStarpet Inc. EnergizerBatterySite WeeksConstruction Covanta(FormerlyGarco) Hamlet HaskettsCreek ROSE LNYZEX ST CREEK S I D EDRCHAMPAGNE DRCARL DR ASPEN CT DUNWOODYCT L AMBCT RYRDGREENTREE CTHOPEWOOD R D RAVENWOOD DR G R E E N V A L E RD ART BRYAN DR ROCK QUARRY RD MCKNIGHT ST NORTHWOOD DR FOREST B R O O K C I R US HWY 220 BYPMW-07D MW-08D MW-09D MW-10D MW-12D MW-13 MW-14D MW-16D MW-17D MW-18D MW-21D MW-26D MW-27D MW-29D MW-02(688.37) MW-03(678.62)MW-04(679.94) MW-05(671.00) MW-06(692.60) MW-11(669.73) MW-15(656.06) MW-19(676.00) MW-20(668.02) MW-22(686.37) MW-23(688.23) MW-24(692.38) MW-25(689.94) MW-28(688.25) 660 690 680 665685 67 06 7 5 ¯Legend Site Wells &,Saprolite Monitor Well &,Bedrock Monitor Well &,Observation Well &,Abandonded Monitoring Well :9 Private Supply Water Well (Active) :9X Private Supply Water Well (Inactive) Saprolite Aquifer (March 2019) Groundwater Elevation Contour (Dashed in areas of less certainty) Approximate Groundwater Flow Direction Potential Source Area Energizer Battery Property Parcels Z Stream (arrow indicates flow direction) Intermittent Stream Road 0 250 500 Feet Basemap NCCGIA. F4_SapGWE.mxd ERM NC, Inc. 5/8/2019A FreemanAS SHOWN DATE:DRAWN:SCALE: Figure 3Groundwater Elevation Contours Saprolite Aquifer - March 2019 Energizer Battery - Plant II 419 Art Bryan Drive Asheboro, Randolph County North Carolina (668.02) Groundwater Elevation Measurement \\SDCLTDC01\Data\Charlotte\Projects\0498725 Energizer Battery Manufacturing, In ASSVE System O&M.AM\SVE System O&M.AM\GIS\MXD\201904GWRpt\ ERM D D D ~ -■■-■■- ZZZZZZZZZZZZZZZZZZZZZZZZZZZZZZZ ZZZZZZZZZZZZZZZZZZZZZZZZZ ZZZZ Z ZZZZZZZZZZZZZZZZZZZZ ZZ Z ZZZZZZZZZZZZZZZZ Z ZZZZZZZZZZZZZZZ ZZZZ Z ZZZZ ZZ ZZ Z Z ZZ ZZ ZZZ ZZZZZZZZZZ ZZ Z&, &, &, &, &, &,&, &, &, &, &,&, &, &, &,&, &, &, &, &,&, &, &, &, &,&, &, &, &, &,&,&, :9 :9 :9 :9 :9X MartinMariettaQuarry Starpet Inc. SD FibersStarpet Inc. EnergizerBatterySite WeeksConstruction Covanta(FormerlyGarco) Hamlet HaskettsCreek YZEX ST CREEK S I D EDRROSE LNCARL DR ASPEN CT GREENTREE CT DUNWOODYCT RAVENWOOD DRHOPEWOOD R D GREENVALE R D ART BRYAN DR MCKNIGHT ST NORTHWOOD DR ROCK QUARRY RD FOREST BRO O K C I R USHWY220BYP3,00030 030 3MW-02(<0.50) MW-03(8,000)MW-04(<0.50) MW-05(18) MW-06(<0.50) MW-11(1.4) MW-15(<0.50) MW-19(<0.50) MW-20(<0.50) MW-22(3,700) MW-24(11,000) MW-28(<0.50) OB-01(4,200) MW-07D MW-08D MW-09D MW-10D MW-12D MW-13 MW-14D MW-16D MW-17D MW-18D MW-21D MW-26D MW-27D MW-29D ¯ Legend Site Wells &,Saprolite Monitor Well &,Bedrock Monitor Well &,Observation Well &,Abandonded Monitoring Well :9 Private Supply Water Well (Active) :9X Private Supply Water Well (Inactive) Temporary Well Remediation Wells &%Vapor Extract Well &.Air Sparge Well TCE Isoconcentration Contour (March 2019) (Dashed in areas of less certainty) Potential Source Area Energizer Battery Property Parcels Z Stream (arrow indicates flow direction) Intermittent Stream Road 0 250 500 Feet Basemap NC Center for Geographic Information & Analysis. F6_SapTCE.mxd ERM NC, Inc. 4/15/2019A. SoplataAS SHOWN DATE:DRAWN:SCALE: Figure 4TCE Isoconcentration Contours Saprolite Aquifer - March 2019 Energizer Battery - Plant II 419 Art Bryan Drive Asheboro, Randolph County North Carolina TCE = Trichloroethene Concentrations in micrograms per liter (ug/L) (1.4) = TCE concentration collected in March 2019 NS = No sample collected on this date "<" = Not detected at a concentration greater than the laboratory method detection limit \\sdcltdc01\data\Charlotte\Projects\0498725 Energizer Battery Manufacturing, In ASSVE System O&M.AM\SVE System O&M.AM\GIS\MXD\201904GWRpt\ &.&. &. &. &. &. &.&. &. &.&. &.&. &. &, &, &, &, &,&, &, &,&, &% &% &% &% &% &% &% &% &% &% &% &% &% &% &%&% Northwest Storage Shed Tank Farm Solidified Bad Anode Storage Former Degreaser System Area (2) Former Virgin TCE ASTs Western Sump AS-01AS-01D AS-02 AS-03 AS-04 AS-05 AS-06 AS-07 AS-08 AS-09 AS-10 AS-11AS-12 AS-13 SVE-01 SVE-06 SVE-07 SVE-08 SVE-09 SVE-10 SVE-11 SVE-12 SVE-13 SVE-14 SVE-15 SVE-16 VE-02 VE-03 VE-04 300 3 0 10,0 0030 0 3,000 3,0 0 0 MW-22(3,700) MW-23(6,700) MW-24(11,000) MW-25(330) OB-01(4,200) OB-02(330) OB-03(1,500) MW-26D 0 25 50 Feet System Start-up February 22, 2016 SVE only (no sparge) Feb 22-Mar 28, 2016 AS started March 29, 2016 Monitor Well Identification Date Trichloroethene (8260B)Monitor Well Identification Date Trichloroethene (8260B)Monitor Well Identification Date Trichloroethene (8260B) 3 3 3 MW-2 12/17/15 <0.50 MW-15 12/17/15 NS MW-25 12/16/15 820 11/29/16 <0.50 11/29/16 NS 11/29/16 8,700 02/22/17 <0.50 02/24/17 <0.50 02/21/17 3,600 09/07/17 <0.50 09/07/17 <0.50 9/8/17 4,000 02/14/18 1.7 02/14/18 <0.50 02/14/18 6,300 10/02/18 12 10/02/18 <0.50 10/04/18 250 03/07/19 <0.50 03/06/19 <0.50 03/07/19 330 MW-3 12/17/15 NS MW-19 12/17/15 NS MW-28 12/17/15 NS 11/29/16 NS 11/29/16 NS 11/29/16 NS 02/23/17 11,000 02/23/17 <0.50 2/20/17 <0.50 09/07/17 12,000 09/05/17 <0.50 9/5/17 <0.50 02/14/18 11,000 02/14/18 <0.50 