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HomeMy WebLinkAboutWQ0035324_Complete File - Historical_20150813(YVATC ATC ASSOCIATES OF NORTH CAROLINA, P.C. Engineering Individual Solutions August 10, 2015 2725 East Millbrook Road Suite 121 Raleigh, NC 27604 Tel: 919-871-0999 Fax: 919-871-0335 www.ateassociates.com N.C. Engineering License No. C-1598 North Carolina Department of Environment and Natural Resources Division of Water Resources — Information Processing Unit 1617 Mail Service Center Raleigh, North Carolina 27699-1617 Re: Quarterly Groundwater Results —June 2015 Former Pro Cleaners f� 8377 Creedmoor Road AUG 13 9015 Raleigh, Wake County, North Carolina Groundwater Remediation Permit No. WQ0035324 DWR SECTION DSCA Site Identification No. 920001 WOWTION PROCESSING UNIT ATC Project No. DC9201 SL30 ATC Associates of North Carolina, P.C. (ATC), under contract to the North Carolina Drycleaning Solvent Cleanup Act (DSCA), is providing the June 2015 groundwater sampling results required by Groundwater Remediation Permit No. WQ0035324 for the former Pro Cleaners site in Raleigh, North Carolina. The analytical results for the June 2015 post -injection sampling event are reported on the enclosed GW-59 Groundwater Quality Monitoring Compliance Report Forms in Appendix A. The required monitoring wells and water supply wells were sampled pursuant to the referenced permit. Corresponding GW-1 forms were submitted to NCDENR in the Quarterly Groundwater Results submitted August 29, 2012. For the June 2015 reporting period, a GW-59A form is included in Appendix B. Note that the full scale compliance boundary, documented in the Injection Application Addendum submitted to NCDENR on March 23, 2011, is used in lieu of a review boundary. Analytical data tables are included in Appendix C, and document groundwater analytical data from monitoring wells, water supply wells, and natural attenuation parameters. Note that extraction wells EW-8 and EW-9 were formerly injection wells IW-8 and IW-9. Also note that the extraction well EW-8 was not sampled during the June 2015 event due to an issue with the extraction pump at the time of sampling. During this sampling event, semi-annual samples were not collected from water supply well 8408 and 8409 Azalea Place Drive and 8412 and 8413 Camellia Drive due semi-annual sampling. Monitoring wells MW-I I and MW-12 historically contain a low water level. As such, some field analyzed natural attenuation parameters were not able to be analyzed and are listed as "NA" on the GW-59 forms. Complete laboratory reports for the June 2015 sampling event is included in Appendix D. The next quarterly sampling event is scheduled for September 2015. Former Pro Cleaners Permit No. WQ0035324 August 10, 2015 Page 2 GW-59 forms. Complete laboratory reports for the June 2015 sampling event is included in Appendix D. The next quarterly sampling event is scheduled for September 2015. If you have any questions or require additional information, please contact our office at (919) 871- 0999. Sincerely, ATC Associates of North Carolina, P.C. Elizabeth Depoy Justin C. Ballard, P.G. Staff Scientist Project Manager Former Pro Cleaners Permit No. WQ0035324 APPENDIX A GW-59 COMPLIANCE REPORT FORMS August 10, 2015 Page 3 GW-59A COMPLIANCE REPORT FORM Permit # W00035324 !Subunit one each monitoring period udtk Gi1'-59 forms., 1 Enter date monitoring results were due. ( 8/10/2015 ) Will this monitoring report (GW-59 and GW59A) s No be submitted after the established due date? 2 Was any required information missing on the GK'-59 report forms? % IF the answer to question 1 or 2 is "YES", list in the space provided below the well identification number(s) and explain the problems encountered in obtaining the required information. For water supply wells, well construction information is unavailable, including well diameter, depth, M.P. elevation, screened interval, and depth to water. 3 Are any of the monitor wells in need of repair or maintenance (damaged casing, unlocked or missing cap, missing YE5 -'O identification plate, area overgrown, etc.)? If the an.nce• is "Yes", contact the Regional Office for guidance. 4 Are any monitored constituents equal to or above the established standards? -(gT No If the answer to question 4 is "NO", skip to section 8. If the answer to question 4 is "YES" list the affected wells individually with constituent(s) and concentration(s) exceeding standards in the space provided below. "ALL UNITS IN mg/L MW-5: PCE (0.0035) MW-16: PCE (0.0055) MW-10B: PCE (0.11) MW-24S: PCE (0.021) MW-11A: PCE (0.002) MW-24D: PCE (0.0012) MW-12: PCE (0.00077) EW-8 (formerly IW-8): Not sampled due to extraction pump not working at time of sampling event 5 For the constituents identified in question 4 above, have standards been exceeded previously for the S `o same constituent(s) in the same well(s) in the last two years? If the answer to question 5 is "NO", skip to section 8. if the answer to question 5 is "YES", list in the space provided below, each well with constituent(s) exceeding standards, concentration(s) reported, and sample collection date for each occurrence (for the last two years). SEE ATTACHED "ALL UNITS IN mg/L 6 Are the monitoring wells listed in section 5 located at or beyond the review boundary? YE NO if the answer is "YES", a groundwater quality problem maybe occurring. CONTACT THE REGIONAL OFFICE IMMEDIATELY FOR GUIDANCE. If the answer is "NO", monitoring wells maybe improperly located; contact the Regional Office. Wells located at or beyond the review boundary: MW-5, MW-10A, MW-10B, MW-11A, MW-11B. MW-12, MW-16, MW-24S, MW-24D, EW-8, EW-9 7 Is the permittee implementing previously approved actions required by the Division involving this NO groundwater quality problem? If the answer to question 7 is `YES", describe those actions in the space provided below. If the answer to question 7 is "NO", contact the Regional Office within 90 days: an evaluation may be required to determine the impact the waste disposal system is having at the review and compliance boundaries surrounding this facility. Failure to do so may subject the permittee to a Notice of Violation. fines, and/or penalties, In accordance with Groundwater Remediation Permit #W00035324, issued on April 16, 2012, a pump and treat system was installed at the site in August 2012. Pilot scale operations began on August 29, 2012 and full scale operations began on September 10, 2013. Pursuant to the permit, sampling of eleven pre -agreed upon monitoring wells will continue on a quarterly basis. Note that Permit #W00035324 requests the sampling of twelve monitoring wells, however, one of these, MW-4, was abandoned prior to 2008. 8 The person completing this portion (GW-59A) of the monitoring report should sign below and submit this form with GW-59 forms for required wells to the address provided at the top of the current GW-59 form. I hereby acknowledge that the above information was evaluated and the information submitted in this report (Compliance Report GW-59A) is true and complete to the best of my knowledge. Signature of Permittee (or Authorized Agent) Date GW-59A 128'2003 GROUNDWATER QUALITY MONITORING: COMPLIANCE REPORT FORM FACILITY INFORMATION Facility Name: Former Pro Cleaners Permit Name (if different): Facility Address: 8377 Creedmoor Road Raleigh NC 27613 Raleigh NC c,." ltact Person: Justin Ballard II Location/Site Name: Former Pro Cleaners SUBMIT FORM ON YELLOW PAPER ONLY or 27613 County Wake irip FELL ID NUMBER (from Permit): EW-9 (formerly IW-9) fell Depth: 87 ft. epth to Water Level 82546: NA ft. below measuring point easuring Point is 0 ft. above land surface Dlume of water pumped/bailed before sampling: 10 annDles for metals were collected unfiltered: ❑ YES Telephone#: 919-871-0999 No. of wells to be sampled: 20 DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919-807-6306 PERMIT Number: Expiration Date: July 31, 2016 Non -Discharge WQ0035324 UIC NPDES Other TYPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field 0 Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: Date sample collected: 6/17/2015 Well Diameter: 2 in. 45I 611 Greened Interval: 35166/62/)2ft. to . Relative M.P. Elevation: 478.90 ft. minutes (to parameter stabilization) Id X0 91 FIELD ANALYSES: WAS DRY pH ooaoa: 5.92 units Temp. 00010: 30.69 oC at time of sampling, Spec. Cond. Ooosa: 91 uMhos check Odor 00085: here: Appearance 0 ate sample analyzed: 6/18,19,22,23,24,25/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 kRAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 0.0039J mg/L Pb - Lead o1o51 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Not Detected mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L E L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Un Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L Tetrachloroethene: 0.22 mg/L tt i IC 1 2 ��,G pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: 0.004 mg/I TOC 00680 0.242J mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: 0.0048 mg/I Chloride oosao mg/L Cd - Cadmium 01027 ug/L trans-1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 >1200 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑ Yes (1) iv No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH, as N; Ammonia Nitrogen, Total) Mn - Manganese 01055 910 ug/L Sulfate , method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 C_ SAL-CA-C—E�' Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: , DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807-6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July 31, 2016 Facility Name: Former Pro Cleaners Non -Discharge W00035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh (str­ ,' NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery 'c," s'" `°' 17"'I ❑ Spray Field © Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION WELL ID NUMBER (from Permit): MW-5 Well Depth: 68.5 ft. Depth to Water Level 82546: 22.92 ft. below measuring point Measuring Point is 0 ft. above land surface Volume of water pumped/bailed before sampling: 27 Samples for metals were collected unfiltered: ❑ YES Date sample collected: 6/16/2015 Well Diameter: 2 in. Screened Interval: 63.5 ft. to 68.5 ft. Relative M.P. Elevation: 472.49 ft. of minutes (to parameter stabilization) NO and field acidified: ❑ YES M NO FIELD ANALYSES: pH 00400: 5.92 units Spec. Cond. 00094: 91 Odor 00085: Appearance Temp. 00010: 30.69 °C µMhos ate sample analyzed: 6/18,19,22,23,24,25/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 4RAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 Not Detected mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Not Detected mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum olim mg/L Tetrachloroethene: 0.0035 mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichooroethene: 0.00022J mg/1 TOC 00680 Not Detected mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: 0.00088J mg/1 Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- l,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 Not Detected ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑ Yes (1) (0 No (0) Specific Conductance 00095 LtMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 0.29J mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH,as N;Ammonia Nitrogen, Total) Mn - Manganese 01055 15 ug/L Sulfate , method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 WAS DRY at time of sampling, check here: For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 �..rSYr..I � • B n L�-A-F9 Permittee (or Authorized Agent) Name and Title - Please print or type GROUNDWATER QUALITY MONITORING: COMPLIANCE REPORT FORM acility Name: Former Pro Cleaners ermit Name (if different): acility Address: 8377 Creedmoor Road Raleigh NC 27613 Raleigh «A NC ioavl tact Person: Justin Ballard I Location/Site Name: Former Pro Cleaners 27613 (zir) or SUBMIT FORM ON YELLOW PAPER ONLY County Wake Telep hone#: 919-871-0999 No. of wells to be sampled: 20 DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807.6306 PERMIT Number: Expiration Date: July31,2016 Non -Discharge W00035324 UIC NPDES Other TYPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field © Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: WELL ID NUMBER (from Permit): MW-10B Well Depth: 45 ft. Depth to Water Level 82546: 37.73 ft. below measuring point Measuring Point is 0 ft. above land surface Volume of water pumped/bailed before sampling: 1 Samples for metals were collected unfiltered: ❑ YES ❑ Date sample collected: 6/16/2015 FIELD ANALYSES: Well Diameter: 2 in. pH 00400: NA units Temp. 00010: Screened Interval: 25 ft. to 45 ft. Spec. Cond. 00094; NA Relative M.P. Elevation: 480.65 ft. Odor 00085: Va*ensminutes (insufficient recharge for purging) Appearance NO and field acidified: ❑ YES ❑� NO NA oC µMhos WAS DRY at time of sampling, check here: LABORATORY INFORMATION Date sample analyzed: 6/19,22,23,24,25,26/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 0.0027J mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 0.047J mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum o1105 mg/L Tetrachloroethene: 0.11 mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: 0.0006J mg/L TOC 00680 0.26J mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 Not Detected ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑ Yes (1) ❑ No (0) Specific Conductance 00095 uMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH, as N; Ammonia Nitrogen, Total) Mn - Manganese 01055 400 ug/L Sulfate , method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 Permittee (or Authorized Agent) Name and Title - Please print or type •/L Effluent Total VOCs:I at the laboratory analytical data was produced using fines and imprisonment for knowing violations. RAW' OM .II L16l mg/L VOC Removal% 100 GW-59 Rev.8/2013 GROUNDWATER QUALITY MONITORING: COMPLIANCE REPORT FORM or Facility Name: Former Pro Cleaners Permit Name (if different): Facility Address: 8377 Creedmoor Road Raleigh NC 27613 NC 27613 iary� (9i:n,�i (z�o1 Contact Person: Justin Ballard Well Location/Site Name: Former Pro Cleaners SUBMIT FORM ON YELLOW PAPER ONLY County Wake Telephone#: 919-871-0999 No. of wells to be sampled: 20 DEPARTMENT OF ENVIRONMENT 8 NATURAL RESOURCES DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919-807-6306 PERMIT Number: Expiration Date: July31,2016 Non -Discharge W00035324 UIC NPDES Other TYPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field 0 Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): MW-10A Date sample 6/16/2015 ple collected: FIELD ANALYSES: WAS DRY Well Depth: 80 ft. Well Diameter: 2 in. pH 00400: 5.67 units Temp. 00010: 24.39 °C at time of sampling, Depth to Water Level 82546: 37.82 ft. below measuring point Screened Interval: 75 ft. to 80 ft. Spec. Cond. 00094: 52 µMhos check Measuring Point is 0 ft. above land surface Relative M.P. Elevation: 480.65 ft. Odor o0085: here: Volume of water pumped/bailed before sampling: 24 gaueaa minutes (to parameter stabilization) Appearance ❑ Samples for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES ❑ NO LABORATORY INFORMATION Date sample analyzed: 6/19,22,23,24,25,28/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 '0.0025J mg/L Pb - Lead o1051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Not Detected mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L Tetrachloroethene:'O.0o028J mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: Not Detected TOC 0068o Not Detected mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 Not Detected ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑ Yes (1) ❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260B Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH,as N;Ammonia Nitrogen, Total) Mn -Manganese o1055 17 ug/L Sulfate ,method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite , method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 Permittee (or Authorized Agent) Name and Title - Please print or type Signature of IS GW-59 Rev.8/2013 ROUNDWATER QUALITY MONITORING: OMPLIANCE REPORT FORM Name: Former Pro Cleaners Name (if different): Address: 8377 Creedmoor Road Raleigh NC 27613 h NC (CO, tact Person: Justin Ballard I Location/Site Name: Former Pro Cleaners SUBMIT FORM ON YELLOW PAPER ONLY or 27613 County Wake (7ip) 4MPLING INFORMATION 'ELL ID NUMBER (from Permit): MW-11A ell Depth: 105 ft. apth to Water Level 82546: 34.51 ft. below measuring point easuring Point is 0 ft. above land surface Aume of water pumped/bailed before sampling: 24 3117113les for metals were collected unfiltered: ❑ YES Te le phone#: 919-871-0999 No. of wells to be sampled: 20 DEPARTMENT OF ENVIRONMENT 8. NATURAL RESOURCES DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699.1617 Phone: 919-807-6306 PERMIT Number: Expiration Date: July 31, 2016 Non -Discharge WQ0035324 UIC NPDES Other TYPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field m Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: Date sample collected: 6/16/2015 Well Diameter: 2 in. Screened Interval: 100 ft. to 105 ft. Relative M.P. Elevation: 476.37 ft. a+Ienr minutes (to parameter stabilization) NO and field acidified: ❑ YES❑ NO FIELD ANALYSES: WAS DRY