02/15/18 <0.50 10/02/18 11,000 10/04/18 <0.50 10/03/18 <0.50 03/05/19 8,000 03/06/19 <0.50 03/04/19 <0.50 MW-4 12/17/15 NS MW-20 12/17/15 NS OB-1 12/16/15 15,000 11/29/16 NS 11/29/16 NS 11/29/16 NS 02/23/17 14.0 02/23/17 <0.50 02/21/17 16,000 09/07/17 6.5 09/07/17 NS 09/08/17 30,000 02/12/18 2.1 02/15/18 NS 02/14/18 88,000 10/01/18 <0.50 10/04/18 <0.50 10/01/18 17,000 03/07/19 <0.50 03/05/19 <0.50 03/07/19 4,200 MW-5 12/17/15 NS MW-22 12/17/15 1,900 OB-2 12/16/15 19,000 11/29/16 NS 11/29/16 4,700 11/29/16 1,300 02/21/17 16.0 02/24/17 1,400 02/21/17 1,600 09/05/17 2.0 09/06/17 170 09/08/17 1,600 02/13/18 2.2 02/15/18 8,200 02/15/18 4,300 10/03/18 1.6 10/05/18 1,100 10/01/18 570 03/07/19 18.0 03/08/19 3,700 03/07/19 330 MW-6 12/17/15 NS MW-23 12/17/15 520,000 OB-3 12/17/15 NS 11/29/16 NS 11/29/16 NS 11/29/16 1,700 02/22/17 <0.50 02/24/17 NS 02/21/17 NS 09/05/17 <0.50 09/07/17 88,000 09/08/17 740 02/13/18 <0.50 02/15/18 100,000 02/14/18 960 10/02/18 <0.50 10/05/18 10,000 10/04/18 4,900 03/06/19 <0.50 03/08/19 6,700 03/07/19 1,500 MW-11 12/17/15 NS MW-24 12/16/15 5,400 11/29/16 NS 11/29/16 6,100 02/24/17 16.0 02/22/17 6,100 09/07/17 11.0 09/08/17 8,200 02/14/18 21.0 02/14/18 6,300 10/03/18 6.5 10/04/18 3,600 03/06/19 1.4 03/07/19 11,000 NC 2L Ground Water StandardNC 2L Ground Water Standard NC 2L Ground Water Standard 0 II ERM CJ CJ CJ - ZZZZZZZZZZZZZZZZZZZZZZZZZZZZZZZ ZZZZZZZZZZZZZZZZZZZZZZZZZ ZZZZ Z ZZZZZZZZZZZZZZZZZZZZ ZZ Z ZZZZZZZZZZZZZZZZ Z ZZZZZZZZZZZZZZZ ZZZZ Z ZZZZ ZZ ZZ Z Z ZZ ZZ ZZZ ZZZZZZZZZZ ZZ Z&, &, &, &, &, &,&, &, &, &, &,&, &, &, &,&, &, &, &, &,&, &, &, &, &,&, &, &, &, &,&,&, :9 :9 :9 :9 :9X MW-07D MW-08D MW-09D MW-10D MW-12D MW-13 MW-14D MW-16D MW-17D MW-18D MW-21D MW-26D MW-27D MW-29D MW-02(<3.0) MW-03(1,100)MW-04(<3.0) MW-05(<3.0) MW-06(<3.0) MW-11(<3.0) MW-15(1.1) MW-19(<3.0) MW-20(<3.0) MW-22(1,900) MW-23(13,000) MW-24(1,400) MW-25(<3.0) MW-28(<3.0) MartinMariettaQuarry Starpet Inc. SD FibersStarpet Inc. EnergizerBatterySite WeeksConstruction Covanta(FormerlyGarco) Hamlet HaskettsCreek YZEX ST CREEKS I D EDRROSE LNCARLDRASPENCT GREENTREE CT DUNWOODY CT RAVENWOOD DRHOPEWOOD R D GREENVALE R D ART BRYAN DR MCKNIGHT ST NORTHWOOD DR ROCK QUARRY RD FOREST BR O O K C I R USHWY220BYP¯ Legend Site Wells &,Saprolite Monitor Well &,Bedrock Monitor Well &,Observation Well &,Abandonded Monitoring Well :9 Private Supply Water Well (Active) :9X Private Supply Water Well (Inactive) Temporary Well Remediation Wells &%Vapor Extract Well &.Air Sparge Well 1,4-Dioxane Isoconcentration Contour (March 2019) Energizer Battery Property Parcels Z Stream (arrow indicates flow direction) Intermittent Stream Road 0 250 500 Feet ERM NC, Inc. 4/18/2019A. SoplataAS SHOWN DATE:DRAWN:SCALE: Figure 51,4-D Isoconcentration Contours Saprolite Aquifer (March 2019) Energizer Battery - Plant II 419 Art Bryan Drive Asheboro, Randolph County North Carolina Basemap Aerial provided by NC One Map System Start-up February 22, 2016 SVE only (no sparge) Feb 22-Mar 28, 2016 AS started March 29, 2016 1,4-D = 1,4-Dioxane Concentrations in micrograms per liter (ug/L) (15) = 1,4-D concentration collected in March 2019 NS = No sample collected on this date "<" = Not detected at a concentration greater than the laboratory method detection limit 3,000 &.&. &. &. &. &. &.&. &. &.&. &.&. &.&, &, &, &, &,&, &, &,&, &% &% &% &% &% &% &% &% &% &% &%&% &% &% &%&% Western Sump Northwest Storage Shed Tank Farm Solidified Bad Anode Storage Former Degreaser System Area (2) Former Virgin TCE ASTs Former Solvent Vapor Recovery Area AS-01D AS-02 AS-03 AS-04 AS-05 AS-06 AS-07 AS-08 AS-09 AS-10 AS-11AS-12 AS-13 SVE-01 SVE-05 SVE-06 SVE-07 SVE-08 SVE-09 SVE-10 SVE-11 SVE-12 SVE-13 SVE-14 SVE-15 SVE-16 VE-02 VE-03 VE-04 MW-22(1,900) MW-23(13,000) MW-24(1,400) MW-25(<3.0) OB-01(120) OB-02(15)OB-03(140) MW-26D 0 25 50 Feet 3 ,00 0 300 30 0 Source Area Detail 30 3300303F8_Sap14D.mxd \\sdcltdc01\data\Charlotte\Projects\0498725 Energizer Battery Manufacturing, In ASSVE System O&M.AM\SVE System O&M.AM\GIS\MXD\201904GWRpt\ Monitor Well Identification Date 1,4 Dioxane (Selective Ion Method - 8260B)Monitor Well Identification Date 1,4 Dioxane (Selective Ion Method - 8260B)Monitor Well Identification Date 1,4 Dioxane (Selective Ion Method - 8260B) 3 3 3 MW-2 12/17/15 <3.0 MW-15 12/17/15 NS MW-25 12/16/15 2.3 11/29/16 <3.0 11/29/16 NS 11/29/16 1.2 02/22/17 <3.0 02/24/17 <3.0 02/21/17 3.2 09/07/17 1.3 09/07/17 <3.0 09/08/17 2.1 02/14/18 <3.0 02/14/18 <3.0 02/14/18 1.3 10/02/18 <3.0 10/02/18 <3.0 10/04/18 <3.0 03/07/19 <3.0 03/06/19 1.1 03/07/19 <3.0 MW-3 12/17/15 NS MW-19 12/17/15 NS MW-28 12/17/15 NS 11/29/16 NS 11/29/16 NS 11/29/16 NS 02/23/17 1,800 02/23/17 <3.0 02/20/17 NS 09/07/17 2,200 09/05/17 <3.0 09/05/17 <3.0 02/14/18 1,700 02/14/18 <3.0 02/15/18 2.6 10/02/18 1,400 10/04/18 <3.0 10/03/18 <3.0 03/05/19 1,100 03/06/19 <3.0 03/04/19 <3.0 MW-4 12/17/15 NS MW-20 12/17/15 NS OB-1 12/16/15 32 11/29/16 NS 11/29/16 NS 11/29/16 NS 02/23/17 3.5 02/23/17 <3.0 02/21/17 180 09/07/17 1 09/07/17 NS 09/08/17 65 02/12/18 <3.0 02/15/18 NS 02/14/18 160 10/01/18 <3.0 10/04/18 <3.0 10/01/18 170 03/07/19 <3.0 03/05/19 <3.0 03/07/19 120 MW-5 12/17/15 NS MW-22 12/17/15 540 OB-2 12/16/15 <3.0 11/29/16 NS 11/29/16 1,200 11/29/16 2.8 02/21/17 17 02/24/17 800 02/21/17 5.4 09/05/17 5.3 09/06/17 360 09/08/17 8 02/13/18 1.7 02/15/18 2,400 02/15/18 2.4 10/03/18 <3.0 10/05/18 1,400 10/01/18 2.5 03/07/19 <3.0 03/08/19 1,900 03/07/19 15 MW-6 12/17/15 NS MW-23 12/17/15 6,200 OB-3 12/17/15 NS 11/29/16 NS 11/29/16 NS 11/29/16 NS 02/22/17 <3.0 02/24/17 NS 02/21/17 NS 09/05/17 <3.0 09/07/17 10000 09/08/17 180 02/13/18 <3.0 02/15/18 11,000 02/14/18 79 10/02/18 <3.0 10/05/18 10,000 10/04/18 140 03/06/19 <3.0 03/08/19 13,000 03/07/19 140 MW-11 12/17/15 NS MW-24 12/16/15 530 11/29/16 NS 11/29/16 1,100 02/24/17 1.2 02/22/17 1,000 09/07/17 <3.0 09/08/17 1,300 02/14/18 1.3 02/14/18 1,000 10/03/18 <3.0 10/04/18 350 03/06/19 <3.0 03/07/19 1,400 NC 2L Ground Water Standard NC 2L Ground Water Standard NC 2L Ground Water Standard 0 II ERM CJ CJ - &. &. &, &% &% &% !. !. AS-09 AS-10 MW-23 SVE-07 SVE-14 SVE-15 OB-5 A/B OB-6 A/B ¯Legend !.Proposed Pilot Test Observation Well Pair Site Wells &,Saprolite Monitor Well &,Bedrock Monitor Well &,Observation Well &,Abandonded Monitoring Well Remediation Wells &%Vapor Extract Well &.Air Sparge Well Energizer Battery Property Building Floorplan 0 2.5 5 Feet Basemap NCCGIA. ERM NC, Inc. 6/28/2019A FreemanAS SHOWN DATE:DRAWN:SCALE: Figure 6Proposed Injection Layout Energizer Battery - Plant II 419 Art Bryan Drive Asheboro, Randolph County North Carolina &.&. &. &. &. &. &.&. &. &.&. &.&.&.&, &, &, &, &, &, &, &, &, &, &, &, &, &, &, &, &, &,&, &, &,&,&, &% &%&% &% &% &%&%&% &%&% &%&%&% &%&%&% 0 125 250 Feet F1_ProposedInjection.mxd \\USBDCFS02\Data\Charlotte\Projects\0498725 Energizer Battery Manufacturing, In ASSVE System O&M.AM\SVE System O&M.AM\GIS\MXD\ --• J • D II ERM 6506556606656706756806856906957000 5 10 15 20 25 30 35 40FIGURECROSS SECTION A-A’ENERGIZER BATTERY - PLANT II419 ART BRYAN DRIVEASHEBORO, NORTH CAROLINA7SVE-07AS-09MW-23AS-101,4-Dioxane 13,000 µg/L TCE: 6,700 µg/LPCE: NDNote: Water level from MW-23 in March 2019. Contaminant concentrations from March 2019. PWRLOADING DOCKTANK FARMPilot test design notes:•Injection program will include the followingwells:•AS‐09 ‐Initial•SVE‐07 & AS‐10 ‐Supplemental•MW‐23 – Observation, existing•OB‐5 A/B & OB‐6 A/B ‐Observation,proposed•Slug testing of above wells pre‐and post‐initialinjection to evaluate effects on permeability•Sampling before injection (baseline) and at 1month, 3, month, and 6 months post injection•Injection treatment area is 20 feet deep by 30feet wide by 20 feet long.  Assume replace 10%of the pore space with injectant, results in3,300 gallons of injectant required.•Injection concentration 10% wt/wtsodiumpermanganate, or less.•Initial injection into AS‐09 of 1,100 gallons•Evaluate permeability impacts beforesubsequent•Supplemental injection of 1,100 gallons intoSVE‐07 and AS‐10•Total injection volume of 3,300 gallonsAA’Initial Injection WellSupplemental Injection WellSupplemental Injection WellExisting Observation WellOB-5 A/BProposed Observation WellOB-6 A/BProposed Observation WellI_•·-••-••··•-•·•-•-I .·.·.·.·.·.·.·.·.·.·.·. ERM .·.·.·.·.·.·.·.·.·.·,·,· )] !l /J !J :_\_\_\:_::,: :,1,1 :::::::: !l /::/:::::: I] ii ::::::j ~ }] ii )j !l • ". •. • ~ I! /J il ·.·.·., il )j i! nu ii }) 11 i:JEJH/J.~: :7':i: .. :'"~:':,,,':;,.\:': .. \7:77:7"""'"77"77"""""''"""""'""""""""""'" ________ _J .·.·, 1·-·.·.·.·.·.·.·.·.·.·.·.· II 1::!:!:!I!:i:!iJ:i:!:/ INJECTION PERFORMANCE MONITORING SUMMARY PILOT TEST MONITORING PLAN The following table outlines the proposed monitoring plan for the duration of the pilot test. Pilot Test Monitoring Plan Baseline and performance groundwater monitoring samples will be collected using low-flow groundwater sampling methods. ERM proposes to use Shealy Environmental Services, Inc. (Shealy) of West Columbia, SC (NC DEQ No. 329) or other NCDEQ-certified laboratory for analytical testing of VOCs via EPA Method 8260. Groundwater samples will also be analyzed for 1,4-dioxane via EPA Method 8260B SIM and manganese via EPA Method 200.7. Shealy will provide ERM with laboratory-prepared containers. Upon filling each container, they will be labeled with the site name, analyses requested, sampler’s initials, date of collection, and time of collection. This information will be transferred to the chain-of-custody to ensure proper tracking and analysis of the sample. Groundwater samples will be placed on ice immediately after collection and maintained under proper chain of custody control throughout the handling process.  Event Wells Ana lysis Baseline SVE-07 , AS-09, . v oes vi a EPA Method 8260 B AS-10, SV E-14 , . 