pH 00400: 5-97 units Temp. 00010: 27.24 oC at time of sampling, Spec. Cond. 00094: 35 PS/Cm' check Odor 000m: here: Appearance 0 ate sample analyzed: 6/19,22,23,24,25,26/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 kRAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 Not Detected mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Not Detected mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L AI - Aluminum 01105 mg/L Tetrachloroethene: 0.002 mg/L pH (Lab) 00403 units Be - Barium 01007 ug/L Trichloroethene: 0.00012J mg/L TOC 00680 Not Detected mg/L Ca - Calcium 00916 mg/L cis- 1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans-1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 >1200 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ll Yes (1) El No (0) Specific Conductance 00095 uMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH,as N;Ammonia Nitrogen, Total) Mn - Manganese 01055 590 ug/L Sulfate , method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 SyS{rea C. gAwli Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: , DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807-6306 FACILITY INFORMATION Please Print Clearly or type PERMIT Number: Expiration Date: July 31.2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery )shl�,) ¢'r" ❑ Spray Field 0 Remediation: Pump and Treat Fwc act Person: Justin Ballard Telephone#: 919-871-0999 El Rotary Distributor ❑ Land Application of Sludge Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: WELL ID NUMBER (from Permit): MW-11B Well Depth: 35 ft. Depth to Water Level 82546: 32.69 ft. below measuring point Measuring Point is 0 ft. above land surface Volume of water pumped/bailed before sampling: 1 Date sample collected: 6/16/2015 Well Diameter: 2 in. Screened Interval: 25 ft. to 35 Relative M.P. Elevation: 476.41 ft. allergy minutes (to parameter stabilization) NO and field acidified: ❑ YES E1 NO In FIELD ANALYSES: pH 00400: NA units Spec. Cond. 00094: NA Odor 00085: Appearance U WAS DRY Temp. 00010: NA °C at time of sampling, �1S/Cm2 check here: Date sample analyzed: 6/19,22,23,24,25,26/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 0.0022 J mg/L Pb - Lead olo51 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Not Detected mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L NA = Not analyzed due to lack of sufficient water. (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specry Compounds and Concentration nl s Dissolved Solids:Total 70300 mg/L Al -Aluminum oil o5 mg/L Tetrachloroethene: Not Detected pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: Not Detected TOC 00680 0.7 mg/L Ca - Calcium oo916 mg/L cis-1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 NA ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑� Yes (1) 10 No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH3 as N; Ammonia Nitrogen, Total) Mn - Manganese 01055 7700 ug/L Sulfate , method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 �.,ST..-I G . 9p(G'-h4Zj> Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 ROUNDWATER QUALITY MONITORING: OMPLIANCE REPORT FORM FACILITY INFORMATION Please Print Facility Name: Former Pro Cleaners Permit Name (if different): Facility Address: 8377 Creedmoor Road Raleigh NC 27613 Raleigh NC (C"y) Contact Person: Justin Ballard Well Location/Site Name: Former Pro Cleaners 27613 (zhn SAMPLING INFORMATION WELL ID NUMBER (from Permit): MW-12 Well Depth: 40 ft. Depth to Water Level 82546: 35.94 ft. below measuring point Measuring Point is 0 ft. above land surface Volume of water pumped/bailed before sampling: 1 or Type SUBMIT FORM ON YELLOW PAPER ONLY County Wake Te le p hone#: 919-871-0999 No. of wells to be sampled: 20 DEPARTMENT OF ENVIRONMENT 8 NATURAL RESOURCES DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 1617 MAIL SERVICE CENTER,..RALEIGH, NC 27699-1617 Phone: 919.807.6306 PERMIT Number: Expiration Date: July3t,2016 Non -Discharge W00035324 UIC NPDES Other TYPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field CO Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: Date sample collected: 6/17/2015 FIELD ANALYSES: Well Diameter: 2 in. pH 00400: 4.01 units Temp. 00010: 23.67 oC Screened Interval: 30 ft. to 40 ft. Spec. Cond. 00094: 25 ps/cm2 Relative M.P. Elevation: 480.12 ft. Odor 00085: minutes (insufficient recharge for purging) Appearance NO and field acidified: ❑ YES 173 NO If WELL WAS DRY at time of sampling, check here: 11 Date sample analyzed: 6119.22.23,24,25,26/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 0.0039J mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 0.32 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L NA = Not analyzed due to lack of sufficient water. (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum o11o5 mg/L Tetrachloroethene: 0.00077 mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichooroethene: Not Detected TOC 00680 0.37J mg/L Ca - Calcium 00916 mg/L cis- 1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans-1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 '1200 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 4.1 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ED Yes (1) i❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260B Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH, as N; Ammonia Nitrogen, Total) Mn -Manganese oloss 1000 ug/L Sulfate ASTM D516-90 ,method # TKN as N 00625 mg/L Ni - Nickel 01067 Ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 C . $A,-LA­e_� Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • • . DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: , • DIVISION OF WATER RESOURCES -INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919-807.6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: JuIY 31, 2016 Facility Name: Former Pro Cleaners Non -Discharge W00035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creed moor Road Raleigh NC 27613 TYPE ❑ OF PERMITTED OPERATION BEING MONITORED Lagoon ❑ Remediation: Infiltration Gallery Raleigh (Street) NC 27613 County Wake (C'M Sr,iel (eo) ❑ Spray Field © Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): MW-12 Date sample collected: 6/18/2015 FIELD ANALYSES: WAS DRY 40 Well Depth: ft. 2 Well Diameter: n. 3.66 21.03 pH ooaoo: units Temp. 00010: �C at time of sampling, Depth to Water Level 82546: 27.52 ft. below measuring point Screened Interval: 20 ft. to 40 ft. Spec. Cond. 00094: 37 PS/Cm, check Measuring Point is 0 ft. above land surface Relative M.P. Elevation: 477.62 ft. Odor 00085: here: Volume of water pumped/bailed before sampling: 22 4oRer&minutes (to parameter stabilization) Appearance ❑ Samples for metals were collected unfiltered: ElYES ElNO and field acidified: ElYES ❑ NO LABORATORY INFORMATION Date sample analyzed: 6/19,22,23,24,25,2612015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 0.0083J mg/L Pb - Lead o1o51 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 0.82 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L Tetrachloroethene: 0.0055 mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichooroethene: Not Detected TOC 00680 Not Detected mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans-1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total olo34 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 >1200 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑� Yes (1) ❑ No (0) Specific Conductance 00095 [Mhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH,as N:Ammonia Nitrogen, Total) Mn - Manganese 01055 300 ug/L Sulfate , method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 e- - b 1_(-AR;T> Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 ROUNDWATER QUALITY MONITORING: OMPLIANCE REPORT FORM Please Print Clearly or Type SUBMIT FORM ON YELLOW PAPER ONLY Facility Name: Former Pro Cleaners Permit Name (if different): Facility Address: 8377 Creedmoor Road Raleigh NC 27613 Raleigh NC 27613 County Wake (cry Contact Person: Justin Ballard Well Location/Site Name: Former Pro Cleaners (st.m) (z4» WELL ID NUMBER (from Permit): MW-24D Well Depth: B3 ft. Depth to Water Level 82546: 29.85 ft. below measuring point Measuring Point is 0 ft. above land surface Volume of water pumped/bailed before sampling: 11 Telephone#: 919-871-0999 No. of wells to be sampled: 20 Date sample collected: 6/15/2015 Well Diameter: 2 in. Screened Interval: 73 ft. to 83 Relative M.P. Elevation: 475.40 ft. gaueasminutes (to parameter stabilization) DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807.6306 PERMIT Number: Expiration Date: July31,2016 Non -Discharge WQ0035324 UIC NPDES Other TYPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field © Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: [a FIELD ANALYSES: pH 00400: 5.26 units Spec. Cond. 00094: 36 Odor 00085: Appearance WAS DRY Temp. 00010: 2412 oC at time of sampling, uS/Cm2 check here: LABORATORY INFORMATION Date sample analyzed: 6-16,17,18,19.22,23 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 0.0031J mg/L Pb - Lead o1o51 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Not Detected mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /10omL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L AI -Aluminum oilm mg/L Tetrachloroethene: 0.0012 mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichlorcethene: Not Detected TOC 00680 8.2 mg/L Ca - Calcium 00916 mg/L cis- 1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 >1200 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑7 Yes (1) ❑ No (0) Specific Conductance 00095 ttMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 Not Detected mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH, as N; Ammonia Nitrogen, Total) Mn -Manganese o1055 74 ug/L Sulfate ASTM D516-90 ,method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 <.. FAe`AQ_�p Permittee (or Authorized Agent) Name and Title - Please print or type Authorized Agent) 1/io (Date) GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • . DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: • , DIVISION OF WATER RESOURCES -INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807.6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July 31, 2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh s'r1111 NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery l7in> ❑ Spray Field ❑ Remediation: Pump and Treat rW--r111tLocatio'Cn`/`S'ite act Perso: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: ILL ID NUMBER (from Permit): MW-24S Date sample collected: 6/15/2015 FIELD ANALYSES: WAS DRY I Depth: 50 ft. Well Diameter: 2 in. pH 00400: 5.09 units Temp. 00010: 28.89 oC at time of sampling, th to Water Level 82546: 24.23 ft. below measuring point Screened Interval: 30 ft. to 50 ft. Spec. Cond. 00094: 30 ps/cm2 check Isuring Point is 0 ft. above land surface Relative M.P. Elevation: 475.48 ft. Odor 00085: here: Ime of water pumped/bailed before sampling: 9 jauePr_minutes (to parameter stabilization) Appearance iDles for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES I] NO ete sample analyzed: 6/16,17,18,19,22,23/2015 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 kRAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 0.0087 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 0.56 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Not Detected mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum o1105 mg/L Tetrachloroethene: 0.021 mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: Not Detected TOC 00680 Not Detected mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 '1200 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Not Detected mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑ Yes (1) ❑ No (0) Specific Conductance 00095 ItMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260B Total Ammonia 00610 0.29 mg/L Mg - Magnesium 00927 mg/L Total Organic Carbon method # EPA 5310C (Ammonia Nitrogen; NH, as N; Ammonia Nitrogen, Total) Mn - Manganese 01055 21 ug/L Sulfate , method # ASTM D516-90 TKN as N 00625 mg/L Ni - Nickel 01067 ug/L Ammonia, sulfide, nitrate, nitrite method # EPA 4500 For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 ROUNDWATER QUALITY MONITORING: OMPLIANCE REPORT FORM Facility Name: Former Pro Cleaners Permit Name (if different): Facility Address: 8377 Creedmoor Road Raleigh NC 27613 Raleigh Stroo1 NC (City) Contact Person: Justin Ballard Well Location/Site Name: Former Pro Cleaners 27613 (7t)) WELL ID NUMBER (from Permit): 8404 Azalea Place Well Depth: NA ft. Depth to Water Level 82546: NA ft. below measuring point Measuring Point is NA ft. above land surface Volume of water pumped/bailed before sampling: NA Samples for metals were collected unfiltered: m YES or SUBMIT FORM ON YELLOW PAPER ONLY County Wake Telephone#: 919-871-0999 No. of wells to be sampled: 20 DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807.6306 PERMIT Number: Expiration Date: July31,2016 Non -Discharge WQ0035324 UIC NPDES Other TYPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field © Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: Date sample collected: 6/15/2015 Well Diameter: NA in. Screened Interval: NA ft. to NA ft. Relative M.P. Elevation: NA ft. galleAs minutes NO and field acidified: ❑ YES 0 NO Date sample analyzed: 6n3115 Laboratory Name PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 pH (Lab) 00403 units Be - Barium 01007 TOC 00680 mg/L Ca - Calcium 00916 Chloride 00940 mg/L Cd - Cadmium 01027 Arsenic 01002 ug/L Chromium: Total 01034 Grease and Oils 00552 mg/L Cu - Copper 01042 Phenol 32730 ug/L Fe - Iron 01045 Sulfate 00945 mg/L Hg - Mercury 71900 Specific Conductance 000m ttMhos K - Potassium 00937 Total Ammonia 00610 mg/L Mg - Magnesium 00927 (Ammonia Nitrogen; NH,as N; Ammonia Nitrogen, Total) Mn -Manganese oloss TKN as N 00625 mg/L Ni - Nickel 01067 Con -test Analytical Laboratory FIELD ANALYSES: WAS DRY p 27 p at time of H ooaoo: units Temp. 00010: 19.3 °C sampling, Spec. Cond. 000sa: 75 )JS/Cm2 check Odor 00085: here: Appearance E] Certification No. 652 mg/L Pb - Lead o1o51 ug/L mg/L Zn - Zinc 01092 mg/L mg/L mg/L Other (Specify Compounds and Concentration Units): mg/L Tetrachloroethene: Not Detected ug/L Trichloroethene: Not Detected mg/L cis-1,2-Dichloroethene: Not Detected ug/L trans- 1,2-Dichloroethene: Not Detected ug/L Vinyl chloride: Not Detected mg/L ORGANICS: (by GC, GC/MS, HPLC) ug/L (Specify test and method #. ATTACH LAB REPORT.) ug/L Lab Report Attached? ED Yes (1) ❑ No (0) mg/L VOC 78732 method # EPA 8260B mg/L method # ug/L method # ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 f19 Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • . DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699.1617 Phone: 919-807-6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July 31, 2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery t7"'I ❑ Spray Field © Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: WELL ID NUMBER (from Permit): 8405 Azalea Place Date sample collected: 6/15/201E Well Depth: NA ft. Well Diameter: NA in. Depth to Water Level 82546: NA ft. below measuring point Screened Interval: NA ft. Measuring Point is NA ft. above land surface Relative M.P. Elevation: NA Volume of water pumped/bailed before sampling: NA 4da4eaTmlflUteS Samples for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES to NA ft. ft. ❑+ NO FIELD ANALYSES: pH 00400: 8 units Spec. Cond. 00094: 257 Odor 00085: Appearance Temp. 00010: 22.27 °C US/Cm2 WAS DRY at time of sampling, check here: LABORATORY INFORMATION Date sample analyzed: 6123115 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al - Aluminum 01105 mg/L Tetrachloroethene: Not Detected pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichlorcethene: 0.00041J mg/L TOC 00680 mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans-1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? El Yes (1) ❑ No (0) Specific Conductance o0095 FtMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260B Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH3as N; Ammonia Nitrogen, Total) Mn - Manganese 01055 ug/L , method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 :S-)L-gy l C . 