1,4-Dioxane via EPA Method 8260B S IM' AS-0 4, MW -23, . Ma nganese via EPA Met hod 200.7 O B-4N B , O B-5A/8 . Field parame ters: O RP, pH, DO , electrical con d uctivity (EC ) and tempera ture Performance Sam pling MW -23, OB -4A /B, . v oes via EPA Method 8260B* -1 month post injection O B-5N B . 1,4-Dioxane via EPA Method 8260B S IM* . Ma nganese via EPA Met hod 200.7 . Field parame ters: O RP, pH, DO , EC and tem pe rature Performance sampling MW -23, OB -4A /B, . v oes vi a EPA Method 8260B* -3 months foll owing O B-5A/B . 1,4-Dioxane via EPA Method 8260B S IM* injection . Ma nganese via EPA Met hod 200.7 . Field parame ters: O RP, pH, DO , EC and tem pe rature Performance sampling MW -23, OB -4A /B, . v oes via EPA Method 8260B* -6 months fo ll owing O B-5N B . 1,4-Dioxane via EPA Me thod 8260B SIM * injection . Manganese via EPA Me thod 200.7 . Fie ld parameters: O RP , pH , DO , EC and temperature *If pennanganate is visib ly present in the well, sam ples wi ll e it h er be fie ld quench ed to consu me t h e remain in g pennanganat e prior to laborat ory subm itta l, or will not be sampl ed, d epend ing on t he concentrati on of pennangan at e present. Sodium Permanganate SDS 1. Identification Product identifier Other means of identification Recommended use Recommended restrictions SAFETY DATA SHEET RemOx® L ISCO Reagent Not available. Liquid oxidant recommended for applications that require a concentrated permanganate solution. Use in accordance with supplier's recommendations. Manufacturer / Importer / Supplier / Distributor information Manufacturer/Supplier Address Telephone E-mail Website Contact person Emergency Telephone 2. Hazard(s) identification Physical hazards Health hazards OSHA defined hazards Label elements Signal word Hazard statement Precautionary statement Prevention Response Storage Disposal Hazard(s) not otherwise classified (HNOC) Environmental hazards CARUS CORPORATION 315 Fifth Street, Peru, IL 61354, USA 815 223-1500 - All other non -emergency inquiries about the product should be directed to the company salesmkt@caruscorporation.com www.caruscorporation.com Dr. Chithambarathanu Pillai For Hazardous Materials [or Dangerous Goods] Incidents ONLY (spill, leak, fire, exposure or accident), call CHEMTREC at CHEMTREC®, USA: 001 (800) 424-9300 CHEMTREC®, Mexico (Toll -Free - must be dialed from within country): 01-800-681-9531 CHEMTREC®, Other countries: 001 (703) 527-3887 Oxidizing liquids Acute toxicity, oral Skin corrosion/irritation Serious eye damage/eye irritation Specific target organ toxicity, single exposure Not classified. Category 2 Category 4 Category 1 B Category 1 Category 3 respiratory tract irritation Danger May intensify fire; oxidizer. Harmful if swallowed. Causes severe skin burns and eye damage. May cause respiratory irritation. Keep away from heat. Take any precaution to avoid mixing with combustibles. Keep/Store away from clothing//combustible materials. Use only outdoors or in a well -ventilated area. Do not breathe mist or vapor. Wear protective gloves/protective clothing/eye protection/face protection. Do not eat, drink or smoke when using this product. Wash thoroughly after handling. In case of fire: Use water for extinction. If in eyes: Rinse cautiously with water for several minutes. Remove contact lenses, if present and easy to do. Continue rinsing. If on skin (or hair): Take off immediately all contaminated clothing. Rinse skin with water/shower. Wash contaminated clothing before reuse. If swallowed: Rinse mouth. Do NOT induce vomiting. If inhaled: Remove person to fresh air and keep comfortable for breathing. Store locked up. Store in a well -ventilated place. Keep container tightly closed. Dispose of contents/container in accordance with local/regional/national/international regulations. Not classified. Hazardous to the aquatic environment, acute Category 1 hazard Hazardous to the aquatic environment, long-term hazard Category 1 Supplemental information Hazard symbol Hazard statement Precautionary statement Prevention Response Very toxic to aquatic life with long lasting effects. Avoid release to the environment. Collect spillage. 3. Composition/information on ingredients Mixtures Chemical name CAS number Sodium permanganate 10101-50-5 36 - 40 Composition comments 4. First -aid measures Inhalation Skin contact Eye contact Ingestion Most important symptoms/effects, acute and delayed Indication of immediate medical attention and special treatment needed General information 5. Fire -fighting measures Suitable extinguishing media Unsuitable extinguishing media Specific hazards arising from the chemical Special protective equipment and precautions for firefighters All concentrations are in percent by weight unless ingredient is a gas. Gas concentrations are in percent by volume. If breathing is difficult, remove to fresh air and keep at rest in a position comfortable for breathing. Remove victim to fresh air and keep at rest in a position comfortable for breathing. Move to fresh air. For breathing difficulties, oxygen may be necessary. Call a physician or poison control center