5 Aft Pf> Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • • . DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807.6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July31,2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh INC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh so- cl NC 27613 County Wake Cl Lagoon ❑ Remediation: Infiltration Gallery c,Isiaml (zip) ❑ Spray Field © Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): 8409 Azalea Place Date sample collected: NA FIELD ANALYSES: WAS DRY Well Depth: NA ft. Well Diameter: NA in. pH 00400: NA units Temp. 00010: NA C at time of sampling, Depth to Water Level 82546: NA ft. below measuring point Screened Interval: NA ft. to NA ft. Spec. Cond. 00094: NA NS/Cm2 check Measuring Point is NA ft. above land surface Relative M.P. Elevation: NA ft. Odor 00085: here: Volume of water pumped/bailed before sampling: NA tdalleas.minutes Appearance Samples for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES ❑r NO LABORATORY INFORMATION Date sample analyzed: Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 Fri (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L Tetrachloroethene: pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: TOC 00680 mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Arsenic 01002 ug/L Chromium: Total o1o34 ug/L Vinyl chloride: Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 ri Hg - Mercury 71900 ug/L Lab Report Attached? ❑ Yes (1) ❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH,as N;Ammonia Nitrogen, Total) Mn -Manganese 01055 ug/L ,method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal°/ 100 75-61,il C. �ALti►C� Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • • DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: • • , DIVISION OF WATER RESOURCES -INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807-6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July31,2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh S1r tl NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery �Dt , Is,.9.F, (Zv ❑ Spray Field Q Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): 8409 Azalea Place Date sample collected: NA FIELD ANALYSES: WAS DRY Well Depth: NA ft. Well Diameter: NA in. pH ooaoo: NA units Temp. 00010: NA oC at time of sampling, Depth to Water Level 82546: NA ft. below measuring point Screened Interval: NA ft. to NA ft. Spec. Cond. 00094: NA PS/Cm, check Measuring Point is NA ft. above land surface Relative M.P. Elevation: NA ft. Odor 00085: here. Volume of water pumped/bailed before sampling: NA t,alleas-minutes Appearance Samples for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES ❑� NO LABORATORY INFORMATION Date sample analyzed: 6/23/15 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L 'Owner does not want well to be sampled by ATC. pH (Lab) 00403 units Ba - Barium 01007 ug/L TOC 00680 mg/L Ca - Calcium 00916 mg/L Chloride 00940 mg/L Cd - Cadmium 01027 ug/L Arsenic 01002 ug/L Chromium: Total 01034 ug/L Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑ Yes (1) ❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH3as N;Ammonia Nitrogen, Total) Mn - Manganese 01055 ug/L , method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0,08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • . . DEPARTMENT OF ENVIRONMENT 8 NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: NLj . DIVISION OF WATER RESOURCES -INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807-6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July 31, 2016 Facility Name: Former Pro Cleaners Non -Discharge W00035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery (7,) Spray Field Q Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: L ID NUMBER (from Permit): 8401 Camellia Drive Depth: 111 ft. h to Water Level 82546: NA ft. below measuring point curing Point is NA ft. above land surface ne of water pumped/bailed before sampling: NA Y Date sample collected: 6/15/2015 Well Diameter: NA in. Screened Interval: NA ft. Relative M.P. Elevation: NA laAeasminutes NO and field acidified: ❑ YES to NA ft. ft. IM►Ce7 FIELD ANALYSES: pH 00400: 6.22 units Spec. Cond. 00094: 275 Odor 00085: Appearance WAS DRY Temp. 000lo: 19.93 oC at time of sampling, us/Cm2 check LABORATORY INFORMATION Date sample analyzed: 6t23115 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L Tetrachloroethene: Not Detected pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: Not Detected TOC 00680 mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: Not Detected Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑� Yes (1) ❑ No (0) Specific Conductance 00095 [Mhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH3 as N; Ammonia Nitrogen, Total) Mn - Manganese 01055 ug/L , method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOIDS: 0 mg/L VOC Removal% 100 Q-a,0A c . '&A"AZ-V> Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • • . DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: , • , DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699.1617 Phone: 919.807.6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July 31, 2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery cy� mi,,I znl ❑ Spray Field © Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): 8404 Camellia Drive Date sample collected: 6/15/2015 FIELD ANALYSES: WAS DRY Well Depth: NA ft. Well Diameter: NA in. pH 00400: 6.5 units Temp. 00010: 20.74 oC at time of sampling, Depth to Water Level ersas: NA ft. below measuring point Screened Interval: NA ft. to NA ft. Spec. Cond. 000sa: 75 Ns/cm2 check Measuring Point is NA ft. above land surface Relative M.P. Elevation: NA ft. Odor 00085: here: Volume of water pumped/bailed before sampling: NA minutes Appearance ❑ Samples for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES ❑ NO LABORATORY INFORMATION Date sample analyzed: 6/23/15 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead o1o51 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al - Aluminum 01105 mg/L Tetrachloroethene: Not Detected pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: 0.0023 mg/L TOC 00680 mg/L Ca - Calcium 00916 mg/L cis- 1,2-Dichloroethene: 0.008 mg/L Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans-1,2-Dichloroethene: 0.00031J mg/L Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? El Yes (1) ❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH,as N;Ammonia Nitrogen, Total) Mn - Manganese 01055 ug/L , method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY DEPARTMENT OF ENVIRONMENT 8 NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: , DIVISION OF WATER RESOURCES -INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807-6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July31,2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery (CRY) izpl ❑ Spray Field 0 Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): 8405 Camellia Drive Date sample collected: 6/15/2015 FIELD ANALYSES: WAS DRY NA Well Depth: ft. NA Well Diameter: in. 6.21 20.43 pH ooaoo: units Temp. 000lo: oC at time of sampling, Depth to Water Level 82546: NA ft. below measuring point Screened Interval: NA ft. to NA ft. Spec. Cond. 00094: 146 ).tS/Cm2 check Measuring Point is NA ft. above land surface Relative M.P. Elevation: NA ft. Odor 00085: here: Volume of water pumped/bailed before sampling: NA minutes Appearance 1-1 Sam les for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES ❑ NO LABORATORY INFORMATION Date sample analyzed: 6t23115 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L AI -Aluminum oilo5 mg/L Tetrachloroethene: Not Detected pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: Not Detected TOC 00680 mg/L Ca - Calcium oo916 mg/L cis- 1,2-Dichloroethene: 0.00033J mg/L Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans- 1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑e Yes (1) ❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH,as N;Ammonia Nitrogen, Total) Mn - Manganese o1o55 ug/L , method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • • . DEPARTMENT OF ENVIRONMENT 8 NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: • , , DIVISION OF WATER RESOURCES -INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, INC 27699-1617 Phone: 919.807.6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July 31. 2ote Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC NPDES Other Permit Name (if different): Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE ❑ OF PERMITTED OPERATION BEING MONITORED Lagoon ❑ Remediation: Infiltration Gallery Raleigh NC 27613 County Wake (C"v' (Z"') ❑ Spray Field © Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): 8408 Camellia Drive Date sample collected: 6/15/2015 FIELD ANALYSES: WAS DRY Well Depth: NA ft. Well Diameter: NA in. pH 00400: 7.05 units Temp. 00010: 22.96 oC at time of sampling, Depth to Water Level 82546: NA ft. below measuring point Screened Interval: NA ft. to NA ft. Spec. Cond. 00094: 259 PS/Cm2 check Measuring Point is NA ft. above land surface Relative M.P. Elevation: NA ft. Odor 00085: here: Volume of water pumped/bailed before sampling: NA �alleasminuteS Appearance Samples for metals were collected unfiltered: m YES ❑ NO and field acidified: ❑ YES ❑ NO LABORATORY INFORMATION Date sample analyzed: 6/23115 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /1 OOmL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L Tetrachloroethene: Not Detected pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: 0.00061J mg/L TOC oomo mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: 0.0032 mg/L Chloride 00940 mg/L Cd - Cadmium 01027 ug/L trans-1,2-Dichloroethene: Not Detected Arsenic 01002 ug/L Chromium: Total 01034 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 Fri Hg - Mercury 71900 ug/L Lab Report Attached? ❑� Yes (1) ❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH3 as N; Ammonia Nitrogen, Total) Mn- Manganese o1o55 ug/L , method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • . . DEPARTMENT OF ENVIRONMENT & NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919.807-6306 FACILITY INFORMATION Please Print Clearly or Type PERMIT Number: Expiration Date: July 31, 2016 Facility Name: Former Pro Cleaners Non -Discharge WQ0035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED RaleighNC 27613 CountyWake 11 Lagoon ❑ Remediation: Infiltration Gallery 01v 07a, 17,) ❑ Spray Field 10 Remediation: Pump and Treat Contact Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Well Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: SAMPLING INFORMATION If WELL WELL ID NUMBER (from Permit): 8409 Camellia Drive Date sample collected: 6/15/2015 FIELD ANALYSES: WAS DRY Well Depth: NA ft. Well Diameter: NA in. pH 00400: 6.54 units Temp. 00010: 20.67 oC at time of sampling, Depth to Water Level 82546: NA ft. below measuring340 point Screened Interval: NA ft. to NA ft. Spec. Cond. 000sa: )JS/Cm 2 check Measuring Point is NA ft. above land surface Relative M.P. Elevation: NA ft. Odor 00085: here: Volume of water pumped/bailed before sampling: NA 4auerminutes Appearance Samples for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES r❑ NO LABORATORY INFORMATION Date sample analyzed: 6/23/15 Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 11001 Nitrate (Ni as N 00620 mg/L Zn - Zinc 01092 ni Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPNmethod for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L AI -Aluminum 01105 mg/L Tetrachloroethene: Not Detected pH (Lab) 00403 units Ba - Barium 01007 ug/L Trichloroethene: 0.00021 ri TOC 00680 mg/L Ca - Calcium 00916 mg/L cis-1,2-Dichloroethene: 0.00088J mg/L Chloride 00940 mg/L Cd - Cadmium 01027 1 trans- l,2-Dichloroethene: Not Detected Arsenic 01002 1 Chromium: Total o1o34 ug/L Vinyl chloride: Not Detected Grease and Oils 00552 ni Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 1 Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑� Yes (1) ❑ No (0) Specific Conductance 00095 µMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260E Total Ammonia 00610 mg/L Mg - Magnesium 00927 ni method # (Ammonia Nitrogen; NH, as N; Ammonia Nitrogen, Total) Mn -Manganese 01055 ug/L ,method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCS: 0 mq/L VOC Removal% 100 Permittee (or Authorized Agent) Name and Title - Please print or type GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY • . . DEPARTMENT OF ENVIRONMENT 8 NATURAL RESOURCES GROUNDWATER QUALITY MONITORING: , , DIVISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT COMPLIANCE REPORT FORM 1617 MAIL SERVICE CENTER, RALEIGH, NC 27699-1617 Phone: 919-807-6306 FACILITY INFORMATION Pease Print Cleary or Type PERMIT Number: Expiration Date: July31,2016 Facility Name: Former Pro Cleaners Non -Discharge W00035324 UIC Permit Name (if different): NPDES Other Facility Address: 8377 Creedmoor Road Raleigh NC 27613 TYPE OF PERMITTED OPERATION BEING MONITORED Raleigh s« , NC 27613 County Wake ❑ Lagoon ❑ Remediation: Infiltration Gallery cry, s��:„ z,�„ ❑ Spray Field © Remediation: Pump and Treat Fwc'e act Person: Justin Ballard Telephone#: 919-871-0999 ❑ Rotary Distributor ❑ Land Application of Sludge Location/Site Name: Former Pro Cleaners No. of wells to be sampled: 20 ❑ Water Source Heat Pump ❑ Other: L ID NUMBER (from Permit): 8412 Camellia Drive Depth: NA ft. h to Water Level 82546: NA ft. below measuring point curing Point is NA ft. above land surface ne of water pumped/bailed before sampling: NA oles for metals were collected unfiltered: 0 YES Date sample collected: NA Well Diameter: NA Screened Interval: NA Relative M.P. Elevation: NA minutes Date sample analyzed: NA Laboratory Name PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 Dissolved Solids:Total 70300 mg/L AI -Aluminum 01105 pH (Lab) 00403 units Ba - Barium 01007 TOC 00680 mg/L Ca - Calcium 00916 Chloride 00940 mg/L Cd - Cadmium 01027 Arsenic 01002 ug/L Chromium: Total 01034 Grease and Oils 00552 mg/L Cu - Copper 01042 Phenol 32730 ug/L Fe - Iron 01045 Sulfate 00945 mg/L Hg - Mercury 71900 Specific Conductance 00095 µMhos K - Potassium 00937 Total Ammonia 00610 mg/L Mg - Magnesium 00927 (Ammonia Nitrogen; NH3as N;Ammonia Nitrogen, Total) Mn -Manganese 01055 TKN as N 00625 mg/L Ni - Nickel 01067 in. ft. to NA ft. ft. Ir Con -test Analytical Laboratory If WELL FIELD ANALYSES: WAS DRY pH 0040o: NA units Temp. 00010: NA oC at time of sampling, Spec. Cond. 00094: NA NS/Cm2 check Odor 00085: here: Appearance 0 Certification No. 652 mg/L Pb - Lead o1o51 ug/L mg/L Zn - Zinc 01092 mg/L mg/L mg/L Other (Specify Compounds and Concentration Units): mg/L ug/L mg/L ug/L ug/L mg/L ORGANICS: (by GC, GC/MS, HPLC) ug/L (Specify test and method #. ATTACH LAB REPORT.) ug/L Lab Report Attached? ❑ Yes (1) ❑ No (0) mg/L VOC 78732 method # EPA 8260E mg/L method # ug/L method # ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 G1 J �/ N L L7iQ Permittee (or Authorized Agent) Name and Title - Please print or type ar/IQ (Date) GW-59 Rev.8/2013 SUBMIT FORM ON YELLOW PAPER ONLY GROUNDWATER QUALITY MONITORING: COMPLIANCE REPORT FORM ikC I LITY INFORMATION Please Print Clearly or Type acility Name: Former Pro Cleaners ermit Name (if different): 3cilityAddress: 8377 Creedmoor Road Raleigh NC 27613 Raleigh NC 27613 County Wake ra1, tact Person: Justin Ballard I Location/Site Name: Former Pro Cleaners rsmi�e (Z,jp; Telephone#: 919-871-0999 No. of wells to be sampled: 20 'ELL ID NUMBER (from Permit): 8413 Camellia Drive Date sample collected: NA ell Depth: NA ft. Well Diameter: NA apth to Water Level 82546: NA ft. below measuring point Screened Interval: NA easuring Point is NA ft. above land surface Relative M.P. Elevation: NA 31ume of water pumped/bailed before sampling: NA ja49FI&minutes am les for metals were collected unfiltered: ❑ YES ❑ NO and field acidified: ❑ YES in. ft. to NA ft. ft. R _PARTMENT OF ENVIRONMENT & NATURAL RESOURCES VISION OF WATER RESOURCES - INFORMATION PROCESSING UNIT 17 MAIL SERVICE CENTER, RALEIGH, INC 27699-1617 Phone: 919.807.6306 ERMIT Number: Expiration Date: July31.2016 on -Discharge WQ0035324 UIC PDES Other YPE OF PERMITTED OPERATION BEING MONITORED ❑ Lagoon ❑ Remediation: Infiltration Gallery ❑ Spray Field © Remediation: Pump and Treat ❑ Rotary Distributor ❑ Land Application of Sludge ❑ Water Source Heat Pump ❑ Other: FIELD ANALYSES: WAS DRY pH 00400: NA units Temp. 00010: NA C at time of sampling, Spec. Cond. 00094: NA NS/Cm2 check Odor 00085: here: Appearance a LABORATORY INFORMATION Date sample analyzed: NA Laboratory Name: Con -test Analytical Laboratory Certification No. 652 PARAMETERS NOTE: Values should reflect dissolved and colloidal concentrations. COD 00335 mg/L Nitrite (NO2) as N 00615 mg/L Pb - Lead 01051 ug/L Coliform: MF Fecal 31616 /100mL Nitrate (NO3) as N 00620 mg/L Zn - Zinc 01092 mg/L Coliform: MF Total 31504 /100mL Phosphorus: Total as P 00665 mg/L (Note: Use MPN method for highly turbid samples) Orthophosphate 70507 mg/L Other (Specify Compounds and Concentration Units): Dissolved Solids:Total 70300 mg/L Al -Aluminum 01105 mg/L pH (Lab) 00403 units Ba - Barium 01007 ug/L TOC 00680 mg/L Ca - Calcium 00916 mg/L Chloride 00940 mg/L Cd - Cadmium 01027 ug/L Arsenic 01002 ug/L Chromium: Total 01034 ug/L Grease and Oils 00552 mg/L Cu - Copper 01042 mg/L ORGANICS: (by GC, GC/MS, HPLC) Phenol 32730 ug/L Fe - Iron 01045 ug/L (Specify test and method #. ATTACH LAB REPORT.) Sulfate 00945 mg/L Hg - Mercury 71900 ug/L Lab Report Attached? ❑� Yes (1) ❑ No (0) Specific Conductance 00095 ttMhos K - Potassium 00937 mg/L VOC 78732 method # EPA 8260B Total Ammonia 00610 mg/L Mg - Magnesium 00927 mg/L method # (Ammonia Nitrogen; NH, as N; Ammonia Nitrogen, Total) Mn - Manganese 01055 ug/L , method # TKN as N 00625 mg/L Ni - Nickel 01067 ug/L method # For Remediation Systems Only (Attach Lab Reports): Influent Total VOCs: 0.08532 mg/L Effluent Total VOCs: 0 mg/L VOC Removal% 100 I- S Permittee (or Authorized Agent) Name and Title - Please print or type GW-59A Question #5 MW-5: PCE - 6/16/2015 (0.0035), 3/19/2015 (0.0025), 12/18/2014 (0.0036), 9/25/2014 (0.0022), 6/18/14 (0.0012), 3/27/2014 (0.0014), 12/11/2013 (0.0033), 09/10/2013 (0.0041), 05/30/2013 (0.0026) MW-10B: PCE - 6/18/2015 (0.11), 3/19/2015 (0.11), 12/18/2014 (0.18), 9/25/2014 (0.17), 6/18/14 (0.15), 3/27/2014 (0.19), 12/13/2013 (0.11), 09/12/2013 (0.046), 05/31/2013 (0.039) MW-11A: PCE - 6/18/2015 (0.002), 3/18/2015 (0.00086), 12/16/2014 (0.0012), (9/23/2014 (0.0033), 6/18/14 (0.0015), 3/26/2014 (0.00096), 09/12/2013 (0.0014), 05/29/2013 (0.0033), 02/27/2013 (0.0027) MW-12: PCE - 6/17/2015 (0.00077), 3/20/2015 (0.00074) MW-16: PCE - 6/18/2015 (0.0055), 3/19/2015 (0.0044), 12/18/2014 (0.0043), 9/25/2014 (0.0041), 6/18/14 (0.0019), 3/26/2014 (0.0024), 12/11/2013 (0.011), 09/10/2013 (0.0063), 05/30/2013 (0.0066) MW-24S: PCE - 6/15/2015 (0.021), 3/17/2015 (0.030), 12/17/2014 (0.038), 9/23/2014 (0.0.32), 6/16/14 (0.0099), 3/24/2014 (0.043), 12/10/2013 (0.0077), 09/10/2013 (0.004), 05/29/2013 (0.007), 02/25/2013 (0.008) MW-24D: PCE - 6/15/2015 (0.0012), 3/18/2015 (0.00090), 12/17/2014 (0.00078), 9/23/2014 (0.0.00087), 12/10/2013 (0.0014), 09/10/2013 (0.0021), 05/29/2013 (0.0016), 02/27/2013 (0.0015) EW-8 (IW-8): PCE - 3/20/2015 (0.24), 12/18/14 (0.26), 9/25/2014 (0.29), 6/20/14 (0.28), 3/27/2014 (0.43), 12/11/2013 (0.47), 09/11/2013 (0.18), 05/30/2013 (0.093), 02/28/2013 (0.12), 11/30/12 (0.081); TCE - 9/25/2014 (0.0032J), 6/18/14 (0.0.0033J), 3/27/2014 (0.0040) EW-9 (IW-9): PCE - 6/17/2015 (0.22), 12/18/2014 (0.2), 9/25/2014 (0.17), 3/27/2014 (0.32), 12/12/2013 (0.29), 09/11/2013 (0.087), 05/30/2013 (0.28), 02/28/2013 (0.31), 12/03/12 (0.31);TCE - 3/27/2014 (0.0038), 02/28/2013 (0.0047), 12/03/12 (0.0052); TCE - 6/17/2015 (0.004), 12/18/2014 (0.0042), 3/27/2014 (0.0038) Former Pro Cleaners Permit No. WQ0035324 APPENDIX C ANALYTICAL DATA TABLES August 10, 2015 Page 5 Table of Contents 1 DSCA 11) No.: 920001 Table/ Description Check box Att. No. if included Tables Table 1 Site Chronology p Table 2 Analytical Data for Soil ❑ Table 3 Analytical Data for Sub -slab Gas ❑ Table 4 Analytical Data for Soil Gas ❑ Table 5 Analytical Data for Indoor and Outdoor Air ❑ Table 6 Monitoring Well Construction Data O Table 7 Groundwater Elevation Data p Table 8 Analytical Data for Groundwater El Table 9 Analytical Data for Surface Water ❑ Table 10 Water Wells Survey Data p Table 11 Analytical Data for Water Supply Well(s) 0 Table 12 Analytical Data for Natural Attenuation Parameters CJ Attachments Aft. 1 Site map showing location(s) of soil boring(s). ❑ Soil contaminant concentration maps showing the concentration at each sampling Aft. 2 point. ❑ Aft. 3 Soil isoconcentration maps. ❑ Aft. 4 Site map showing location(s) of monitoring wells . p Aft. 5 Well completion diagrams and records of construction submitted to state. ❑ Aft. 6 Groundwater gradient map for each sampling event. p PCE concentration map showing the concentration at each sampling point and isoconcentration map. However, if there are significant plumes for other dry- Aft. 7 cleaning contaminants, contaminant concentration maps for each chemical of p concern should be included. Att. 8 Groundwater concentration trend plots. p Att. 9 Map showing locations of surface water sample(s) (if applicable). ❑ Surface water concentration map showing the concentration at each sampling Att. 10 point (if applicable). ❑ USGS Quad map with plotted water well location(s) within the 1,500 foot and 0.5 Att. 11 mile radii of the site (if applicable). Att. 12 Site map showing location(s) of monitoring well(s) for natural attenuation paramet, ❑ Att. 13 Site map showing location(s) of indoor air, outdoor air, or soil gas samples. ❑ Att. 14 Air and soil gas concentration map showing the concentration at each sampling oint. ❑ Signed laboratory analytical reports including chain -of custody and quality Att.15 assurance/quality control (QA/QC) documentation (only if not previously submitted). Att. 16 ❑ Att. 17 ❑ Att. 18 ❑ Att. 19 ❑ Att. 20 ❑ Att. 21 ❑ Note: 1. All maps must include a bar scale, north arrow, site name, DSCA ID No., and date. Table 1: Site Chronology DSCA II) No.: 920001 Chronolo2v of Events Instructions: Brief description of all significant events that have occurred since a problem was Date suspected at the facility. Commence with the first date a problem was suspected and continue through the most recent activity described in the current report. Late 1994 or Early 1995 (report not A Phase I Environmental Site Assessment (ESA) was prepared by Smith Environmental Technologies (Smith). This provided) ESA identified Pro -Cleaners as a potential environmental concern. A Phase 11 ESA was prepared by Smith. Three 2-inch monitoring wells (MW-1, MW-2, & MW-3) were installed at the site and three hand auger borings (CS-01, CS-02, & CS-03) were advanced within the the former dry-cleaning location. Groundwater samples collected from MW-1 (located along the western wall of the building) indicated June 1995 tetrachloroethylene (PCE) and trichloroethylene (TCE) at concentrations of 1,000 ppb and 24 ppb, respectively. The average depth -to -groundwater was documented to be —29 feet bgs. PCE was detected in each of the soil borings (advanced to 3 feet with samples collected from I foot bgs and at 3 feet bgs) at concentrations ranging from 240 ppb to 21 b. An ESA was prepared by Southeastern Environmental Services, Inc. (SES). The field assessment included the installation of four monitoring wells (MW-4 through MW-7), collection/analysis of shelby tube samples, and the collection/analysis of groundwater samples. The four wells were installed to varying depths ranging from 68.5 feet bgs (MW-5) to 70 feet bgs (MW-4, MW-6, & MW-7). Shelby tube samples were collected during the installation of MW-7 at depths of 29.5-31.5 feet bgs and 37.5-39.5 bgs and analyzed for vertical and horizontal hydraulic conductivity. The analysis revealed horizontal and vertical hydraulic conductivities of 0.000091 cm/sec and 0.000018 cm/sec, respectively, December 1995 in the sample collected from above the water table; the analysis also revealed horizontal and vertical hydraulic contductivities of 0.000017 cm/sec and 0.0000079 cm/sec, respectively, in the sample collected from below the water table. Groundwater samples were also collected from five monitoring wells (MW-1 and MW4 through MW-7) at the site. PCE was detected in MW-1 at a concentration of 3410 ppb; PCE was detected in MW4 at a concentration of 204 ppb; and, PCE was detected in MW-5, MW-6, MW-7 at concentrations ranging from 28 ppb to 11 ppb. Groundwater was also identified as a source for drinking water in the area of the site; a water supply well was identified approximately )150 feet north of the site An ESA Addendum and Remedial Action Plan were prepared by SES and Walton Engineering ( Walton). Two additional monitoring wells were installed at the site; MW-8 was installed to a depth of 83 feet bgs and MW-9 was installed to a depth of 63 feet bgs. Groundwater samples were collected from eight monitoring wells at the site. PCE was detected in the samples collected from MW-1 (2895 ppb), MW-4 (663 ppb), and MW-8 (142 ppb). Samples collected from MW-3, MW-5, M W-6 MW-7, and MW-9 did not contain PCE. Samples collected from MW-I and MW- July 1996 4 included breakdown chlorinated compounds (TCE and cis-1,2-dichloroet)lene [cis-1,2-DCE]). Water samples were collected from three water supply wells; chlorinated solvents were not detected in these samples. The Remedial Action Plan of this report discusses the implentation of several remedial technologies. The report concludes that the most effective remediation technology for the site would be a combination of air sparging with vapor extraction. Design schematics and operation and maintanence schedules were provided. The system became was installed and became ggerational on June 7 6 A Site Assessment Addendum was prepared by SES and Walton. Four additional monitoring wells were installed on the north side of Strickland Road. Monitoring well MW-l0A was installed to a depth of 80 feet bgs; monitoring well MW- 10B was installed at a depth of 45 feet bgs; MW-11A was installed to a depth of 104 feet bgs; and MW-1113 was installed to a depth of 35 feet bgs. PCE was detected in groundwater samples collected from MW-1 (1744 ppb), MW4 February 1997 (260 ppb), MW-5 (8.6 ppb), MW-7 (8.7 ppb), MW-8 (347 ppb), and MW-9 (2.2 ppb). Samples collected from MW-I, MW4, and MW-8 included breakdown chlorinated compounds (TCE and cis-1,2-DCE). Chlorinated compounds were not detected in MW-3, MW-6, MW-10A, MW-IOB, MW-11A, MW-1113, or the three residential water supply wells sampled during this event. SES and Walton stated that the remediation system appeared to be reducing the solvent concentrations in the so a area. A Site Assessment and Corrective Action Plan Addendum were prepared by SES and Walton. Six additional monitoring wells (two were temporary and abandoned) were installed at the site. Monitoring well MW-8A was installed to a depth of 151 feet bgs. Monitoring wells MW-12, MW-13, NM-14 (abandoned), MW-15 (abandoned), and MW-16 were installed to a depth of 40 feet. Laboratory analysis of groundwater samples revealed the presence of PCE in MW-1 (3380 ppb), MW4 (50.6 ppb), MW-5 (4.4 ppb), MW-7 (1.9 ppb), MW-8 (194 ppb), MW-8A (271 ppb), MW-9 (2.4 April 1997 ppb), MW-14 (10 ppb), MW-15 (29.6 ppb) and MW-16 (43.0 ppb). Breakdown chlorinated compounds were also detected in MW-I, MW-8, MW-8A, and MW-15. Chlorinated solvents were not detected in MW-3, MW-10A, MW- IOB, MW-1 ] A, MW-1113, MW-13, or the three residential water supply wells sampled during this event. Chlorinated compounds were not detected in the soil samples collected during the installation of MW-12, MW-13, and MW-14 from 20 feet bgs. Slug testing at the site during this assessment indicated an average hydraulic conductivity of 0.00067 cm/sec in the intermediate zones and 0.000425 in the deep zone. Two additional air sparge wells were constructed north Page 5 of 127 Table 1: Site Chronology DSCA ID No.: 920001 it - Chronology of Events Instructions: Brief description of all significant events that have occurred since a problem was Date suspected at the facility. Commence with the first date a problem was suspected and continue through the most recent activity described in the current report. A Final Corrective Action Plan Addendum was prepared by SES and Walton. This addendum was prepared to address September 1997 concerns of the NCDENR regarding the off -site migration of the plume to the southwest and other various technical and administrative issues. A Groundwater Monitoring Report was prepared by SES and Walton. Monitoring well MW-17 was sampled for the first time during this sampling event, however a discussion regarding the installation was not provided. Groundwater samples were collected from 18 monitoring wells and three water supply wells. Concentrations of chlorinated March 1998 compounds increased drastically in samples collected from MW-1. No significant changes in contaminant concentrations were observed in samples collected from MW-4 or noted for the remainder of the monitoring wells or water supply wells. It was noted in this report that Pro -Cleaners moved to another tenant space within Towne North ShoDDin2 Center anddry-cleaning o erations ceased on the property. An Active Remediation Groundwater Monitoring Report was prepared by SES and Walton. Groundwater samples were June 1998 collected from 18 monitoring wells, three water supply wells, and one private utility supply well. Concentrations of chlorinated compounds continued to show increasing values in MW-1. Additionally, samples collected from MW-8, MW-8A and MW-l0A also showed increased concentrations of chlorinated compounds. An Active Remediation Groundwater Monitoring Report was prepared by SES and Walton. Groundwater samples were January 1999 collected from 15 monitoring wells and three private water supply wells. The results revealed a decrease in concentration of chlorinated compounds from the previous sampling event. An Assessment Addendum and Active Remediation Groundwater Monitoring Report was prepared by SES and Walton. Thee temporary monitoring wells were installed (MW-18, MW-19, and MW-20). Monitoring well MW-18 was April 1999 abandoned based on the analytical data; wells MW-19 and MW-20 were made permanent. Groundwater samples were collected from 18 monitoring wells and three water supply wells. The plume geometry remained unchanged and volatile organic compounds (VOCs) were not detected in the samples collected from the three water supply wells. An Active Remediation Groundwater Monitoring Report was prepared by SES and Walton. Groundwater samples were August 1999 collected from 15 monitoring wells and three private water supply wells. The results indicated an unchanged plume geometry and increase in concentrations in samples collected from monitoring wells MW-lOB and MW-1113; VOCs were not detected in the samples collected from the three water supply wells. An Active Remediation Groundwater Monitoring Report was prepared by SES and Walton. Groundwater samples were December 1999 collected from 15 monitoring wells and three water supply wells. The results indicated a narrowing of the groundwater plume and unstable concentrations in samples collected from MW-1 OB and MW-1 1 B; VOCs were not detected in the samples collected from the three water sui)i)lv wells. An Active Remediation Groundwater Monitoring Report was prepared by SES and Walton. Groundwater samples were collected from 15 monitoring wells and three water supply wells. The results indicated stable plume geometry and May 2000 concentrations from the samples were generally consistant with the previous sampling event. The sample from the water supply well located at 8401 Azalea contained a low concentration (1.16 ppb) of 1,2,4-trimethyl benzene. No other VOCs were detected in the sam les collected from the three water supply wells. An Active Remediation Groundwater Monitoring Report was prepared by SES and Walton. Groundwater samples were October 2000 collected from 15 monitoring wells and three water supply wells. The results indicated stable plume geometry and concentrations from the samples were either decreased or stable; VOCs were not detected in the samples collected from the three water supply wells. An Active Remediation and Groundwater Monitoring Report was prepared by SES and Walton. Groundwater samples April 2001 were collected from 17 monitoring wells and three water supply wells. The results indicated stable plume geometry and contaminant concentrations; VOCs were not detected in the samples collected from the three water supply wells. Au ist 2001 Northridge Partners filed a Petition for Certification of the site into the DSCA Program. October 2001 The air spargelsoil vapor extraction system was taken out of service. December 2001 The site was certified into the DSCA program. A Groundwater Monitoring Report was prepared by MACTEC Engineering and Consulting, Inc. (MACTEC). Groundwater samples were collected from ten monitoring wells and three water supply wells. The results indicated October 2001 stable plume geometry and varying (increasing to the south-southwest and decreasing in the source and north of the source area) concentrations of VOCs. TCE and cis-1,2-DCE were detected in the sample collected from the water supply well located at 8400 Camellia Drive; VOCs were not detected in the samples collected from the other water supply wells. December 2004 An Administrative Agreement for State -Directed Assessment and Remediation under the DSCA Program was executed. Page 6 of 127 Table l: Site Chronology DSCA 11) No.: 920001 IL ChronologN of Events Instructions: Brief description of all significant events that have occurred since a problem was Date suspected at the facility. Commence with the first date a problem was suspected and continue through the most recent activity described in the current report. A Groundwater Monitoring Report was prepared by MACTEC. Groundwater samples were collected from 16 April 2005 monitoring wells and three water supply wells. The results indicated stable plume geometry and varying concentations in samples collected from the monitoring wells. Contaminant concentrations increased in the sample collected from 8400 Camellia Drive the remaining two water supply wells did not contain VOCs. A Report of Water Supply Well Sampling Event was prepared by Engineering Consulting Services, Ltd. (ECS). July 2005 Groundwater samples were collected from ten water supply wells. No chlorinated compounds were detected in the samples collected. October 2005 Towne North Shopping Center, LLC purchased the Towne North Shopping Center property and became a DSCA etitioner. A Report of Soil Assessment and Groundwater Monitoring was prepared by MACTEC. Soil samples were collected from soil borings S-1 through S-16 and from the boring associated with the installation of MW-ld; the soil samples were collected from varying depths. The results indicated high concentrations of PCE in soil outside the building in the area of the rear door and along the sewer and water lines near the rear of the facility. One Type -II monitoring well (MW-21) April 2006 was installed to replace MW-20; one Type -III monitoring well (MW-1d) was installed immediately downgradient of the source area. Monitoring wells MW-6 and MW-20 were abandoned. Groundwater samples were collected from 12 monitoring wells and 18 water supply wells. The results indicated stable plume geometry and generally increasing contaminant concentrations. The sample collected from the water supply well located at 8400 Camellia Drive contained TCE and cis-1,2-DCE. The sample collected from the water supply well at 8404 Camellia Drive contained cis-1,2-DCE. No other samples contained chlorinated solvent compounds. A Report of Groundwater Monitoring was preapared by MACTEC. Groundwater samples were collected from 11 October 2006 monitoring wells and four water supply wells. The results indicated generally increasing contaminant concentrations in the monitoring wells and the water supply well located at 8400 Camellia Drive. The remaining three water supply wells sampled did not contain chlorinated solvent compounds. June 2007 Towne North, LLC purchased the Towne North Shopping Center property. June 2007 A Building Exterior Assessment was conducted by MACTEC. The report indicates that MACTEC was unable to detect anv new distresses to the exterior of the facility after the excavation which is discussed below. A Letter Report of Environmental Services was prepared by MACTEC. A soil excavation was conducted in June of 2007. A total of 90.59 tons of soil were excavated from the site. Two soil samples (B-1 & B-2) were collected from the July 2007 base of the excavation. Sample B-2 contained 0.0087 ppm of PCE based on laboratory analysis; sample B-1 did not contain PCE above a concentration of 0.0011 ppm. The soil was transported to and disposed at Wayne Disposal, Inc. in Belleville Michigan. A Water Supply Well Abandonment Report was prepared by ATC. Water supply wells were abandoned in accordance November 2007 with applicable rules at 8400 Camellia Drive, 8401 Azalea Drive, and 8400 Azalea Drive. These residences had been vreviouslv connected to City of Raleigh public water. ATC collected groundwater samples from seven monitoring wells and 17 water supply wells. PCE was detected above December 2007 2L Standards in samples collected from monitoring wells MW-8B and MW-l6. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, 8408, and 8405 Camellia Drive below 2L Standards. ATC collected groundwater samples from six monitoring wells and three water supply wells. PCE was detected above March 2008 2L Standards in samples collected from monitoring wells MW-5, MW-17, and MW-IOB. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, 8408, and 8405 Camellia Drive below 2L Standards. ATC collected groundwater samples from seven monitoring wells and three water supply wells. PCE was detected June 2008 above 2L Standards in samples collected from monitoring wells MW-8B and MW-16. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 Camellia Drive below 2L Standards. ATC collected groundwater samples from six monitoring wells and three water supply wells. PCE was detected above September/October 2L Standards in samples collected from monitoring wells MW-5, MW-17, and MW-IOB. Chlorinated compounds were 2008 detected in samples collected from water supply wells located at 8404, 8408, and 8405 Camellia Drive below 2L Standards. Monitoring wells MW-22S, MW-22D, and MW-23 and injection wells IW-1, IW-2, IW-3, IW4, IW-5, IW-6, IW-7, IW- November 2008 8, IW-9, and IW-10 were installed. ATC collected groundwater samples from eight monitoring wells. PCE was detected above 2L Standards in MW-5 MW-8B MW-10B MW-16 MW-22S and MW-23. December 2008 ATC collected groundwater samples from six monitoring wells. PCE was detected above the 2L Standard in MW-22S, MW-23 IW-3 IW4and IW-5. January 2009 A pilot injection for enhanced reductive dechlorination was conducted. ABC+ was injected into ]W-1 and IW-2. ATC collected groundwater samples from 12 monitoring wells and 17 water supply wells. PCE was detected in MW-5, February 2009 MW-8B, MW-IOB, MW-16, MW-22S, MW-23, IW-3, IW-4, and IW-5 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply well located at 8405 Camellia Drive below the 2L Standards. Page 7 of 127 Table 1: Site Chronology DSCA 1 D No.: 920001 Chronology of Events Instructions: Brief description of all significant events that have occurred since a problem was Date suspected at the facility. Commence with the first date a problem was suspected and continue through the most recent activity described in the current report. ATC collected groundwater samples from 11 monitoring wells and three water supply wells. PCE was detected in MW- April 2009 5, MW-813, MW-IOB, MW-16, MW-22S, MW-22D, MW-23, RV-3, IW4, and IW-S at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 and 8408 Camellia Drive below 2L Standards. ATC collected groundwater samples from 18 monitoring wells and 17 water supply wells. PCE was detected in MW-5, July 2009 MW-813, MW-16, MW-17, MW-22S, MW-23, AV-3, IW4, and IW-5 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, 8408, and 8409 Camellia Drive below 2L Standards. September 2009 ATC collected groundwater samples from eight monitoring wells. PCE was detected in MW-22S, MW-23, RV-1, IW-6, RV-7 IW-8 and IW-9 at concentrations greater than the 2L Standard. ATC collected groundwater samples from 12 monitoring wells and three water supply wells. PCE was detected in MW- October 2009 5, MW-8B, MW-10A, MW-10B, MW-16, MW-22S, MW-23, IW-3, IW-4, and IW-5 at concentrations greater than 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 and 8408 Camellia Drive below 2L Standards. ATC conducted an air sampling event. The scope included the collection of air samples Indoor #1, Indoor 42 and an January 2010 outdoor air sample. It also included the collection of sub -slab soil gas samples SGMP # 1 and SGMP #2. The results of the air sampling indicated no exceedances of the risk levels considered acceptable by the DSCA Program. February 2010 ATC prepared an Injection Evaluation Report and a Groundwater Monitoring Report documenting sampling activities from October 2008 to October 2009. ATC collected groundwater samples from 18 monitoring wells and 14 water supply wells. PCE was detected in MW-5, February 2010 MW-813' MW-9, MW-IOB, MW-16, MW-17, MW-22S, MW-23, IW-3, IW4, and IW-5 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, 8405 and 8408 Camellia Drive below the 2L Standards. ATC collected groundwater samples from 12 monitoring wells and three water supply wells. PCE was detected in MW- April 2010 5, MW-8B, MW-IOB, MW-16, MW-22S, MW-23, IW-3, IW-4, and IW-5 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 and 8408 Camellia Drive below the 2L Standards. ATC collected groundwater samples from 21 monitoring wells and 10 water supply wells. PCE was detected in MW- July 2010 813, MW-16, MW-21, and NM-23 at Concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, 8408, and 8409 Camellia Drive below the 2L Standards. August 2010 ATC prepared a Soil Gas and Air Sampling Report documenting the January 2010 vapor intrusion sampling. ATC collected groundwater samples from 12 monitoring wells and three water supply wells. PCE was detected in MW- October 2010 5, MW-813, MW-IOB, MW-I IA, MW-16, MW-22S, MW-23, IW-3, IW4, and IW-5 at concentrations greater than the 2L Standard. January 2011 ATC submitted an annual Groundwater Monitoring Report documenting groundwater sampling events conducted in February 2010 April 2010 July 2010 and October 2010. ATC collected groundwater samples from 9 monitoring wells and 12 water supply wells. PCE was detected in MW-Sli, MW-16, MW-21, and MW-23 at concentrations greater than the 2L Standard. Chlorinated compounds were detected iu April 2011 samples collected from water supply wells located at 8404, 8405, 8408, and 8409 Camellia Drive and 8405 Azalea Place below the 2L Standards. TCE, 1,24chloroethane, and carbon tetrachloride were detected in the water supply well located at 8404 Azalea Place at concentrations greater than the 2L Standards. ATC collected groundwater samples from 7 monitoring wells and 5 water supply wells. PCE was detected in MW-5, MW-IOB, and MW-22S at concentrations greater than the 2L Standard. Chlorinated compounds were detected in July 2011 samples collected from water supply wells located at 8405, 8408, and 8409 Camellia Drive below the 2L Standards. PCE was detected in the water supply well located at 8404 Camellia Drive at a concentration greater than the 2L Standard. ATC collected groundwater samples from 8 monitoring wells and 9 water supply wells. PCE was detected in MW-811, October/November MW-IOB, and MW-23 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples 2011 collected from water supply wells located at 8405 Azalea Place and 8404, 8405, 8408, and 8409 Camellia Drive below the 2L Standards. ATC collected groundwater samples from 10 monitoring wells, 2 injection wells and 5 water supply wells. PCE was January/February detected in MW-5, MW-lOB, MW-11A, MW-16, MW-22S, MW-24S, MW-24D, IW-8, and IW-9 at concentrations 2012 greater than the 2L Standard. cis-1,2-DCE was detected in the sample collected from the water supply well located at 8409 Camellia Drive below the 2L Standards. PCE was detected in the sample collected from the water supply well located at 8404 Camellia Drive at a concentration greater than the 2L Standard. April 2012 ATC submitted an annual Groundwater Monitoring Report documenting groundwater sampling events conducted in A ril 2011 July 2011 November 2011 and February 2012. April 2012 lGroundwater Remediation Permit #WQ0035324 was issued by NCDENR on April 16, 2012. Page 8 of 127 Table I: Site Chronology MEL DSCA ID No.: 920001 ` Chronology of Events Instructions: Brief description of all significant events that have occurred since a problem was Date suspected at the facility. Commence with the first date a problem was suspected and continue through the most recent activity described in the current report. ATC collected groundwater samples from 15 monitoring wells and 9 water supply wells. PCE was detected in MW-5, July 2012 MW-813, MW-1013, MW-16, MW-22S, MW-23, MW-24S, MW-24D, IW4, IW-5, IW-8, and RV-9 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 Azalea Place and 8405, 8408, and 8409 Camellia Drive below the 2L Standards. July/August 2012 ATC supervised the installation of an In Situ Delivery (ISDT ) system for the injection of CarBstrateTM. The system became operational on Wednesday, August 28, 2012. August 2012 ATC began pilot phase activities on August 28, 2012. During the pilot phase, wells AV-1 and IW-3 were used for injection and well EW-2 was used for extraction. ATC collected groundwater samples from 13 monitoring wells and 7 water supply wells. PCE was detected in MW-5, November/ MW-813, MW-IOB, MW-11A, MW-16, MW-22S, MW-23, MW-24S, MW-24D, IW-4, IW-5, IW-8, and IW-9 at December 2012 concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8405 Azalea Place and 8404, 8405, 8408, and 8409 Camellia Drive below the 2L Standards ATC collected groundwater samples from 15 monitoring wells and 10 water supply wells. PCE was detected in MW- 8B, MW-11A, MW-22S, MW-23, MW-24S, MW-24D, IW4, IW-5, IW-8, and IW-9 at concentrations greater than the I chruai y 2013 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8405 Azalea Place and 8404, 8405, 8408, 8409, and 8412 Camellia Drive below the 2L Standards. Naphthalene was detected in samples collected from water supply wells located at 8408 Azalea Place and 8401, 8404, 8412, and 8413 Camellia Drive below the 2L Standards. On February 25, 2013, the pilot phase of the recirculation system was terminated. February 2013 On February 25, 2013, pilot phase activities for the recirculation system were terminated. May 2013 ATC collected Crawlspace Air #3. ATC collected groundwater samples from 15 monitoring wells and 7 water supply wells. PCE was detected in MW-5, MW-813, MW-lOB, MW-I IA, MW-16, MW-22S, MW-23, MW-24S, MW-24D, IW4, IW-5, IW-8, and IW-9 at May 2013 concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 and 8405 Azalea Place and 8401, 8404, 8405, 8408 and 8409 Camellia Drive below the 2L Standards. Naphthalene was detected in the sample collected from the water supply well located at 8401 Camellia Drive below the 2L Standards. August 2013 ATC submitted a Residential Indoor Air Sampling Report documenting the sampling of Crawlspace Air #3. ATC collected groundwater samples from 15 monitoring wells and 10 water supply wells. PCE was detected in MW-5, MW-813, MW-1 OB, MW-11A, MW-16, MW-22S, MW-23, MW-24S, MW-24D, IW4, IW-5, IW-8, and IW-9 at concentrations greater than the 2L Standard. Concentrations TCE in MW-23 and bromodichloromethane in IW-5 were September 2013 also detected above 2L Standards. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, 8405, and 9408 Azalea Place and 8404, 9405, 8408, 8409, 8412, and 8413 Camellia Drive below the 2L Standards. Carbon tetrachloride and 1,2-dichloroethane were detected in the sample collected from the water supply k� ell located at 8408 Camellia Drive above the 2L Standards ATC supervised the implementation of full-scale activities for the ISDTM system for the continued injection of September 2013 CarBstrate m. The system became operational on Tuesday, September 10, 2013. During full-scale activities, wells I W- IA, IW-2, IW-3, IW-4, TWA, IW-6, and IW-7A were used for injection and wells EW-8, EW-9, and EW-10 were used for extraction. ATC collected groundwater samples from 11 monitoring wells, 2 injection wells, 2 extraction wells and 7 water supply wells. PCE was detected in MW-5, MW-813, MW-IOB, MW-16, MW-22S, MW-23, MW-24S, MW-24D, IW-5, IW-7, December 2013 EW-8, and EW-9 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 9404, and 8405 Azalea Place and 8404, 8405, 8408, and 8409 Camellia Drive below the 2L Standards. December 2013 ATC submitted an annual Groundwater Monitoring Report documenting groundwater sampling events conducted in July 2012 November 2012 February 2013 May 2013 and September 2013. January 2014 ATC collected indoor air samples Indoor # I and Indoor #2. ATC collected groundwater samples from I monitoring wells, 2 injection wells, 2 extraction wells and 9 water supply wells. PCE was detected in MW-5, MW-813, MW-1013, MW-11A, MW-16, MW-22S, MW-24S, IW-5, IW-7, EW-8, and March 2014 EW-9 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, and 8405 Azalea Place and 8404, 8405, 8408, 8409, 8412, and 8413 Camellia Drive below the 2L Standards. ATC collected groundwater samples from 11 monitoring wells, 2 injection wells, 2 extraction wells and 9 water supply wells. PCE was detected in MW-5, MW-813, MW-lOB, MW-11A, MW-16, MW-22S, MW-24S, IW-5, IW-7, and EW-8 June 2014 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 and 8405 Azalea Place and 8404, 8405, 8408, and 8409 Camellia Drive below the 2L Standards. August 2014 ATC collected indoor air samples Indoor #1 and Indoor #2. ATC collected groundwater samples from 12 monitoring wells, 2 injection wells, 2 extraction wells and 10 water supply wells. PCE was detected in MW-5, MW-8B, MW-IOB, MW-11A, MW-16, MW-22S, MW-24S, MW-24D, IW-7, EW-8 September 2014 and EW-9 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404, 8405, 8408 Azalea Place and 9404, 8405, 8408, 8409, 8412, and 8413 Camellia Drive below the 2L Standards. Page 9 of 127 Table 1: Site Chronology MCA 11) 10.: 920001 Chronology of Fvents Instructions: Brief description of all significant events that have occurred since a problem was Date suspected at the facility. Commence with the first date a problem was suspected and continue through the most recent activity described in the current report. ATC submitted an Indoor Air Sampling Report documenting the sampling of Indoor #1 and Indoor #2 during the winter October 2014 and summer months of 2014. ATC collected groundwater samples from 12 monitoring wells, 1 injection well, 2 extraction wells, and 7 water supply wells. PCE was detected in MW-5, MW-813, MW4013, MW-11A, MW-16, MW-22S, MW-24S, MW-24D, EW-8, and December 2014 EW-9 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 and 8405 Azalea Place and 8404, 8405, 8408, and 8409 Camellia Drive below the 2L Standards. ATC collected groundwater samples from 13 monitoring wells, 2 (previously used) injection wells, 1 extraction well, and 10 water supply wells. PCE was detected in MW-5, MW-813, MW-lOB, MW-11A, MW-12, MW-16, MW-22S, March 2015 MW-24S, MW-24D, IW-7, EW-8 and EW-9 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8404 and 8405 Azalea Place and 8404, 8405, 8408 and 8409 Camellia Drive below the 2L Standards. ATC collected groundwater samples from 13 monitoring wells, 2 (previously used) injection wells, 1 extraction well, and 7 water supply wells. PCE was detected in MW-5, MW-813, MW-lOB, MW-11A, MW-12, MW-16, MW-22S, MW- June 2015 24S, MW-24D, IW-7, and EW-9 at concentrations greater than the 2L Standard. Chlorinated compounds were detected in samples collected from water supply wells located at 8405 Azalea Place and 8404, 9405, 8408, and 8409 Camellia Drive below the 2L Standards. Page 10 of 127 Table 6: Monitoring \\ ell (construction Jima 1 DSCA IDNo.: 92000 , — Well ID Date Installed (mm/dd/yy) Number of Samples Well Depth [feet] Well Diameter [inch] Screen Interval [feet] Status (Active/Inactive) MW-1 5/l/95 20 36 2 26-36 Abandoned MW-ID 11/11/05 2 140 2 130-140 Not Locatable MW-2 6/l/95 1 28 2 18-28 Abandoned MW-3 6/l/95 12 40 2 3040 Active MW4 11/1/95 19 70 2 65-70 Abandoned MW-5 ll/l/95 41 68.5 2 63.5-68.5 Active MW-6 ll/l/95 3 70 2 65-70 Destroyed MW-7 ll/l/95 24 70 2 65-70 Active MW-SA 3/13/97 20 148 2 138-148 Active MW-8B 3/2196 44 83 2 73-83 Active MW-9 3/3/96 25 63 2 53-63 Active MW-l0A 1 /16/97 39 80 2 75-80 Active MW-IOB 1 1697 46 45 2 2545 Active MW-11A 1/I/97 42 105 2 100-105 Active MW-I1B I/l/97 21 35 2 25-35 Active MW-12 3/I1/97 18 40 3040 \ctice MW-13 3/11/97 16 40 2040 Active NM'-14 3/11/97 1 40 20-40 Abandoned MW-15 3/12/97 1 40 ? 