immediately. Get medical attention immediately. Call a physician if symptoms develop or persist. Get medical attention if symptoms persist. Take off immediately all contaminated clothing. (Caution: Solution may ignite certain textiles). Immediately flush skin with plenty of water. Get medical attention immediately. Wash contaminated clothing before reuse. Contact with skin may leave a brown stain of insoluble manganese dioxide. This can be easily removed by washing with a mixture of equal volume of household vinegar and 3% hydrogen peroxide, followed by washing with soap and water. Immediately flush with plenty of water for up to 15 minutes. Remove any contact lenses and open eyelids wide apart. Continue rinsing. Get medical attention immediately. Immediately rinse mouth and drink plenty of water. Never give anything by mouth to a victim who is unconscious or is having convulsions. Do not induce vomiting. If vomiting occurs, keep head low so that stomach content doesn't get into the lungs. Get medical attention immediately. Before using, read Material Safety Data Sheet (MSDS) for this product. Rinse container at least three times to an absence of pink color before disposing. Contact with this material will cause burns to the skin, eyes and mucous membranes. Corrosive effects. Irritation of eyes and mucous membranes. Symptoms may include stinging, tearing, redness, swelling, and blurred vision. May cause temporary blindness and severe eye damage. Permanent eye damage including blindness could result. Show this safety data sheet to the doctor in attendance. Provide general supportive measures and treat symptomatically. In case of shortness of breath, give oxygen. Decomposition products are alkaline. Brown stain is insoluble manganese dioxide. In the case of accident or if you feel unwell, seek medical advice immediately (show the label where possible). If you feel unwell, seek medical advice (show the label where possible). Ensure that medical personnel are aware of the material(s) involved, and take precautions to protect themselves. For personal protection, see Section 8 of the MSDS. Show this safety data sheet to the doctor in attendance. Wash contaminated clothing before reuse. Flood with water from a distance, water spray or fog. The following extinguishing media are ineffective: Dry chemical. Foam. Carbon dioxide (CO2). Halogenated materials. May intensify fire; oxidizer. May ignite combustibles (wood, paper, oil, clothing, etc.). Contact with incompatible materials or heat (135 °C / 275 °F) could result in violent exothermic chemical reaction. Oxidizing agent, may cause spontaneous ignition of combustible materials. By heating and fire, corrosive vapors/gases may be formed. Self-contained breathing apparatus and full protective clothing must be worn in case of fire. Selection of respiratory protection for firefighting: follow the general fire precautions indicated in the workplace. Fire -fighting equipment/instructions Move container from fire area if it can be done without risk. Cool containers exposed to flames with water until well after the fire is out. Prevent runoff from fire control or dilution from entering streams, sewers, or drinking water supply. Dike fire control water for later disposal. Water runoff can cause environmental damage. 6. Accidental release measures Personal precautions, protective equipment and emergency procedures Methods and materials for containment and cleaning up Environmental precautions 7. Handling and storage Precautions for safe handling Conditions for safe storage, including any incompatibilities Keep unnecessary personnel away. Keep upwind. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Avoid inhalation of vapors and contact with skin and eyes. Wear protective clothing as described in Section 8 of this safety data sheet. Local authorities should be advised if significant spillages cannot be contained. Keep combustibles (wood, paper, oil, etc.) away from spilled material. Should not be released into the environment. This product is miscible in water. Large Spills: Stop leak if possible without any risk. Dike the spilled material, where this is possible. Proceed with either of the following two options depending upon the size of the spill and the availability of the neutralizing agents: Option # 1: Dilute to approximately 6% with water, and then reduce with sodium thiosulfate, a bisulfite or ferrous salt solution. The bisulfite or ferrous salt may require some dilute sulfuric acid (10% w/w) to promote reduction. Neutralize with sodium carbonate to neutral pH, if acid was used. Decant or filter and deposit sludge in approved landfill. Where permitted, the sludge may be drained into sewer with large quantities of water. Option # 2: Absorb with inert media like diatomaceous earth or inert floor dry, collect into a drum and dispose of properly. Do not use saw dust or other incompatible media. Disposal of all materials shall be in full and strict