20-40 Abandoned MW-16 3/13/97 41 40 2040 Active MW-17 925/97 20 40 2040 Active MW-18 3/30/99 1 35 30-35 Abandoned MW-19 3/31/99 6 35 2 30-35 Not Locatable MW-20 3/31/99 8 35 2 30-35 Abandoned MW-21 11/10/05 9 28 2 13-28 Active MW-22S 11/5/08 25 45 1 3045 Active MW-22D 11/5/08 ?; 85 1 80-85 Active NM-23 11/4/08 25 45 2 3045 Active MW-24S 2/7/12 12 50 1 30-50 Active M"'-241) 2/7/l2 12 83 2 73-83 Active IN`-1 11/3/08 2 47 2 29-39,4547 Inactive IW-lA 727/13 0 47 4 29-39, 4547 Active IW-2 11/6/08 0 67 2 35-50, 54-60, 65-67 Active IW-3 11/5/08 8 47 2 27.47 Active IW4 11/11/08 14 87 2 3045,55.60,75-87 Active IW-5 I I/13/08 21 87 2 35-60, 70-87 Inactive IW-5A 7/27/13 0 87 4 35-60, 70-87 Active IW-6 11/14/08 1 87 2 40-50, 60-87 Active IW-7 11/6/08 7 87 2 35-50, 60-70, 80-87 Inactive IW-7A 727/13 0 87 4 35-50, 60-70, 80-87 Active 'EW-8 11/12/08 13 87 2 30-55,60.65,75-87 Active •EW-9 11/11/08 12 87 2 35-45,50-87 62-67,72 Active 'EW-10 1 11/17/08 1 2 87 2 30-55, 60-75, 80-87 Active 'Formerly injection ell (IW). Page 24 of 127 Table 7: Groundwater Elevation Data Groundwater Sampling Point Sampling Date (mm/dd/yy) TOC Elevation [feet] Depth to Water [feet bgs] Elevation Groundwater feet Depth to NAPL [feet bgs] NAPL Thickness [feet] Corrected* Groundwater Elevation feet MW-1 11/13/95 477.32 31.16 446.16 NA NA NA 4/1"6 29.40 44T92 NA NA NA 6/6/96 28.45 448.87 NA NA NA 6/20/96 27.85 449.47 NA NA NA 4/1/99 27.86 44946 NA NA NA 10/19/99 28.50 448.82 NA NA NA 3/14/00 27.70 44962 NA NA NA 8/12/03 27.60 449.72 NA NA NA 3N/05 25,42 45190 NA NA NA 12/9/05 29.81 447.51 NA NA NA 8/8106 29.82 447.50 NA NA NA MW ID 1219/05 477.63 31.34 446.29 NA NA NA 8/8/06 6.12 471.51 NA NA NA MW-2 11/13/95 NA 21.80 71.08 NA NA NA MW-3 11/13/95 479.04 31.52 447.12 NA NA NA 4/18f96 30.12 44892 NA NA NA 6/6/96 29.67 449.37 NA NA NA 6/20/96 29.55 449.49 NA NA NA 4/1/99 28.15 450.89 NA NA NA 10/19/99 28. 76 450.28 NA NA NA 8/12/03 27.41 451.63 NA NA NA 3/9/05 28.97 450.07 NA NA NA 12/9105 30.27 449.77 NA NA NA 8/8/06 30. 19 448.85 NA NA NA 3/11/08 3207. 44697 NA NA NA 9/9/08 32.00 447.04 NA NA NA 1018/08 31.73 447.31 NA NA NA 10/7/09 31.05 447.99 NA NA NA 2/2/10 30.85 448.19 NA NA NA 7/13/10 29.50 449.54 NA NA NA 10/19/10 29.71 449.33 NA NA NA 4/25/11 30.99 448.05 NA NA NA 7/26/11 31_18 447,86 NA NA NA 11/1/11 31.65 447.39 NA NA NA 1/25/12 32.15 446.89 NA NA NA 7/17/12 31.92 447.12 NA NA NA 11/28/12 32.41 446.63 NA NA NA 2/25/13 32.66 446.38 NA NA NA 5/28/13 31.68 447,36 NA NA NA 9/9/13 30.30 448.74 NA NA NA 12/9113 31.69 447.35 NA NA NA 3/24/14 31.56 447,48 NA NA NA 6/16/14 30.28 448.76 NA NA NA 9/22/14 30.04 449.00 NA NA NA 12/15/14 30.33 448.71 NA NA NA 3/16/15 29.78 449.26 NA NA NA 6/15/15 29.04 450.00 NA NA NA MW4 11/13/95 477.02 31.05 445.97 NA NA NA 4/19/96 29.22 447.80 NA NA NA 6/6Y96 28.34 448.68 NA NA NA 6/20/96 57.79 419,23 NA NA NA 4/1/99 2Z67 449.35 NA NA NA 10/19/99 29.11 448.91 NA NA NA 3/14/00 27.67 449.35 NA NA NA 8/12/03 27.52 449.50 NA NA NA 3/14/05 28.08 448 94 NA NA NA 12/9/05 30.27 448.77 NA NA NA 818/06 29.72 447.30 NA NA NA Page 25 of 127 Table 7: Groundwater Elevation Data Groundwater Sam lin Point p g Sampling Date mm/dd/ YY) TOC Elevation feet Depth to Water feet b s S ] Groundwater Elevation feet Depth to NAPL feet b NAPL Thickness feet Corrected' Groundwater Elevation feet MW-5 11/13/95 47249 29.76 442.73 NA NA NA 4/18/96 28.84 443.65 NA NA NA 4/1/99 22.65 449.84 NA NA NA 10/19/99 22.95 449.54 NA NA NA 3/14/00 22.31 450.18 NA NA NA 8/12/03 21.32 451,17 NA NA NA 3/9/05 23.18 449.31 NA NA NA 12/9/05 24.76 447.73 NA NA NA 818/06 2459 447.90 NA NA NA 3/11/08 26.75 445.74 NA NA NA 9/9/08 26.54 445.95 NA NA NA 1018/08 26.54 445.95 NA NA NA 2/4/09 2625 446.24 NA NA NA 4/2/09 25.81 446.68 NA NA NA 7/15/09 24.80 447.69 NA NA NA 10/6/09 25.69 446.80 NA NA NA 22/10 25.66 446.83 NA NA NA 4/20/10 24.61 447.88 NA NA NA 7/13/10 24.16 448.33 NA NA NA 10/20/10 24,68 447.81 NA NA NA 4/25/11 26.08 44641 NA NA NA 726/11 26.20 446.29 NA NA NA II/1/I1 26.73 445.77 NA NA NA 1126/12 26.80 445.69 NA NA NA 7/17/12 26A2 44607 NA NA NA 11/28/12 25.53 446.96 NA NA NA 225/13 27.26 44i 23 NA NA NA 528/13 26.36 446.13 NA NA NA 9/9/13 2665 445.84 NA NA NA 12/9/13 25.85 446.64 NA NA NA 3/24/14 25,07 447A2 NA NA NA 6/16/14 24.30 448.19 NA NA NA 9/22/14 23.7i 448.74 NA NA NA 12/15/14 24.02 448.47 NA NA NA 3/16/15 2354 44895 NA NA NA 6/16/15 22.92 449.57 NA NA NA MW-6 11/13/95 NA 31.36 65,10 NA NA NA 4/18/96 29.50 66.96 NA NA NA 6/6/96 28.18 68.28 NA NA NA MW-7 11/13/95 47690 30.86 446.04 NA NA NA 4/18/96 29.13 447.77 NA NA NA 6/6/96 28,60 448.30 NA NA NA 6/20/96 28.36 448.54 NA NA NA 4/l/99 27.26 449.64 NA NA NA 10/19/99 28.20 448.70 NA NA NA 3/14/00 27.75 449.15 NA NA NA 12/9/05 28.73 448.17 NA NA NA 8/8/06 29.79 447.11 NA NA NA 12/12/07 31.00 44590 NA NA NA 10/8/08 31.52 445.38 NA NA NA 7/16/09 30.00 44690 NA NA NA 10/7109 30.52 446.38 NA NA NA 2/2/10 30.75 446.15 NA NA NA 4/20/10 30.26 446.64 NA NA NA 7/13/10 29.86 447.04 NA NA NA 10/19/10 29.37 447.53 NA NA NA 4/25111 3093 44597 NA NA NA 7/26/11 31.09 445.81 NA NA NA 11/1/11 31,05 445.77 NA NA NA 7117/12 31.77 445.13 NA NA NA 11/28/12 3146 445.44 NA NA NA 225/13 31.90 445.00 NA NA NA 529/13 31.56 445.34 NA NA NA 919/13 30.85 446.05 NA NA NA 12/9/13 30.67 446.23 NA NA NA 3/24/14 31.14 445.76 NA NA NA 6/16/14 31.05 445.85 NA NA NA 9122/14 30.36 446.54 NA NA NA 12/15/14 29.48 447,42 NA NA NA 3/16/15 29.30 447.60 NA NA NA 6/15/15 30.50 446.40 NA NA NA Page 26 of 127 v� v � o a¢ Z Z Q a Z Z a¢ Z Z a¢ Z Z Q¢ Z Z a Q Z Z a a Z Z a Q¢ Z Z a¢¢¢ Z Z Z Z Q¢ Z Z Q Z Z Q a Z Z Q a Z Z a Q¢¢ Z Z Z Z Q¢ Z Z Q Q Z Z Q Q Z Z a¢ Z Z a¢ Z Z a¢ Z Z Q Q Z Z Q Q¢ Z Z a¢ Z Z a Z Z a¢ Z Z a a Z Z Q Q Z Z a¢¢¢¢ Z Z Z Z Q¢ Z Z Z 0 0 � v F ¢ a z z a a z z a a¢¢¢¢¢ z z z z z z a z z a a z z Q a¢¢¢¢ z z z z z z a a z z a¢ z z a a z z a¢¢¢¢ z z z z a¢¢ z z z z a a z z a a z z a a z z a¢ z z a a z z a¢ z z a a¢¢ z z z z a¢¢ z z a z z a a¢ z z a z z a¢¢ z z a¢ z z a¢ z z z z ..1 z m c z a a z z a a z z a a z z a a¢ z z a z 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V � m F C7 {e / \/ 15, )f __,»_,_-_:_::::::::aJ)!■;$//«\ieJ/27{je7G®g§!e\/e2\$$y$j/$)2;;\{ � § \( ;tt tt § �! !»!#f§§!§§§§§§§$!!!!$!§§§»»!!!f&&!!tf!!!ft(f)%t))f#t;ltt#$$$#!(/( _ \2 y Z Z 2: 7: Z Z Z Z Z Z Z z z z z z z z z z > > Z> > > > > > > > > > > > > > > > > > > > > > > > > > > > > `\\ \ T ^& \ \ \ \ >>>>>>>>>>>>>>>>>>>>>>>>>>>>> >>>>>>>>>>>>>>>>>>>>>>>>>>>>>>>> �) \ [ \ [on. zz�zzzzzzzzzzzzzzzzzzzzzzzzzz(;i {!\>>>>»>>>>>>>>>>>>>>>>>>>»>>>>>�>�»>>>>>>>���� \}§\ Table 7: Groundwater Elevation Data OSOM a Groundwater Sampling Point Sampling Date (mm/dd/yy) TOC Elevation [feet] Depth to Water [feet bgs] Groundwater Elevation feet Depth to NAPL [feet bgs] NAPL Thickness [feet] Corrected' Groundwater Elevation Ifeetl MW-IOB 4/l/99 480.65 36.42 444.23 NA NA NA 10/19/99 37.36 443,29 NA NA NA 3/14/00 36.61 444,01 NA NA NA 8/13103 36,06 444,59 NA NA NA 12/9/05 38.72 441.93 NA NA NA 8/8/06 39.38 441.27 NA NA NA 3/12/08 41.25 439,40 NA NA NA 1018/08 41.33 439.32 NA NA NA 214/09 4195 438.70 NA NA NA 42/09 40.52 440. 13 NA NA NA 7114/09 39.03 441.62 NA NA NA 10/7/09 39.31 441.34 NA NA NA 2/2110 40,50 440,15 NA NA NA 4/20/10 39.03 441.62 NA NA NA 7113/10 38.17 44248 NA NA NA 10/20/10 39.02 441.63 NA NA NA 4/26111 40.83 439.82 NA NA NA 7/27/11 40,83 439.82 NA NA NA 11/1/11 41.72 438.93 NA NA NA 1/25/12 41.82 438.83 NA NA NA 7/17/12 41.00 439.65 NA NA NA 11/28/12 41.97 438.68 NA NA NA 2/25/13 42.29 438.36 NA NA NA 5/28113 41.20 439.45 NA NA NA 9/9/13 3999 440.66 NA NA NA 12/9/13 4174 438.91 NA NA NA 3124/14 41.52 439,13 NA NA NA 6/16/14 40.21 440,44 NA NA NA 9/22/14 39.94 440.71 NA NA NA 12/15/14 39.98 440.67 NA NA NA 3/16/15 39.39 441,26 NA NA NA 6/19/15 37.73 442,92 NA NA NA MW-1]A 411/99 476.37 31.55 444.82 NA NA NA 10/19/99 35.24 441,13 NA NA NA 3/14/00 33,84 442,53 NA NA NA 8/13/03 33.59 442.78 NA NA NA 12/20/05 37,58 428.79 NA NA NA 8/8/06 37.64 438,73 NA NA NA 12/11/07 38,77 437.60 NA NA NA 10/8/08 39,19 437.18 NA NA NA 2/4/09 38.71 43766 NA NA NA 4/2/09 37,93 438.44 NA NA NA T14/09 36,64 439.73 NA NA NA 10/7/09 3642 439.95 NA NA NA 22/10 38.01 43836 NA NA NA 4/20/10 36,29 440,08 NA NA NA 7/13/10 35,79 440,58 NA NA NA 10/20/10 37.15 439.22 NA NA NA 426,111 37.32 439.05 NA NA NA 727/11 38,81 437.56 NA NA NA 11/1/11 39.62 436.75 NA NA NA 1/25/12 39.41 436.96 NA NA NA 7/17/12 38,78 437.59 NA NA NA 11/28/12 39,93 436,44 NA NA NA 2/25/13 39,81 436,56 NA NA NA 528/13 38,56 437.81 NA NA NA 9/9/13 37,52 438,85 NA NA NA 12/9/13 38.86 43751 NA NA NA 3/24/14 38.25 438.12 NA NA NA 36,89 439.48 NA NA NA 37.13 439.24 NA NA NA E36 37.03 439.34 NA NA NA 35.94 44043 NA NA NA 34.91 441.86 NA NA NA Page 29 of 127 Q Q Q Q Q Q Q Q Q¢¢ Q Q 6 Q 6 0 0 0 Q Q Q Q Q¢ Q Q Q Q 6 6¢ G Q Q Q Q Q Q¢¢¢¢ Q 6 6 Q G Q .� z Z z z Z z Z z Z z z z z z Z z Z z z z z z Z z z z z z z z z z z Z z Z z z z z z z z z z z z z Z Z z z z z mm U 0 t F Q Q z Z Q Q Z Z Q Q Z Z Q Q Z Z Q Q Z z Q¢¢ Z Z Q Z z Q Q Z Z 6¢ Z z Q Q z Z Q Q z z Q Q z z G Q z z Q Q z Z Q Q z z Q Q z z Q Q z Z Q Q¢ Z z G Z z Q Q z z Q 6 z z Q Q z z Q Q¢¢¢ z Z Z Z G Z Z Q 6 z z Q Q z z i qJq Q z s Q Q z z Q ¢ z z ¢ ¢ z z ¢ Q z z ¢ Q z z ¢ ¢ z z ¢ Q z Z ¢ G z z ¢ G z z ¢ G z z Q G z z G ¢ z z G ¢ z z G G Z z ¢ Q Z Z ¢ Q z Z Q Q z z ¢ ¢ z z G ¢ z z G ¢ z z G Q Z z Q ¢ z z ¢ ¢ z z ¢ ¢ z z Q ¢ z z ¢ ¢ z z G ¢ z z v � o W C7 `v m ,- 3� "''-aaaaaaaaa -aaaaaaa°°aaaxa� o _ aaaa,� a� O 0 _u z A :v, T 4,2=2c ZZ 9 C C � � o a U Table 7: Groundwater Elevation Data Groundwater Sam lin Point P g Sampling Date mm/dd/ YY) TOC Elevation feet Depth to Water feet b s g� Groundwater Elevation feet Depth to NAPL feet bgs NAPL Thickness feet Corrected* Groundwater Elevation rfmtj MW-13 4/IN9 477.66 29.50 448.16 NA NA NA 10/19/99 30,23 447.43 NA NA NA 3/14/00 29.85 447,81 NA NA NA 8/12/03 29.77 447,89 NA NA NA 12/9/05 31.35 446.31 NA NA NA 8/8106 31.98 445.68 NA NA NA 3/11/08 33.57 444.09 NA NA NA 9/9108 3384 443.82 NA NA NA 10/8/08 33,70 443.92 NA NA NA 7/14/09 32.15 445 91 NA NA NA 10/7/09 32.58 445.08 NA NA NA 2/2/10 32 95 444.71 NA NA NA 420/10 31,90 44536 NA NA NA 7/13/10 31.32 446.34 NA NA NA 10/IWIO 3161 446,05 NA NA NA 4/25/I1 33.02 444.64 NA NA NA 7/26/11 33,26 444.40 NA NA NA 11/1/I1 33,84 443.82 NA NA NA 7/17/12 33.73 443.93 NA NA NA 11/28/12 34.15 443.51 NA NA NA 2/25113 34.36 443,30 NA NA NA 5/28/13 33.78 443,88 NA NA NA 9/9/13 32,56 445.10 NA NA NA 12/9/13 33.66 444.00 NA NA NA 3/24/14 3407 443.59 NA NA NA 6/16/14 32.61 445,05 NA NA NA 9/22/14 3041 447.25 NA NA NA 12/15/14 31.83 445,83 NA NA NA 3/I6/15 31.76 445.90 NA NA NA 6/15/15 29,21 448645 NA NA NA MW-14 3/II197 NA NA NA NA NA NA MW-15 3/12/97 NA NA NA NA NA NA MW-16 4/1/99 477.62 26.75 450.87 NA NA NA 10/19/99 26,75 450,87 NA NA NA 3/14/00 26,12 45150 NA NA NA 8/12/03 23.10 45452 NA NA NA 8/8/06 28,63 448,99 NA NA NA 12/12/07 40.00 437.62 NA NA NA 10/8/08 30,20 447,42 NA NA NA 2/4/09 29.85 447.77 NA NA NA 4/2/09 24,41 453.21 NA NA NA 7/15/09 28.88 448,74 NA NA NA 10/6/09 29,91 447.71 NA NA NA 2/2/10 29,20 44842 NA NA NA 4/20/10 28,27 449.35 NA NA NA 7/13/10 28,24 449.38 NA NA NA 10/20/10 28.79 448.83 NA NA NA 4/26/11 29.68 44794 NA NA NA 7/26/11 30.26 447,36 NA NA NA 11/1/I1 30.47 447.15 NA NA NA 1/26/12 30,50 447.12 NA NA NA 7/17/12 3043 447,19 NA NA NA 11/28/12 31,00 446.62 NA NA NA 225/13 31,18 446.44 NA NA NA 5/28/13 30,20 44742 NA NA NA 9/9/13 29,57 448,05 NA NA NA 12/9/13 30.71 44691 NA NA NA 324/14 29.74 417,88 NA NA NA 6116/14 28.70 448...92 NA NA NA 22/4 28,69 44893 NA N N 4 28.85 44877 NA NA A2I1 39 28.02 449.6 NA NA NA / 27.52 450.10 NA NA NA Page 31 of 127 Table 7: Groundwater Elevation Data Groundwater Sampling Point Sampling Date (mm/dd/yy) TOC Elevation [feet] Depth to Water [feet bgs] Groundwater Elevation feet Depth to NAPL [feet bgs] NAPL Thickness [feet] Corrected* Groundwater Elevation feet MW-17 4/l/99 476.07 25,01 451.06 NA NA NA 10/1999 24.90 451.17 NA NA NA 3/14/00 24,31 451.76 NA NA NA 8/13/03 27.02 449.05 NA NA NA 12/9105 27,39 448.68 NA NA NA 8/8/06 26.63 449,44 NA NA NA 3/11108 28,40 447.67 NA NA NA 9/9/08 30,55 445.52 NA NA NA 7/14/09 27.10 448.97 NA NA NA 10/7/09 28.20 447.87 NA NA NA 2/2/10 27,23 448.84 NA NA NA 7/13/10 26.39 449.68 NA NA NA 10/19/10 27.08 44899 NA NA NA 4/25/II 27,78 448.29 NA NA NA 7/26111 28A3 44764 NA NA NA 11/1/11 28 53 447.54 NA NA NA 7/17/12 28.60 447,47 NA NA NA 11/28/12 29.01 447.06 NA NA NA 2/25/13 29,24 446.83 NA NA NA 5/28/13 28.22 447.85 NA NA NA 9/9/13 27,67 448.40 NA NA NA 12/9/13 28.97 447,10 NA NA NA 3/24/14 27.87 448.20 NA NA NA 6/16/14 26.86 449.21 NA NA NA 9/22/14 2692 449. 15 NA NA NA 12/15/14 27.12 448.95 NA NA NA 3/16/15 26.14 449.93 NA NA NA 6/15/15 26.40 449.67 NA NA NA MW-18 4/1/99 NA NA NA NA NA NA MW-19 4/l99 10/1999 NA 18,00 72.43 NA NA NA 17.11 73.32 NA NA NA 3/14/00 17.51 72.92 NA NA NA MW-20 4/l/99 10/19/99 NA 24.62 70.99 NA NA NA 24.45 71916 NA NA NA 3/14/00 24.34 71.27 NA NA NA 8/13/03 23.97 7164 NA NA NA MW-21 129105 467,90 1950. 448.40 NA NA NA 8/8/06 18.75 449915 NA NA NA 12/12/07 20.85 447.05 NA NA NA 10/8/08 19.94 447.96 NA NA NA 7/14/09 18.95 448.95 NA NA NA 10/6/09 20,26 447,64 NA NA NA 2/2/10 18.72 449.18 NA NA NA 7/13/10 1841 449.49 NA NA NA 10/19/10 1938. 44852 NA NA NA 4/25/II 1890 449.00 NA NA NA 7/26/11 20.45 447945 NA NA NA 11/1/11 20.it 447,87 NA NA NA 7/17/12 2035 447.55 NA NA NA 11/28/12 20.97 44693 NA NA NA 2/25/13 2033 447.57 NA NA NA 528/13 19,31 448.59 NA NA NA 99/13 19,50 448.40 NA NA NA 12/9/13 20,81 44709 NA NA NA 324/14 19.07 448.83 NA NA NA 6/I6/14 18.46 449944 NA NA NA 9/22/14 1902. 448,88 NA NA NA 12/15/14 19.05 448.85 NA NA NA 3/16/15 17.59 450.31 NA NA NA 6115/15 22.09 445.81 NA NA NA Page 32 of 127 o y n �! s 0 w 0 o fl C7 ' Ci w>" O a^ z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z a w z �a b r z z z 9 a z z a 9 z z 9 9 z z a a z z a a z z a 9 z z a D z z a D z z a a Z z a 9 z z a D z z 9 a z z 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a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z a a z z n a z z D a z z a a z z D a z z a a z z a a z z a a z a a z r z a z z a a z z a D z z D D z z D a z z a a z z a D z z a D z z a a z z 9 D z z a a z z a a z Z a a z z a 9 z z a a z z a a z z a a z z a a z z D D z z a a z z a a z z a a z z a a z z a D z Z a D z z 9 a Z s a m � z z z z z z z z z z z z z z z z z z z z z z z z z z z 7 z z z z z z z z z z z z z z z z z z z z z z z p a D D D D a D D a D D D 9 D 9 D 9 D D D a a 9> a D D a D D a a D 9 D 9 9 D D a D a D D 9 D D D a 9 D D E m n. Table 7: Groundwater Elevation Data Groundwater Sampling Point Sampling Date (mm/dd/yy) TOC Elevation [feet] Depth to Water [feet bgs] Groundwater Elevation feet Depth to NAPL [feet bgs] NAPL Thickness [feet] Groundwater Corrected' Elevation feet 1W-6 9/15/09 476.88 33.10 443.78 NA NA NA 10/20/10 32.32 444.56 NA NA NA 4/25/11 33.12 443.76 NA NA NA 11/28/12 35.21 441.67 NA NA NA 9/9/13 33.28 443.60 NA NA NA IW-7 9/15/09 477.72 34.04 443.68 NA NA NA 10/20/10 33.28 444.34 NA NA NA 4/25/11 35.09 442.63 NA NA NA 11/28/12 36.23 441 49 NA NA NA 9P9/13 34450 443.22 NA NA NA 12/9/13 35.05 442.67 NA NA NA 3/24/14 34.58 443.14 NA NA NA 6116/14 33.48 444.24 NA NA NA 9/22/14 32.98 444.74 NA NA NA 3/16115 32.82 444.9 NA NA NA 6/18115 31.71 446,01 NA NA NA •EW 8 9/0109 477.84 35.15 442.69 NA NA NA 10/20/10 3445 443.39 NA NA NA 4125/11 36.02 44L82 NA NA NA 1/25/12 37.22 440.62 NA NA NA 7/17/12 36.63 44121 NA NA NA 11/28/12 37.40 440.44 NA NA NA 2/25/13 37.70 440.14 NA NA NA 5/28/13 36.87 440.97 NA NA NA •EW 9 9/15/09 478.90 36.33 442.57 NA NA NA 10/20/10 35.78 443.12 NA NA NA 4/25/11 36.82 442.08 NA NA NA 1/25/12 38.12 440.78 NA NA NA 7/17/12 37.75 441.15 NA NA NA 11/28/12 38.63 440.27 NA NA NA 2/25/13 38.88 440.02 NA NA NA 528/13 3809 440.81 NA NA NA 'EW-10 9/15/09 478.34 36.03 442.31 NA NA NA 10/20/10 35 49 442.85 NA NA NA 4125/11 37.4 440-94 NA NA NA 11/28/12 38.24 440.1 NA NA NA RW-1 2/1/98 NA NA NA NA NA NA 625-26/98 NA NA NA NA NA RW-2 2/I/98 NA NA NA NA NA NA 6/25-26N8 NA NA NA NA NA MWC-I A 2/6/06 NA NA NA NA NA NA 'F-nerh injmtim cell (RV). 