compliance with all federal, state, and local regulations pertaining to permanganates. To clean contaminated floors, flush with abundant quantities of water into sewer, if permitted by federal, state, and local regulations. If not, collect water and treat as described above. Cover with reducing agent (e.g. sodium bisulphite/thiosulphate or a ferrous salt plus 2M H2SO4). Transfer to container with water and neutralize with soda ash. Otherwise, absorb spill with vermiculite or other inert material, then place in a container for chemical waste. Do not use sawdust or other combustible material. Following product recovery, flush area with water. Prevent product from entering drains. Small Spills: Cover with reducing agent (e.g. sodium bisulphite/thiosulphate or a ferrous salt plus 2M H2SO4). Transfer to container with water and neutralize with soda ash. Clean surface thoroughly to remove residual contamination. Never return spills in original containers for re -use. Never return spills in original containers for re -use. Do not allow to enter drains, sewers or watercourses. Contact local authorities in case of spillage to drain/aquatic environment. Take any precaution to avoid mixing with combustibles. Keep away from clothing and other combustible materials. Do not get this material in your eyes, on your skin, or on your clothing. Do not breathe mist or vapor. If clothing becomes contaminated, remove and wash off immediately. Spontaneous ignition may occur in contact with cloth or paper. When using, do not eat, drink or smoke. Good personal hygiene is necessary. Wash hands and contaminated areas with water and soap before leaving the work site. Avoid release to the environment. Store locked up. Keep container tightly closed and in a well -ventilated place. Store in a cool, dry place. Store away from incompatible materials (See Section 10). Follow applicable local/national/international recommendations on storage of oxidizers. Store in accordance with NFPA 430 requirements for Class II oxidizers. 8. Exposure controls/personal protection Occupational exposure limits No exposure limits noted for ingredient(s). US. OSHA Table Z-1 Limits for Air Contaminants (29 CFR 1910.1000) Components Type Value Sodium permanganate Ceiling 5 mg/m3 (CAS 10101-50-5) US. ACGIH Threshold Limit Values Components Type Value Form Sodium permanganate (CAS 10101-50-5) TWA 0.1 mg/m3 lnhalable fraction. 0.02 mg/m3 Respirable fraction. US NIOSH Pocket Guide to Chemical Hazards: Recommended exposure limit (REL) Components Type Value Form Sodium permanganate TWA (CAS 10101-50-5) US NIOSH Pocket Guide to Chemical Hazards: Short Term Exposure Limit (STEL) Components 1 mg/m3 Type Value Fume. Form Sodium permanganate (CAS 10101-50-5) Biological limit values Exposure guidelines Appropriate engineering controls STEL 3 mg/m3 Fume. No biological exposure limits noted for the ingredient(s). Follow standard monitoring procedures. Provide adequate general and local exhaust ventilation. An eye wash and safety shower must be available in the immediate work area. Individual protection measures, such as personal protective equipment Eye/face protection Skin protection Hand protection Other Respiratory protection Thermal hazards General hygiene considerations Wear safety glasses with side shields (or goggles). Wear face shield if there is risk of splashes. Wear chemical -resistant, impervious gloves. Use protective gloves made of: Rubber or plastic. Suitable gloves can be recommended by the glove supplier. Wear appropriate chemical resistant clothing. Rubber or plastic apron. In case of inadequate ventilation or risk of inhalation of vapors, use suitable respiratory equipment. In the United States of America, if respirators are used, a program should be instituted to assure compliance with OSHA 29 CFR 1910.134. Wear appropriate thermal protective clothing, when necessary. When using, do not eat, drink or smoke. Keep from contact with clothing and other combustible materials. Remove and wash contaminated clothing promptly. Wash hands before breaks and immediately after handling the product. Handle in accordance with good industrial hygiene and safety practice. 9. Physical and chemical properties Appearance Physical state Form Color Odor Odor threshold pH Melting point/freezing point Initial boiling point and boiling range Flash point Evaporation rate Flammability (solid, gas) Dark purple liquid. Liquid. Aqueous solution. Dark purple. Odorless. Not available. 5-8 < 24.8 °F (< -4 °C) > 213.8 °F (> 101 °C) Does not flash. As water. Not applicable. Upper/lower flammability or explosive limits Flammability limit - lower (%) Flammability limit - upper (%) Vapor pressure Vapor density Relative density Solubility(ies) Partition coefficient (n-octanol/water) Auto -ignition temperature Decomposition temperature Viscosity Not applicable. Not applicable. 760 mm Hg (105 °C) Not available. 