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Y r i 8 8 e x e e z x a x e p❑ z e p z g ❑❑ g x z g o x e o e z e r. a$ z o g g a„ x 8 g g g g g g g 8 g 8 o g a 8 z e 8 8 e e 8 88 s e 8 a e 8 8 e e 8 8 a e 8 8 s e 8 8 e E 8 8 a e= 8 8 8 8 8 = e s �asuv nyn iA°q-vn �< z z a<< z z e<„ z z z 8 g g ❑ z g ❑ g❑<< z z x g e a z z e a<< z z z x e 8 g g g g g g g e g z 8 8< e e 8 z o 8 8 e e 8 8 9 8 8 8 B B 8 8 B B 8 0 a 8 9 E 8 8 8 9 8 8 B e 8 8 e a 8 8 8 e B e `u <<< z z` z z z °z z g g g °z i' g g e e g z z ez z z g z g g g g g g g s s a e s e s a s e e a s e e s e e e 0 o e e e v o 8 8 8 e e e mo z c7 0 8 e =w<viy=!a.zy.o e g ❑❑ z a z g a❑ x x g g- ❑ c c c c a s s vex 8 8 a $ °z o g g a z g g g g g g 8 eee 8 m 8 8 s s 8 sseeeeaee 8 8 8 8 8 8 8 8 8 8 88 e C `zz z z z ggg=i❑c❑sssag e z z z z z z e e B x z z z z E g g gggzsssssssssssssssssss's'a,s'sa e 9 9 9 e 9 e e e e e e e e e e e B 9 e 6 e g 9 e a 00 F A Table 8: Analvtical Data for Groundwater 1 DSCA (D No.:._.920001 E {{5 §5xx m A. IVI/95 NA <0.005 NA NA NA 0.012 NA NA W.003 NA NA NA NA NA NA \A - 0032 10 a1 M1M'6 VI/% NA W.005 NA NA NA W.003 NA NA 0.005 NA NA NA NA NA NA IA 1.1 1,- <0.01 NA 8/1% NA ND NA NA NA ND NA NA ND NA NA NA NA NA NA NA 0.05 NA NA I l'I'95 NA <O.OD5 NA NA NA 0.1 NA NA <0005 NA NA NA N.4 NA NA NA NA 10.015 <005 NA 0.1; 96 NA <0.005 NA NA NA <0.005 NA NA 0.0.5 NA NA NA NA NA NA NA NA 0.010 <001 NA &1i96 NA ND NA NA NA NA NA ND NA NA NA NA NA N, NA NA ND NA NA ,.I- NA ND NA NA I I0.012 NA NA ND NA NA NA NA NA N':\ NA NA ND NA lwI NA <0,0005 NA NA .0 0.008] NA NA 0-5 NA NA NA NA NA N., NA NA 0.0005 N.A 3121/9] ND ND NA NA ND 0.0019 ND IA ND NA ND NA NA NA N.% NA NA 0.0005 NA 712 ND ND ND NA ND ND ND ND ND ND ND ND ND ND ND N'D ND ND NA 2/1/98 NA NA NA NA NA 0.0007 NA NA NA NA NA NA NA NA NA NA NA NA NA 11 .1-26.98 0.8023 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND NA N:\ 1120.9% ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND NA A 199 00013 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND NA N.A ' 6'199 0.0013 ND 0001 ND ND ND 0.001 ND ND ND 0.0033 ND ND ND ND ND W ND NA NA I011199 ND ND ND ND ND :r, \D ND ND ND ND ND ND ND ND ND \'D ND NA NA 3/1/00 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND \D ND NA NA 1ol- ND ND ND ND ND ID ND ND ND ND ND ND ND ND ND ND \D ND NA NA 1/1/01 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND \I/ M1'D NA NA vi-3 <0.0005 0-5<00005 <0.0005 <0.0005 <0.0005 <0.0005 ­5<0.0005 0-5 -001 <0,0005 00005 <0.0001 10,0005 -5<00005 O.0001 NA NA 311. of <0.0005 <0.0005 0.-1 NA 0.0001 <0.0001 <0.0005 -5 <0,0005 <0.0005 -- <0.0001 00005 <0.00115 -1 0.-1 1.- <0.DD05 NA NA 2'0'06 c0.0002 <0.0002 <0.0001 Om- <0.0008 <0.- <O.00o2 <0.0008 <O.o005 <0.0003 0.- <0.0002 00008 <O.000J .4 0.- <0.0002 N.o008 <0.0012 WA008 12120] c0.0005 <0.005 0.,0.,<0.001 0000631 <0.005 <0.005 N.003 0.0003 W.005 c0005 c0.005 <0.0005 �OM 0.005 W.0005 <0.005 001 Oo. 6.1]OS c0.0005 0.00022 <0.005 <0.005 N.001 0 -1 <0.005 <0.005 0.00181 0.0005 <0.005 Ooo5 <0.005 0.- 0.005 <0.005 0.0005 <0.005 000581 OoI 'I 1609 c0.0005 m.005 ..005 -5 0.001 <0.000] <0.005 <0.005 <0.00n <00005 <0.005 <0.005 <0.003 <0.0005 0.005<0.005 <0.w3 WADS ool ool 23/10 W.0005 A.005 <0.005 -1 0.005 M.0007 0.005 m.005 <0.0028 <0.0003 ..001 -005 m.003 <0.0001 <0.005 N 5 <0.0003 ...5W.05 - 7-10 <0.000}.. 0.001 -1<0.005 10005 -0oD7 -.5-50.-0-1 W.005 0.005<0.005 0.0005 0.005 W.005 0,0003 <0.005 0.00281 Obi 3/1119] ND 0.0022 NA NA 0011 1211 ND NA NA ND NA NA NANA NA NA 0.0007 NA NA Wl1 ND ND NA NA 0.0022 ND ND NA ND NA ND NA NA NA NA NA NA ND NA NA I- ND ND ND NA ND ND ND ND ND ND ND ND ND - ND ND ND ND NA NA 2'198 0.0005 NA 0.000] NA NA 08831 0.0019 NA NA NA 0.0033 0.0006 NA - NA NA NA 0- NA NA 625-2- ND OA01] ND ND ND 0.08I9 ND ND 0.0019 ND ND 00014 ND ND ND ND ND or- NANA 1-ND ND ND ND ND P2913 ND ND 8.805 ND ND ND ND ND ND ND ND ND NA NA 4. 1'99 \D ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND NANA G 199 0.0005 0.0012 0.0009 ND 0000] ND 0.0009 1. 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A^ 6 8 A"^^ B^" a 6 8 a 6^ ■ r CCa a 8 S YY 6 8 6 pp • A^^ S 8 8 A A^"^ A A$$^"" a A A A^ a e s e e a a A 8 e a aCa a s a o e a e a s s e 8 A 8 e a a a a s a a a 8 a s a a "8d 8 8 0 8 8 g 8 Vmyl W.- a s a a a a A 6 6 A a S 6 8 8" a 6" a 6 S ^ 6 6 8 6 6 6 6.a a g 8 8 8 8$ 8 8 8 88 8 8 8 8 8 8 8 8$ 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 rirn.. a.m� 8 $ $ $ 8 $ $ 8 $ $ $ $ $ $ $ $ $ P 8 $ $ $ $ $ $ $ $ $ 8 $ $ 8 $ $ 8 $ $ $ $ $ $ $ $ 8 8 8 " A 8 a^ 8 8 8 8 8 8 a 8$ a a 8 8 8 a 8 8 a 8 8 8 8 8 a 8 8 ea 8 8 a 4181618 8 8 8 8 a 8 8$ 6 a 8 a 8^ 8 8 a 8 8 a 8 8 8 a 8 8 8 Old* 8 8 a 8& 8 8 8 a 8 A B a 8 6 a A 8 a S 6 0 0 66 A 8 0 8 6 6 A 6 A A I a AA a.6 6 6 8 S a 6 8 A S a 8 8 a 8 8 g 8 8 8 a A 8 8 6 8 A 8 8 8 A A 8 6 A 6 a a a S a 8 8 6 A _- ---- 8 8 8 8 8 8 R 8 8 8 8 8 ___ ______ o s 8 14^ s 8 8 8 8 8$ �,o_ hbr«�nrim a A a a a a a 0 a 6 a 6 8 0 a A ^ a A A 8 8 A 6 6 9 8 8 a= a A A A a 8 8 A s A a A A A 8 -DichbroeAm. 8 8 $ 8 x g $ $ 8 $ $ $ $ $ $ $ $ $ $ $ $ 8 8 8 8 8 $ 1 1 $ $ $ $ $ $ e $ 8 $ $ 8 °c( 8 A 8 8 8 A A A a 8 a 8 8 8 8 8 B A a a A a A 8 9 A A a 6 A 8 8 AA A A A 8 A A A A 8 a B 8 . . . . . . .QQ .QQ .QQ .QQ .QQ .QQ .QQ .QQ .QQ. .QQ .QQ .QQ .QQ .pp .pp sspp .Q .QQ . -- .pp .pp -- .pp -- S- .qq ss -- .QQ .QQ b E. .QQ .QQ E E .QQ .QQ S S .Qp S E$g E E 8 e arban iarachlaride S g C S S 8 S g S S S S S$ S S S S 8 8 g 8$ S 8 S W P$ Q W M1bro(mm iS 8 C G oagI AOeBaaae oa8aa A _aas6 ao va_ s e m a E e e B e d z z z z _ e 8 a g e 8$ e B a 8 B e a 8 a n B n ry 8 B B B 8 8 a e BB e z a z a z z S B 8 8 e d 8 8 8 a z z gge g s =P!+�rv+••w �qn 8 8 8 8 8 8 8 e$$$ 8 8 8 8 z z z z gg 3 9 8 8 8 8 8 8 e 8 8 8 B e 9 8 3 9 9 6 6 8 e e 9 E 9 8 8 B 9 B B B 8 g g =�i<a�w4=!a-i• 8 8 8 8 S 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 z < g z z e = e s = e E s s g s s as< E =�•w�=^14=!Q-1.1 H S 8 H H B pp= 8 S QQe ey�e S, S �qe pe E E, pe ape E, E je E, 8 8 $E 8 8 8 y6 �qs'' S S Qs Q3 S b Qe Q3 S, S, p3 �1 E g 8 8 $$e 8 QQ pps S 8"$8s88�s"aa""s"s."8."8."ss."s.s-ss��s"8."s"s"s"a,"s. =��•4N^Ww=!,1-z,• "a, 'a 'spa"a. g g� z z 8 qn.0 m,.yc 9 8 g 8 8 8 8 8 8 g z °z z°$ 2 5 6 e 6 e a a e e e 9 8 e 8 9 9 a 9 9 9 e gg gg 8 e 8 'Eases==assesses $ $ $ $ $ $ $ $ $ $ pg $ 8 $ z z z z $ ses��sees ea a € s 2 in gg ggA A MIA A A 11 7� Lyt z g z gg g e 8 8 s 88 s "a. "s. 8. "s a s. "s, eeaeeaeeeeeeeea�asaee 8. 888 " 8 8 "ss. "s s. "s. "s. a s 's '8 "a. z z z z SeeBaaaaseeE 's s 8 8 8 8 8 8 8 8 S 8 8 8 8 8 8 8 8 z z z z g 0 8 8 a a g s s 9 a e e B$ i$ s a E S 9 6 3 B 9 B a z 8 z 8$ a e= S E a e B B 8 6 Q gg gg z z 3 5g $ b 0 0 o e o a 8 8 8 988 gg ss 8 2 8 8 8 8$ 8 a 8 8 8 8 z z z °z $ < a a o a o e g 8$ 8 8 8 8 8 8 8 8 8 8 8$ 8 8 8 gg 8 8 8$$ 8 8 8 8$ 8 8 8 gg 8 8$ z z z z a $ € s V w � iiv- Q � 5 j F A z Table 8 I : Analvtical Data for Groundwater User Specified Chemicals DSCA 11) No.: 920001 E 5 S E E L g E 2 3 2 Ea m ,L 11/1/95 NA NA N.4 ..005KND NA NA NA NA NA NA N:A NA NA NA NA NA 6196 NA NA NA 0.006 NA NA NA NA NA N.4 N{ NA NA NA NA NA .1. NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA � NA la.w NA NA NA NA N.\ NA NA NA NA NA NA NA NA NA NA 11 Sal- NA NA NA NA N.\ NA NA NA NA NA NA NA NA NA NA 11 ]29M ND ND NA NA ND .ND ND ND ND ND NA NA NA NA NA NA ND2/1r9H NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA NA NA NA NA 6121269H ND ND ND NA 0.0032 ND ND ND �'D ND ND NA NA NA NA NA NA ND I\ N-1 11- NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA IA UI/99 NA N.4 NA NA N.4 NA NA NA NA NA NA NA Nw NA NA M1A �'\ 6- NA N.A NA NA NA NA NA NA 11 NA NA N.{ IA NA NA NA NA NA NA IO- NA IA A 11 A NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA 311AHI NA NA N'A NA NA NA NA NA NA NA NA NA NA NA NA NA NA III- NA NA NA IA NA NA NA NA NA NA NA 11 11 N.\ NA A NA NA NA 41N1 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA H'13103 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 3r10.'OS .-I N.4 <0.0005 <0,0005 <0.0005 <0.0005 m.0005 m.0005 <0.0005 ©A005 ..-I ..-1 <OA005 m.0005 <0.000511 bb'06 m.0001 W.00M NA <U.0010 <0.0006 m.0008 I0'0.'O6 <O.000d �.000B NA <0.0006 <p.0006. <0.0001 <0.0006 N.0006 W.0001 W.0001 <0.0004 <0.0001 <0.0005 <0.0006 <0.0006 <0.0006 ®.000H N.0012 NA LN06 <0.0002 <O.000d NA <0.0003 <0.0003 <0.0002 <0.0003 10.0002 <0.0002 0.- <OA002 <0.0002 <.-I 10.0003 W.0005 W.0002 <0.0004 <0.0006 1.1 MW-ID 10'006 <0.0002 NA ­3 W 3 -0002 <0.0003 0.0002 <0.0002 <0.0002 -2 <0.0002 <0.0002 <o-2 N.0001 W.0006 NA Nm-2 11195 NA NA m..5 NA NA NA NA N. NA NA NA NA NA NA 11191 11 NA mA05 NA NA NA NA NN NA NA NA NA NA NA NA NA J 19t -.5 NA NA NA NA NA NA NA NA IA I I NA NA NA NA .I'. NA NA NA NA NA 11 NA NA NA NA 11 NA NA NA NA NA 121% NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 1219J NA NA NA NA 1:1 NA NA 11 NA NA NA I., I A 32Q'9'1 NA NA NA NA NA NA NA NA IA I NA I NA LIMB NA NA NA NA NA NA NA NA11 IA NA NA NA NA NA 11 NA NA 3'IM <0.005 <0.005 W.., <OA05 11NA <0.005 NA 11 11 NA <0.005 m.005 mow " N.\ NA ..01 19,0H 1 <0.005 NA NA m.005 NA NA 000133 W.005 <0.w5 NA N.1 \'A m.01 NA "/.IJ 10 <0.005 <0.005 <0.005 <0.005 NA NA <0.005 NA NA NA <0.005 <0.005 NM N.A N.4 m.01 NA 7 26 11 <p.5 <0.005 <0.005 7.5 NA NA -A �0? NA NA <0.005 <0.005 <0.W5 NA N:\ NA <0.01 NA 121U <0.005 woos 10005 m.005 NA NA -(f.0;i! NA NA <0..M NM5 <0.005 NA NA NA -1 NA Page 53 of 127 Table 8 1 : Analytical Data for Groundwater Ilser Specified Chemicals tUll DSCA ID No.: 920001 ga E 2 p E 9 m.I NA 1,01 NA NA NA NA NA NA NA NA NA NA NA Nw NA NA 11 NA 0.- NA NA NA NA NA NA NA NA NA NA NA NA NA NA M1A NA NA NA NA NA NA NA I NA NA NA NA NA NA NA NA IA 2- .\:\ NA NA NA NA N.4 NA NA IA NA NA NA NA NA NA NA NA NA 12497 NA NA NA NA NA NA I I NA NA NA NA NA NA NA NA NA NA NA NA NA IA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N.4 - - ND ND NA NA ND ND ND ND ND ND ND NA NA NA NA NA IA ND NA 2198 N:1 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 625-2698 ND ND NA ND ND ND ND ND ND ND 0.0 00000 NA NA NA ND NA N'1 NA NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA IA N'A NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA \:4 NA NA rv199 NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA Idl/59 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 3- NA NA NA NA NA NA NA NA NA NA NA NA NA N.4 NA NA NA M1A NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N.A N4 NA NA NA NA NA N.A NA NA NA NA NA NA NA NA NA NA NA<.M5 r�llll <D.W5 <0.0005 <0.0005 <0.0005 <0.0005 W.00p5 <00005 <00005 <00003 NA 0.W03 <0.0003 W.0002 W.0003 <0.0002 m.0002 <00002 <0.0002 <0.0802 <00002 <0.0003 <O.0005 <0.0002 N.000d <0.0006 NA -2 <O.OMJNA<0.0003 <0.0003 W.0002 <0.0003 0002 <0.0002 -2 <0.0002 <00002 <0.0002 <0.0003 <0.0002 <O W4 11111,16 NA I V193I I I NAO.O7i NA NA NA I I IA NA NA I I NA NA NA NA JJ 96 1 1 11 0.051 NA NA NA NA I NA NA NA N.\ Nk 11 NA NA IA NA NA N IN:\ NA 11 IA NA NA NA I I N:\ NA NA I I N.\ NA NA NA NA NA NA IA NA N.4 NA IN4 3R19'! NA NX NA NA N A \A NA NA NA N.4 NA NA NA NA NA N:\ NA )R097 ND ND NA NA ND\D ND ND ND ND ND NA NA NA N k 2/1/98 NA IA NA NA NA NA NA NA NA NA NA I NA I INA 0212698 ND ND NA ND ND ND ND ND ND ND 0.0018 UrM7 NA NA NA ND IA II20,98 NA N:4 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 11 NA NA NA NI NA N:\ NA NA NA NA \A NA NA NA NA NA 11 NA NA NA I I NA I I NA NA NA NA NA NA NA NA NA NA N.\ 11 NA NA NA NAKI....5 NA NA NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA LO NA NA NA NA NA NA NA NA NA NA 1'1/01 NA NA NA NA NA NA NA NA NA NA n05 W.W5 -.23 NA <0.0003 <00005 <0.0005 <0.0005 W.0005 <0.0005 "WI <00005 <00005 <0.0005 -5 <0.0005 <0.0005 IU8 W.005 -5 <0.005 <.M NA NA NA NA NA -5 m.W5 <0.005 NA NA A010 . W.005 <0.003 W.005 m.M NA NA N.4 NA NA m5 m.00s m.005 'A NA -01 NA 1111i/OB NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NI NA NA NA NA L5- <0005 W.003 W.005 <0.003 NA NA W..5 NA NA NA NA <0.003 -5 1 10.005 1 NA NA N.4 <0.01 NA 11\l-5 N}/0y <0.005 <0.005 -.s m.005 NA NA N.O05 NA NA 1.4 NA -5 W.005 N.005 NA NA \A <0.01 NA l is- <0005 <0.005 m005 - NA NA .05 NA NA NA NA m.003 'a.003 <0005 NA NA NA <0005 NA Idb/09 m.005 �.005 <0.005 -.5 NA NA m.005 NA IA NA NA m.005 -3 <0.005 NA NA NA <001 NA W.10 .005 -.1 <0.005 <0.005 NA NA WM5 NA NA NA NA c0.005 <0.005 <0..5 NA I NA m.01 NA M10 <0.003 <0.005 <0.003 <0.005 NA NA <0.005 NA NA NA NA W005 N.005. <0005 NA N'l NA <..01 NA 71112 <0005 c0005 <0.005 <0.005 NA NA m.005 NA NA NA NA <0005 <O.W5 W.005 NA NA El NA 102010 -0.005 <0.005 -5 <0005 NA NA -W5 NA NA NA NA ., -.5 �.003 NA NA NA m.01 NA 7/ 111 0005 0.00233 <0.005 -.1 NA NA A.005 NA NA NA NA W005 <0.005 <0.005 NA NA NA m.01 NA V26/12 �0005 -5 <0.005 <0005 NA. NA <.M NA NA NA NA <0005 10003 W.005 NA NA NA <0.01 NA 7-12 0.005 W.005 W-5 'DA05 NA NA m.005 NA NA NA m.003 m.005 W.003 NA NA NA NA NA ill2&12 0005 -5 W.005 <0.005 NA NA A.005 NA A NA NA <0005 <0.005 NA NA N.01 NA 727/13 0.005 m.M <.M 4.005 NA NA -.5 NA NA NA NA m005 W.005 <0.00S N:A NA m.01 IA 5.30'1? 0ms <0.005 <0.005 <0.005 NA NA 10.005 NA NA NA NA m.00s <0.005 W.003 NA I I NA .01 0.ms W.005 N005 W005 NA NA <0.005 NA NA NA NA W..5 .W5 <.Ws NA I I NA <0.01 <0003 <0.005 <0.005 m.005 NA NA -1 NA NA NA NA W003 W.005 �.005 NA NANA W01 NA A.00050 <0.0050 <."m <0.00/0 <0.0010 m.0010 -.10 �.Mw W.00m m.0010 `wlo ..-. W.0010 m00m A.0010 181J <0.00050 <0.0050 <0,-50 W.0010 <0.0010 <0.0010 <0.0003 <0.0010 <0.0010 m.00s0 mA to <0.0030 c0.00m �.0010 c0.0010 <0000m m.0010 <O.00m <0.0010 21I4 <0.00050 <0.0030 <0."SO co.0I0 -mlo <.Wlo W.0003 -mlo <00010 <0..m <0.0010 <O.00m <O.00m m.0010 <0.0010 c0.00050 <D.0010 -w" <00010 121811 c0.00050 <0.0p50 N.00050 <O.00b m.0010 �.0010 <0.00030 .0010 m..1. a.w" <0.0010 moom W.00m W.0010 c0.0010 c0.o0050 <0.0012 �.00m <0.0010 dMls A00050 <0.0050 N.00030 m.0010 W 0 <D.Wlo <0.0 % -mlo m0010 <0.0030 W.0010 m.00m <O.00m m.0010 m.0020 <0.00050 <0.0010 <O.00m N.0010 d1v1s <o.000w rn.eo3o a.aaoso m.aow m.aolo <oao2a a.aoow m.aola <o.00lo <o.aow <o.aolo rnoom m.aom a.00la amlo m.aooso <omlo <oarto a.00lo Page 54 of 127 Table 8 ] : Analytical Data for Groundwater ltser Specified Chemicals 1 DSCA ID No.: 920001 e 73 9 e' z it e 9 8 E r gE 11/195 'A NA I 1 -0.005 NA NA NA NA NA NA NA NA NA NA NA NA NA NA h1\\-1 NA NA 0.016 NA NA NA NA NA NA NA NA NA NA NA NA NA NA VV96 NA NA NA NA NA NA NA NA N'A NA NA NA NA NA NA NA NA NA 11'INS NA NA 1 0.028 NA NA NA NA NA NA NA NA NA NA NA NA NA NA d'M NA NA 1 •-0.005 NA NA NA NA NA NA NA NA NA NA NA NA NA ''A NA NA I., NA NA NA NA NA NA I., NA NA NA NA NA NA NA NA 11 NA NA NA NA NA IA NA NA NA NA NA NA NA N.A NA NA NA I-1 N:\ NA NA NA NA NA NA IA I I NA NA NA NA I I NA NA NA NA 37197 \:\ NA NA NA NA NA NA NA 11 NA NA NA NA NA I NA NA 729:97 ND Nil NA NA ND ND ND ND ND ND ND NA NA NA N:\ ND NA 711198 NA NA NA NA NA NA NA S:A NA NA NA NA NA I I NA M1:\ NA NA 6:25-26.98 ND ND NU NA ND ND ND ND ND ND 0.0009 NA I I NA NA NA ND NA 1120.'98 NA NA NA NA NA NA NA NA NA NA NA NA NA I NA NA NA NA NA w� NA NA NA NA NA NA NA NA NA NA NA NA I NA NA NA NA NA Ill -7 6/1r99 NA NA N'A NA NA NA NA \A NA NA NA NA NA I I NA NA NA NA NA 10/IN9 NA NA N'.{ I NA NA NA I NI I I NA NA NA NA NA NA NA NA 3/1/00 NA NI NA I NA NA NA NA NA NA NA NA NA NA NA NA NA IW- NA Ix NA NA NA NA NA NA NA NA NA NA NA NA NA V1N1 NA NA NA NA NA NA I I I NA NA NA NA NA NI NA NA 0.0025 NA NA V13J03 NA NA NA NA NA NA NA NA NA NA NA NA NA N:{ NA NA NA NA NA 3,1005 <0.0005 <0.0025 NA <00005 <0.0005 <0.0005 <0-1 <0.0005 <0 3 40.0005 <0-1 <O 1 <O,wl 0.0005 <0.0005 W.0005 <OA005 <00005 NA 2606 <OA002 -0006 NA <0.0003 W.0003 <O.00D2 <O- -0002 <0.0002 -0002 <0.0002 N.0002 W.0002 <00003 m-1 <OA002 O.000l m.0006 NA 1212'07 <0005 m.005 <0005 <0.005 NA NA <0.003 I NA "'I <0.003 <0005 <0.005 NA NA W.01 NA 6'17:08 <0.005 <0.005 1 0 0.005 NA I NA c0.003 NA z0A05 -005 <0005 NA NA NA <0.01 NA 71609 <0.005 0.001 - <OA05 NA NA <0.003 1 1 NA IA NA <0.005 <0.005 <0005 NA NA NA <OOl NA 2310 <0.005 <0.005 <0- <0ws NA NA <0."5 NA NA NA NA -5 <0.005 <0005 NA NA NA <0.01 NA 7,1 TO <O.ODS <0.003 -0005 <0.005 NA NA W.005 NA NA NA NA <A.ODS 10.005 M5 NA NA N.A <0.01 NA 3111N7 O.BOi9 NA NA NA NA NA U71 0.001< 0.0012 0.0021 0.0021 NA N:{ 11 NA NA NA NA N.{ NA 11 11 NA NA NA NA 00017 D.W24 0.0023 NA NA I I I NA NA NA NA NA ND NIl NA NA ND ND ND ND ND ND NET ND IT, IT, - ND NET ND 2198 ND III NA NA ND 0.0009 ND ND ND ND ND ND ND ND ND ND NA 6'25-2698 ND NA NA 0.0013 ND ND NET ND ND ND ND ND ND ND ND ND NA 112098 ND NA NA NA 0.0013 ND ND ND ND ND NET ND ND ND ND ND \1l NA 8- ND NA NA NA 0.0013 ND ND ND ND ND ND ND ND \Il ND ND NA 6199 ND NA NA NA 0... 0.0007 ND ND 0.0026 ND ND ND ND ND ND ND -1 1 NA 10:199 ND NA NA NA ND ND ND ND ND ND ND ND ND ND ND ND \A NA 1I 4A 311:00 ND NA NA NA ND ND ND ND ND ND ND Np ND ND ND ND ND I NA NA IVI'00 ND NA NA NA ND ND ND ND ND ND ND ND ND NU ND ND ND NA NA VIN1 11) NANA NA ND ND ND I ND ND ND ND ND ND ND ND ND ND NA NA 311315 0DDO5 <0.25 NA 0.0006 <O.0005 <0.0005 <O.ODOS <o 0., -0.0005 W.0003 <0.0005 W.0003 <0.0003 <0.0005 <O.00DS <Olw5 NA IV1310] <0.005 <0005 NA <OA05 NA NA m.005 NA NA NA ­5 <0.0p5 A.O05 NA NA NA O.Ol NA 6117108 <0.003 <0.005 N.005 <0..5 NA NA <0.005 NA Ijk <0.005 NA NA NA <O.01 NA ]/IN09 <O.00S <0.005 <0.005 <0.003 NA NA <0.005 NA NA N:\ m.005 c0.005 <0.005 NA NA NA W.01 NA ]A/10 <0.003 N.005 <0.003 <0.005 NA NA <0.003 NA NA NA -1 10.005 <0.005 NA NA NA <0.Ol NA 71-0 <0.005 c0..1 -5 <0.005 NA NA �.005 NA NA ..003 W.005 <0.005 NA NA NA m.04;4�1 N AR6'11 <O.UO3 0.0009'S1 <0.005 m.005 NA NA m.005 NA NA <U.005 m.005 c0.003 NA NA NA <q.0IN]/ll <0.003 <0.w5 -5 <0.003 NA NA m.001 �NA NA NA NA <0.005 W.005 <0.005 NA NA NA <p.0 Page 55 of 127 Table 8 1 : Analvtical Data for Groundwater User Specified Chemicals 1 DSCA ID No.: 920001 g fip _ E � E iE E 2 - - E 41% NA NA NA W.OoS NA NAINA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA IA N.A NANA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 12- NA NA NA NA NA NA NA NA NA NA NA NA NA N:\ NA NA NA NA 3209'/ NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 7/ ND ND NA NA ND ND ND ND ND NA NA NA NA NA ND NA v- NA NA N.A NA NA NA NA N:4 NA NA NA N':4 NA NA NA NA NA 625-2698 ND ND ND IA ND ND ND NU "I ND ND 0.0008 NA NA NA NA NA ND 1130.98 NA NA NA N:\ NA NA NA NA I I N.A NA NA NA NA NA NA NA NA d'1'99 NA I k NA N'A NA NA NA I I NA NA NA NA NA NA NA NA NA NA 6199 NA "A NA NA NA NA NA NA I N.4 NA NA NA NA NA NA NA NA NA 0199 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 31 Do NA NA NA NA NA NA 0.V N.4 NA NA NA NA NA NA NA NA 101100 N:\ NA IA NA N.4 NA NA IA 11 NI NA NA NA NA NA IA NA NA NA ID1 N.A NA NA NA NA NA NA NA NA NA NA NA NA NA N.1 NA NA NA 0OS W.0003 <0.0025 NA <.