1.37 - 1.4 (20 °C) ( Water = 1) Miscible with water. Not available. Not available. Not available. Not available. Other information Explosive properties Not explosive. Can explode in contact with sulfuric acid, peroxides and metal powders. Oxidizing properties Strong oxidizing agent. 10. Stability and reactivity Reactivity The product is non -reactive under normal conditions of use, storage and transport. Chemical stability Stable at normal conditions. Possibility of hazardous Contact with combustible material may cause fire. Can explode in contact with sulfuric acid, reactions peroxides and metal powders. Conditions to avoid Contact with incompatible materials or heat (135 °C / 275 °F) could result in violent exothermic chemical reaction. Incompatible materials Acids. Peroxides. Reducing agents. Combustible material. Metal powders. Hazardous decomposition By heating and fire, corrosive vapors/gases may be formed. Contact with hydrochloric acid products liberates chlorine gas. 11. Toxicological information Information on likely routes of exposure Ingestion Causes digestive tract burns. Harmful if swallowed. Ingestion causes burns of the upper digestive and respiratory tracts. Inhalation May cause irritation to the respiratory system. Skin contact Causes severe skin burns. Eye contact Causes serious eye damage. Symptoms related to the Contact with this material will cause burns to the skin, eyes and mucous membranes. Permanent physical, chemical and eye damage including blindness could result. toxicological characteristics Information on toxicological effects Acute toxicity Components Causes severe skin burns and eye damage. Causes burns. Harmful if swallowed. Health injuries are not known or expected under normal use. Harmful if swallowed. Species Test Results Potassium permanganate (CAS 7722-64-7) Acute Dermal LD50 Rat 2000 mg/kg Oral LD50 Rat 2000 mg/kg Toxicity data are not available for sodium permanganate. Toxicity is expected to be similar to that of potassium permanganate. Skin corrosion/irritation Causes severe skin burns. Serious eye damage/eye Causes serious eye damage. irritation Respiratory sensitization Not classified. Skin sensitization Not classified. Germ cell mutagenicity Not classified. Carcinogenicity Not classified. Reproductive toxicity Not classified. Specific target organ toxicity - May cause irritation of respiratory tract. single exposure Specific target organ toxicity - Not classified. repeated exposure Aspiration hazard Not classified. Further information Chronic effects are not expected when this product is used as intended. Prolonged exposure, usually over many years, to manganese oxide fume/dust can lead to chronic manganese poisoning, chiefly affecting the central nervous system. 12. Ecological information Ecotoxicity Very toxic to aquatic life with long lasting effects. Components Species Test Results Potassium permanganate (CAS 7722-64-7) Aquatic Fish LC50 Toxicity data are not available Persistence and degradability Bioaccumulative potential Mobility in soil Mobility in general Other adverse effects Bluegill (Lepomis macrochirus) Carp (Cyprinus carpio) Goldfish (Carassius auratus) Milkfish, salmon -herring (Chanos chanos) Rainbow trout (Oncorhynchus mykiss) 2.7 mg/I, 96 hours, static 2.3 mg/I, 96 hours, flow through 2.3 mg/I, 96 hours 1.8 - 5.6 mg/I 3.16 - 3.77 mg/I, 96 hours 2.97 - 3.11 mg/I, 96 hours 3.3 - 3.93 mg/I, 96 hours, static > 1.4 mg/I, 96 hours 1.8 mg/I, 96 hours 1.08 - 1.38 mg/I, 96 hours 0.77 - 1.27 mg/I, 96 hours Rainbow trout,donaldson trout 0.275 - 0.339 mg/I, 96 hours (Oncorhynchus mykiss) for sodium permanganate. Toxicity is expected to be similar to that of potassium permanganate. Expected to be readily converted by oxidizable materials to insoluble manganese oxide. Potential to bioaccumulate is low. The product is miscible with water. May spread in water systems. The product is miscible with water. May spread in water systems. None known. 13. Disposal considerations Disposal instructions Local disposal regulations Hazardous waste code Waste from residues / unused products Contaminated packaging 14. Transport information DOT UN number UN proper shipping name Transport hazard class(es) Subsidiary class(es) Packing group Environmental hazards Marine pollutant Special precautions for user Special provisions Packaging exceptions Packaging non bulk Packaging bulk IATA UN number UN proper shipping name Transport hazard class(es) Subsidiary class(es) Packaging group Environmental hazards Labels required ERG Code Dispose of contents/container in accordance with local/regional/national/international regulations. Rinse container at least three times to an absence of pink color before disposing. D001: Ignitable waste The Waste code should be assigned in discussion between the user, the producer and the waste disposal company. Do not allow this material to drain into sewers/water supplies. Dispose of in accordance with local regulations. Since emptied containers may retain product residue, follow label warnings even after container is emptied. Rinse container at least three times to an absence of pink color before disposing. Empty containers should be taken to an approved waste handling site for recycling or disposal. UN3214 Permanganates, inorganic, aqueous solution, n.o.s. (Sodium permanganate) 5.1 I I Yes Read safety instructions, SDS and emergency procedures before handling. 26, 353, IB2, T4, TP1 152 202 242 UN3214 Permanganates, inorganic, aqueous solution, n.o.s. (Sodium permanganate) 5.1 I I Yes 5.1 5L Special precautions for user IMDG UN number UN proper shipping name Transport hazard class(es) Subsidiary class(es) Packaging group Environmental hazards Marine pollutant Labels required EmS Special precautions for user Transport in bulk according to Annex II of MARPOL 73/78 and the IBC Code 15. Regulatory information US federal regulations Read safety instructions, SDS and emergency procedures before handling. UN3214 PERMANGANATES, INORGANIC, AQUEOUS SOLUTION, N.O.S. (Sodium permanganate) 5.1 I I Yes 5.1 F-H, S-Q Read safety instructions, SDS and emergency procedures before handling. This substance/mixture is not intended to be transported in bulk. This product is a "Hazardous Chemical' as defined by the OSHA Hazard Communication Standard, 29 CFR 1910.1200. All components are on the U.S. EPA TSCA Inventory List. CERCLA/SARA Hazardous Substances - Not applicable. Drug Enforcement Administration (DEA) (21 CFR 1310.02 (b) 8: List II chemical. TSCA Section 12(b) Export Notification (40 CFR 707, Subpt. D) Not regulated. US. OSHA Specifically Regulated Substances (29 CFR 1910.1001-1050) Not listed. CERCLA Hazardous Substance List (40 CFR 302.4) Sodium permanganate (CAS 10101-50-5) LISTED Superfund Amendments and Reauthorization Act of 1986 (SARA) Hazard categories SARA 302 Extremely hazardous substance SARA 311/312 Hazardous chemical SARA 313 (TRI reporting) Chemical name Immediate Hazard - Yes Delayed Hazard - No Fire Hazard - Yes Pressure Hazard - No Reactivity Hazard - No No Yes CAS number % by wt. Sodium permanganate 10101-50-5 36 - 40 Potassium permanganate 7722-64-7 2 Other federal regulations Clean Air Act (CAA) Section 112 Hazardous Air Pollutants (HAPs) List Sodium permanganate (CAS 10101-50-5) Clean Air Act (CAA) Section 112(r) Accidental Release Prevention (40 CFR 68.130) Not regulated. Safe Drinking Water Act Not regulated. (SDWA) Drug Enforcement Administration (DEA). List 2, Essential Chemicals (21 CFR 1310.02(b) and 1310.04(f)(2) and Chemical Code Number Sodium permanganate (CAS 10101-50-5) 6588 Drug Enforcement Administration (DEA). List 1 & 2 Exempt Chemical Mixtures (21 CFR 1310.12(c)) Sodium permanganate (CAS 10101-50-5) 15 % wt DEA Exempt Chemical Mixtures Code Number Sodium permanganate (CAS 10101-50-5) 6588 Food and Drug Administration (FDA) Not regulated. US state regulations This product does not contain a chemical known to the State of California to cause cancer, birth defects or other reproductive harm. US. Massachusetts RTK - Substance List Not regulated. US. New Jersey Worker and Community Right -to -Know Act Sodium permanganate (CAS 10101-50-5) 500 Ibs US. Pennsylvania RTK - Hazardous Substances Not regulated. US. Rhode Island RTK Sodium permanganate (CAS 10101-50-5) US. California Proposition 65 US - California Proposition 65 - Carcinogens & Reproductive Toxicity (CRT): Listed substance Not listed. International Inventories Country(s) or region Inventory name On inventory (yes/no)* Australia Australian Inventory of Chemical Substances (AICS) Yes Canada Domestic Substances List (DSL) No Canada Non -Domestic Substances List (NDSL) Yes China Inventory of Existing Chemical Substances in China (IECSC) Yes Europe European Inventory of Existing Commercial Chemical Yes Substances (EINECS) Europe European List of Notified Chemical Substances (ELINCS) No Japan Inventory of Existing and New Chemical Substances (ENCS) Yes Korea Existing Chemicals List (ECL) Yes New Zealand New Zealand Inventory Yes Philippines Philippine Inventory of Chemicals and Chemical Substances Yes (PICCS) United States & Puerto Rico Toxic Substances Control Act (TSCA) Inventory Yes *A "Yes" indicates this product complies with the inventory requirements administered by the governing country(s). A "No" indicates that one or more components of the product are not listed or exempt from listing on the inventory administered by the governing country(s). 16. Other information, including date of preparation or last revision Issue date Revision date Version # 01 NFPA Ratings References 27-November-2013 HSDB® - Hazardous Substances Data Bank Registry of Toxic Effects of Chemical Substances (RTECS) EPA: AQUIRE database NLM: Hazardous Substances Data Base US. IARC Monographs on Occupational Exposures to Chemical Agents IARC Monographs. Overall Evaluation of Carcinogenicity National Toxicology Program (NTP) Report on Carcinogens ACGIH Documentation of the Threshold Limit Values and Biological Exposure Indices