-1 <00005 W.0005RNA W.0005 W.0005 W,0005 <o0005 W.0005 W.0005 W.0005 W03 <0.0005 W.00Df W.0005 NA 10J06 <0.003 <0.006 NA 10 1 'o-1 W.003 W.003 <OA03 W.003 W.003 W.003 <O.M5 WA075 <0.003 <0.006 W.m NA 3 1 n) W.Od W.2 W.W 10.04 W.01 W.Od W.OJ <o of <0,04 �.01 <0.01 W.od WAd W.. W.Od W.Od 121-7 W.005 W.003 <O005 W.ODS NA NA NA NA NA W.005 W.M W.005 W.005 NA NA W..1 11 6 17 08 W.005 <0.005 <0.005 <0.005 NA NA NA N'4 N:4 e0.005 <I'm W.005 NA NA NA WAi NA 11 IIios NA NA NA NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NA I I I I NA W.005 <0.003 .NA NA W.01 NA dl2/09 <0.0p3 <0.005 W.005 NA NA W.005 NA NA NA NA <o.1 W.005 o.005 <O.OUS NA W.01 NA ]�IW09 <0.005 <p.005 <OOOOS NA NA 1OA05 NA NA NA NA <oW5 W.005 W.003 <0 W:I NA W.01 NA 9'15/09 <0005 o-v W.005 W.W5 NA NA W.005 NA NA NA NA <0.005 W.005 W.003 <0.005 1 NA <p,01 NA loll. <OA05 W.005 W.005 <0.005 NA NA <0.005 NA NA NA NA W.003 WA05 ­5 NA NA <0.01 NA v- Lows W.005 <0.005 WA05 NA NA 1OA05 NA NA NA NA W.005 W- W.005 NA NA NA W.01 41110 0.005 WA05 W.- WA !I N'A NA W.005 NA NA NA NA W.005 W.ODS W.005 NA NA NA <OM 11,11 'o'w5 WDOS W.00I WA05 NA NA <OA05 NA NA NA NA -W5 W005. W.OD5 NA NA cO.OI <O.W5 WAGS - 4.005 IA NA W.W5 I I NA NA NA WA05 WA05 4.005 NA NA I I -I 42111 W.005 .-v D.W5 W.005 NA NA W.005 1 1 NA N.4 11 -5 WA05 W.005 NA NA NA 112'll W.ws WA05 W005 W.005 NA N.4 W.0051.1 NA NA 11 4D05 W.005 <0.005 NA NA NA <001 NA 719/12 W.005 W.005 WA03 W.005 NA NA W.005 NA NA NA NA 4.005 W.005 <0.005 NA NA NA W.o1 IY3/12 W.003 WAOS W005 W.005 NA NA WAGS .NA NA NA N.4 WW5 <0.005 <o..1 NA NA NA WAI 22- W.005 W.005 <OA05 <0.M NA NA m.005 NA NA NA NA -5 W.005 c0005 NA NA NA -,I 5:30i 13 W.005 WM!l <0.005. W.005 NA NA W..5 NA NA NA NA W.005 W.005 WA03 NA NA NA W.01 911113 W,005 W.005 W.005 <0.005 NA NA W.005 NA NA NA NA WM!` <o005 <O.00S NA NA NA W.01 NA I vll, W.005 WA05 c0" <0005 NA NA I.- NA NA NA NA W.005 <0.005 WAO! NA NA NA W.Dl NA 375114 W,00050 W.0050 <0.00050 NA <0.0010 W.0010 W.00050 W-o WD010 W00 .5o W.wlo WA020 c0.0020 ...I. ..mt. W.00050 W.0010 W... W.0010 6'IA'Id W.0010 W.010 W.0010 -so own -w. <0.001 M. c0.ww <0.010 W.00215 Oslo W.0010 <00020 W.o020 WA010 4A020 W.O010 W.0020 W23/14 W.00050 WA050 W.00050 <0.010 W.0010 W.0010 <OA005 W..Io W.ODIO WAO10 <O.wlo W.002D W.0020 W.WIO -I. <p.m" W-o W.0020 W..I. IwI6/I4 W.0020 WA20 W.MM <0,016 0.00d0 -0040 0.002D W.00dO W.ODdO 4.0040 <0.0p10 W.0080 W.ODBO <0 OOd0 W.00/0 W.0020 W.00dO W.0080 W.00dO KIWI! W.00050 W.0050 <0.00050 W,W4D WIWIO W0010 WAOOSO W.0010 W..1. <0.0050 <o.mlo -so W.00L1 W.0010 W.00'20 <0.00050 W.0010 W.ODZO <0.0010 6'17115 W.00IO <0.0010 <0010 <00080 W.0020 W.0020 W.0p10 W.0030 W.0020 W,DD20 <0.0030 W.00dO W.00dO W.0020 W.0020 W.0010 W.0020 O.00IdI <00020 Page 56 of 127 - «_,_l,,,,,, _l,l,; _- „ _,>__! „ _ „ > „ z,z „ !,!l,=,,,,,,==,t� „ , --|!!§l �,!«, ;zl, = ,,,,,l;====,_z - ,�||!■ ,,,,,,,,,,,,, - _ l,,,=,_::;,,,�� ,!l,=,,,l::JJ:;§§§|||§||§ --- ,2=I=»==>;}\/!_l==== „! „ =;,T==,==_§{ " " `®' _--m „ r,l,l,,,,,,§§) " " '� y =_ �\ __,! -- „ I■� „ !==§t§ -�, - ® ==;;Exx>=:===|■I§■§!;,§ / ,_ .__•ST „ §tt�„ :,_, / ,,,,,,,,�|�,! © _=e „ =,==i====®=i=§§§»,:::__ ƒ „ _,__,_,,,,,,§§§§§t)t�� ©®z H „ ;=,I,=,,,,���!!!§ _z =f,=:l:== „ - „ =I.,,,,,,,,=rr <<|||§§;§§§§ - ; e � c Table 8 1 : Analytical Data for Groundwater laser Specified Chemicals t DSCA TD No.: 920001 fi E E 2 a - 12157 NA NA NA NA NA NA NA NA NA NA N:\ 11 NA NA NA NA NA NA NA 11 Om- NA NANNA 00012 0.o011 0.0000 0.0000 ND ND 0.wl NA NA NA NA NA NA NA NA ' ND ND NA ND ND ND O.oO(4 ND ND ND NA NA NA NA NA NA ND NA 2198 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 625-2690 ND ND ND0.02A5 ND ND ND ND ND ND NA NA NA NA NA NA ND NA 1124) NA N.A NA NA N.A N:A NA N.A NA NA NA NA NA NA NA NA NA- NA NA NA NA NA NA NA NA NA NA N.A NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Ip199 NA NA NA ''A N.4 N.4kNA NA NA NA NA NA NA NA NA NA NA 31o0 NA NA NA N:\ NA NA NA NA NA NA NA NA NANA NA NA N':\ NA N.A NA NA NA NANA N.{ NA NA M1A N.ANA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA OS w.m5 w.0023 NA <0.0005 <0.0005 <0.0005 'o-5 w.0005 w.0005 w.0005 w.0005 <00"s w.0o05 w.0o05 -0005 w.0005w.0005 NA w.0002 w.0001 NA <00003 <0.0003 w.0002 <OA002 c0.0002 w.0002 w.0002 c00002 w.0002 w.M3 <00005 10.0002 <0.0009 0,00(K NA 311M <o.005 w.005 w.00� 0.00s NA NA <0o05 NA NA NA NA c0.005 <0.003 <o.005 NA NA NA w.01 NA A9No w.005 -1 0.005 NA NA <0005 NA NA NA NA o.- w.0p5 w.005 N-A NA NA w.01 N.4 1/1A'09 w.005 wA05 <OM5 w.o05 NA NA w..5 NA NA NA NA wo05 w.003 w..5 11 NA NA w.01 NI 1o"09 w.005 <0005 w.005 w.o05 NA NA ,-0005 NA NA NA NA w.005 <OM5 wM 11 NA NA w.01 NA 2'4'10 <0.005 w.003 o-5 w.005 N.\ NA 11.5 NA NA NA NA w.005 <OA05 w.005 NA NA wn1 NA {2110 w.005 w.005 w.005 w.003 NA NA <0.005 NA NA NA NA <0005 w.005 w.005 NA NA NA 713.10 w.w5 -m w.005 w.o03 NA w.005 NA NA NA NA <OM5 <0.005 w.005 NA NA NA w.01 NA 1020: 10 <0.005 w.o05 w.005 w.005 11 NA w.003 NA NA NA NA 0005 10.005 w.005 NA NA NA w.01 NA 4'2N11 <0.005 1 0.000915 w.005 woos NA <0.005 NA NA NA NA -.1 w.005 NA NA NA w.01 NA 72611 <0005 -1 w.005 w.005 NA NA w.005 NA NA NA NA 1A NA NA -01 NA 111 0.005 w.003 -5 w.005 NA wo05 'NA NA NA NA <0.005 10.005 0.003 NA NA NA -01 NA 12512 <0.o05 <p.005 w.005 w.003 NA NA <o s NA NA NA NA -5 c0.00] w.005 NA NA NA w.01 NA 21112 0.005 <0.005 <OM w.0o5 NA NA <0.005 NA NA NA NA w.005 w.003 w.005 NA IA NA 0.01 NA 312 w.005 -005 <o005 w.005 NA N.A NA NA NA NA NA <OM <o005 w.005 NA I NA w.01 NA 2713 w.005 W.005 --00p5 w.005 NA NA 0005 NA NA NA NA w.o05 w.00] - ..m NA NA w.01 NA 2913 w.o05 10.005 <0005 w.005 NARNA<0.005 NA NA NA NA w.005 w.005 w.005 NA w.01 NA 1211 w.005 ..005 <0.005 w.005 NAw.o05 NA NA NA NA w005 w.005 �0M NA w.01 NA 1313 w.005 w,005 <o- w.005 NAw.005 NA NA NA NA <OM5 w.005 w.005 NA NA NA w.01 NA 2114 w.000]0 w.0p50 w0-50 NA w..to w.00050 w.0010 w.0010 w.wso wM. -002o <0o020 w.0010 w.0010 w.0003o w..to w.o020 w.0010 617/u w.000]0 w.0050 <o.00050 w.00J0 w.0010 w.0003 w0010 <0.0020 w.00% w.0010 w.0020 <0.0020 w.0010 w.0010 w.00030 w.0010 w.0020 w.N.o 92511{ <o.00030 m.0p50 <o.0005o w.010 w.0010 w.o005 wo- -to w.0o50 w.0010 c0.0020 <0.0020 w.0010 w.0010 w.000m <o-o w.0020 w.00to M&M w.00050 w.0050 -00050 w.00b <Omlo w.00050 w.0010 w.0010 w.Oom `S-o w.0020 <0.0020 w.0010 w.00t0 w.00050 w.o010 w.o020 w.0010 w.00050 w.00.w.0050 w.w to w,Wo 19MI0 w.0010 w.0030 w.0010 <p oo2o w.00zo w.0010 w.0020 w.000s0 w.0010 <0.0020 w.0o10 tums w.00050 m.005o w.00D50 <o.00A0 w.o010 w.o010 'o.0005o w.0010 w.0020 w.0p]0 <0.0010 w.0020 w.0020 w,wlo w.0010 w.0o10 w.0010 too" w.00Ip Page 58 of 127 Table 8 1 : Analvtical Data for Groundwater laser Specified Chemicals I DSCA ID No.: . 920001 12.w NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 3121197 00034 NA NA NA ND ND ND ND ND ND ND NA N:\ N INA NA NA NA 71&97 ND ND NA NA ND ND ND ND ND ND ND IA NA NA NA NA _ NA ND Im N:\ N:\ NA NA NA NA NA NA NA NA NA NA NA. NA NA NA NA NA NA 42iM . 0.- ND ND NA ND ND ND ND ND ND ND NA NA N1 NA NA NA ND NA NA NA NANA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA NA NA NA 1119 NA N.4 N NA NA 0.0006 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA U. NA NA VA NA N.4 NA NA NA NA NA NA NA NA NA NA NA 101IOD NA N:\ NA NA N.A N.A NA NA NA NA NA NA NA NA NA NA 4IN01 NA NA NA NA NA NA NA NA NA NA NA NA NA UM3 LNA NA NA NA NA NA NA NA NA NA NA NA NA NANA N0005 N.0005 N0005 N0005 W.0005 N0005 N.OD05 N.0005 <0.0005 <0.0005 <O.OD05 N0005 <0.0005 NM5 N 5 <0.0001 NA N.0003 <0.0003 W.0002 <0.0003 W.0002 N0002 N0002 N 2 <0.0002 <0.0002 <0.0003 W.00D5 <00002 W.0004 NA00uw.. . <0.0004 NA N0003 <0000J W.0002 <0.0003 <0.0002 W.0002 <0.0002 <0.0012 <0.0002 <0.0003 N.0005 <00002 <0.0000 N.0006 NA 10/U06 N0002 <0.0004 NA N.M3 -Wl c0.0002P<'.N-A' <0.0002 <0.0002 <0.0002 <O.UW2 <0.0002 <0.0002 <0.0003 W.00D2 N.M2 N.0001 N.0006 NA 10/U06 <0.0002 N.0004 NA <0.0003 <O.000J W.0002 c00002 W.0002 W.0002 W.0003KN-A W.0002 <0.0003 W.OD02 N.0002 N.0000 <0.0006 NA 311M <0.005 N.005 <0.005 <0.005 NA NA NA NA NA NA NO% NA NA <0.01 NA W.& <0.003 <0.w5 <0005 <0.005 NANA NA NA NA<0.005<0005NA IA <0.01 NA I lnil. NA NA N.A NA NA NA NA NA NA NA NA NA NA NA NA v- N.003 N.005 <0.005 <0.005 11 NA NA NA N.A NAN.005 -5 NA NA N.01 NA - WA25 N.025 <0.025 <0.023 NA NA NA NA NA N025 <0025 NA NA -05 NA 714'09 <0.005 N.005 <OA05 <0.005 1.\ NA <0.w5 NA NA NA N'.\<0.005 <0..1 NA NA NA N.01 NA 1-09 N.005 N.003 - 1 <0.005 11 NA N.005 NA NA NA NA <0005 m..5 c0..1 NA I 1 -1 NA 2410 <0.005 -5 <OA05 N.O03 11 NA -.5 NA NA NA NA W.m5 <0.005 <O.00JNA NA I N.01 NA 42110 <OA05 N.005 N.005 <p,005 tit NA W.005 NA NA N I NA <0.003 <0.005 <0.00] NA NA NA N.01 NA 71410 <0.005 N.003 NM N.005 NA NA <0.005 NA NA I N'.\ <0.005 <0.005 W.005 NA NA NA N.01 NA 1020. 10 N.005 N.005 NOD5 N.M NA NA <0.005 NA N I NA NA NODS <O.OD5 <0.003 NA NA NA <0.01 NA 4Z611 N.005 0.000941 -1 <0.003 NA NA <0.005 NA NA -.DOS N005 N005 161 NA NA - NA 72611 N.005 0.000941 N005 <0.005 N.4 NA -m NA 11 NA NA m..5 NW <0..3 N:\ NA NA N.01 NA 11-1 -5 1 N005 <0.M NA NA <OA05 N> 11 NA NA <O05 N.005 <0.m N:\ NA NA N.01 - 12512 N.005 N.005 - 1 <0.005 NA NA W..3 NA 11 A NA NODS m.005 <0.005 NA NA NA N.01 NA 72012 NM5 N005 NOO5 <O.005 NA NA <ODOS NN I I NA NA W.M5 W..5 <0.005 NA NA NA -1 NA 12312 <0005 N.005 <0.005 <o.005 NA NA <0.005 NA NA NA NA N..5 4.005 <0.005 NA NA NA - NA 22713 <0.005 N005 <0.005 -005 NA NA 10.005 NA NA. NA NA N005 4.005 N005 NA NA NA N.01 NA 53113 N.005 -251 <0.005 <0.003 NA NA 4A0311 NA NA NA N005 4.003 <0005 NA NA NA N.01 NA 9.12113 NM =5 4A05 <0005 NA NA c0.005 N1 NA NA NA �M5 N003 c0.005 NA NA NA 4.01 NA IN13113 <0.005 N.M5 <0.005 <0.005 NA NA 4.005 NA NA NA NA a.m <0.W5 <0.005 NA NA NA N.01 NA 3r27114 W.00050 -mm <0.00050 <0.0040 N.wlo <0.0010 -wm <0.0010 <0.00I0 <0.wm <0.0010 N.m ICON <0.0010 4.00050 <O.00030 4.0010 N.0020 �.0010 ml, <00010 N.010 <0.0010 <0 ww -w0 m.O020 <0.0010 N.00ZO c0.0020 -W N.0020 N0010 M.0010 4.w0 N.0020 <aw.0 W.0020 �.0040 -10 NIU14 -.10 4.010 <0.0010 <OA040 <oMN -wN N.O01 N.WZO <0.0020 W.010 ..wN 4.01 N.00/0 c0.00fi N.00Z0 <0.0010 W.0020 m.0040 <0.0010 915114 m.00030 Nmw. <D.00050 <0.010 <OA010 N.O010 <0.0003 m.M10 W.0010 <00050 W.0010 N0030 W.0020 m.00I0 N.0010 <000050 <0.0010 W.0020 �.0010 I Z/M4 <0.0010 N.010 <0.0010 <0.0080 -mm <0.0020 <O.00ID <0.0030 <q,0020 <0.010 <0.0020 N.0040 N.0040 c0.0020 N.0020 <0.0010 4.OD10 <0.0040 N0010 3]OIIS NA010 <0010 .W0 <0.0010 N.0040 <0.0020 W.010 NOOfi N.0010 W.0010 �.00E) N.0020 W.0010 N.0020 N.0610 <0.0029 61U13 W.00030 N0p50 N.00050 <0.0040 N.0010 N.0010 c0.00050 N.0010 <O.wm N.O050 NOD10 N.0020 a.0020 m.0010 N.O010 W.00IO -WIO N.0020 N0010 Page 59 of 127 Table 8 ] : Analytical Data for Groundwater User Specified Chemicals 1 DSCA ID No.: 920001 e € mti I12U0] NA VA NA NA NA NA NA NA NA NA NA NA NA NA N.{ NA 342U9-I ND NA ND ND ND ND ND ND NA NA - NA NA NA NA NA 71,W I ND ND ND ND ND ND ND ND NA NA NA NA NA ND NA VM NA NA NA IND NA NA NA NA NA NA NA NA NA NA NA NA NA 025-2 R O.WB'1 ND ND 0.001 ND ND ND ND ND NA NA NA NA NA NA ND NA IV2008 NA NA NA NA N:{ NA NA NA NA NA NA NA NA NA NA UI'99 �:\ NA NA NA M1'.{ !:.{ NA NA NA N.{ NA NA NA NA NA NA 0'V9 NA OA03 N:\ N.{ NA NA NA NA NA NA NA NA NA NA I0'I- NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0l- N.4 NA NA NA NA NA NA NA NA NA NA 'A NA NA I I A NA I01/00 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0001 NA NA NA NA NA N:\ NA NA NA NA NA NA NA NA NA NA V13ro3 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 31111U1 <0.0005 m.0025 NA <0.0005 <00003 <00005 <0.0005 <DA005 1OA005 -1 <OA005 -5 ­5 <OA005 m.0005 <0.0005 W.0003 <0.0005 2/b06 <0.0002 c0.0004 NA <0.0003 <0.0003 <00002 109-1 10.0002 c0A002 W.0002 -t0)2 <0.0002 <0.0002 <00003 WS <0.W2 --1 <0.0000 1:1 12/1 iro] <0.005 U05 <0.0115 <0.003 NA NA <0.005 N:\ NA NA NA <0M <0005 10.005 <0.005 NA NA c0.01 NA 01]ro0 <0,Ms <0.005 W.005 <0.005 NA NA <0.005 NA NA NA NA <O.00S <O.WS <0.005 NA NA \A -01 NA I Ir11roB NA NA NA NA NA NA NA 11 NA NA NA NA NA NA NA NA NA NA NA YU09 <0.003 <0005 W.005 W.005 NA NA -0.003 NA NA NA NA <OA05 m.005 c0.003 NA NA NA -1 NA UL09 <O.W5 <OA05 <0:003 <0.005 NA IA -119.1 N.{ NA NA NA <0.005 <0.003 <OA05 NA N.{ NA W.01 NA T.- <0D05 <0.005 -I <.M NA NA Owl NA NA NA NA <0.005 <0.005 c0.005 NA I., NA 10.01 NA 10]ro9 <OA05 <01105 <0.005 00.005 NA IA 0.003 N A NA NA IA<0.005 <p.005 c0.005 \-A -01 NA 2J 10 <0005 c0.005 W.005 <0005 NA NA -AWS NA NA NA NA <0.003 -I 1OA03 NA 1.1 NA <0.01 NA 0.005 c0.005 <0.003 0.0p3 NA NA <OA05 -NA NA NA NA <0.005 <0.005 <,m NA N X NA N01 N:{ ] Ii. 10 <0.003 W.005 W.005 <0a03 NA NA W W5 NA NA NA NA <0.005 O.005 <0.0p5 IA NA NA 1001 1021r10 -5 0.005 N.005 <0.003 NA NA W.W5 NA NA <0.005 <p.005 <0.005IA NA NA <001 42611 <OA05 OA0263a WA03 N.WS NA NA W.005 NA NA IA NA <O.M W.005 <0.005 NA NA <001 NA <O.M 0.002J1 <0.003 <0.005 NA NA <OA05 NA N:\ NA NA 0.ww <0.005 <0.005 NA NA -01 IA I11 <OA05 :-1 -5 WM5 NA NA m.005 NA NA NA NA <0005 <0.005 c0,003 NA NA NA <001 IA 12 <0.005 <0.005 <0.005 <0.005 NA NA <OA05 NA NA NA -.003 <0,005 W.00311 NA NA -01 NA 71012 <0.005 c0.005 WAW W.005 NA NA OAS NA NA ..5 NA NA NA WAI NA 123'12 <0.003 c-5 <0005 W.WS NA NA W.005 NA NA NA NA<0.005 W.003 <0.005 N:{ NA NA W.Ol N'A 13, 0..1 <O.ODS m..5 W.005 NA NA NW5 NA NA NA NA<D.005 <0.W5 <0.005161 NA NA <O.OI NA - <0003 N.005 A.005 <0.005 NA NA <0.Ms NA NA NA NA W.005 W.005 <0.0p5I., NA NA <0.01 NA <0.005 <0.005 <0.005 <0005 NA NA ..005 NA NA I., NA <OA05 <0.005 NA NA ®.01 NA 1211'13 <0.005 10005 d1.005 <0.005 NA NA -1 IA NA I I NA -1 <0.005 ODUS NA NA NA <0.01 NA ?2614 <0.00050 <0 M. W.00050 NA <0.0010 m.0010 W.00010 �.0010 m.0010 <0.0030 <0.0010 <0.0020 <0.0020 <0.0010 <OA010 <0,00030 <0,0010 c0.0O20 <00010 c000050 ..0050 <0.00050 0.00JO <l)MIO <0.0030 U.0005 W.0010 <0.0010 m.0050 W.0010 OA050 c0.0020 <00010 WA010 <0.00050 W.0010 <D-m m.00t0 <0.00050 N0050 <0.00050 <0.010 <p_p010 <0.0010 <0.0005 W.0010 <0-0 <0.0050 <00010 <0.0020 W.0020 <00010 <0.0010 <0.-1. WA010 <OA020 c0.00t0 c0.00050 N0030 <ll.0005. <O.00JO <00010 <OA010 <0.00050 W.0010 <0.0010 <0.0050 <0.0010 <D.0020 <0.0020 <00010 <0.0010 <0.00050 <O.00IO <0.0020 <0.0010 m.00p30 <0.0050 <..w5o <O OOJO <0.0010 <OAOIO <0.Ww m.0010 .-0 c0.0050 <0.0010 <0.0020 <0.0020 <0.0010 W.0020 NDOONI <0.0010 <0.0020 <0.0010 <O.000Sp N0050 <0,00050 <O OOJO <00010 <OA010 <O.000NI -0010 W.0020 <0.0050 �.0010 <0.0020 <0,0020 <0.0010 m.0010 �.0010 W.0010 <0.0020 <0.0010 Page 60 of 127 LZ I la 19 a3-d i.. 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QB Q� 4 4 qp 44 E E z z Z X z z z z z z Z z z z z z Ya Z a????? p9 QB Q8 QB aseeee eseses z< z z z < x x a < z z a < z z < < z z < z x < a z z ! < z z 'g g g g g 'g G < < < ¢ a z z s e z z < < z z < < z z < < z z < a z z < g z g 'g 'g 'g 'g B B B B B E g 8 B E B E Baa S 8 E ,u•ypwaoq�o.gyou 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 S 8 8 8 8 8 8$ 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 < x e e E s a e e a e a s E e e a e s e s e e a e e s e e e e e e s e e e a e s a e= e s E s e a s s s �aeeEeE eaeeeeaeesees esessE eeeESEese auzvgpn9 < < z z < z z ¢ z z t 6 z z < < z z 8e $ g g 8 g z a < z z < z z z < z < z z < < z z < g z 8 $ $ $ $ < z B' B 8 B e e 9 9 8 9 au,z",gaory,ulEY•� E a zzx < a z Izz<t880 z z x z z z z x z 8 8<e<aza<zQa <<zaa<8 z z < B E B e z z z z. z. z z z z x z e 5 B 9 B E ,w,.w,go,gyq,lyz•� z z z 8 8 8 8=1. z z z z 8 8 8 8 8 8 e e e e Z z z z z z Z z z Z` z z$$= a$ s < z z z< z z z z z<<< z z z z z$ 8$$ H$ B B 8 B 8 B B B E B B 8 E < x nwy,auw,gy,owwgi g g • z u •�•WlgWwwl f•C a z < a z z < z z z < < < < < < < Z x < 6 Z Z < z Z < < Z Z $ $ g 8 $ $ 6 6 x Z z Z z z < z z < 6 6 < ! < 6 < < $ 8 8 8 8 g 4 'u a e o 0 9 z Z z Z z Z z z z e a e •n%N•91•�4�•aw10Y•� 6<<< z z x z 6 6 z z z z< t :. 6< z z 6 6< z z 6 z z Q< z z g 8 B e c 8 o 8 8 8 8 6 6 z z 4 <' z z z Qz 4 z <z 6<<< x z z z 6<! z z a z z 6 8 z 9 8$$ 8 B 8 8 8 8 B u m < z =vymgv nnwa, 8 8 S g 8 8 8 8 8 8 8 8 8 8 8 0 8 z g g g g 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 z g q 8 8 ~ z a 0 V r ,pu°Iv„nnl.yw z 8 8 8 g 8 8 8 8$ 8 8 8 8 8 8 8 8 8 8 8 8 gg 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 0 a G g ,°ayuwngy>!p°nw z€ N QIJJ/PP""al qe�l .:in�Jw•S Y � $ � $ A 3 � 3 � L Q xod BgldwvS ulv.npuno,� y F Table 8 1 : Analytical Data for Groundwater User Specified Chemicals) 1 DSCA ID No.: 9200E01 mEE _ .fi E 3 g 0 x t £ 5 E 5 663F e� 6 F EQ E 6z EE < ?- _ A ti II/1N06 NA NA NA NA NA NA NA NA N:\ NA NA NA NA NA NA NA NA NA NA 12/L08 <0.003 <0.003 <Om3 <OA05 NA NA -1a NA N.\ NA - <0.005 -5 NA NA NA 0.00341 NA 2�5,09 <0.005 -.5 m.005 W.WS NA NA <Om5 NA IANA <0.005 W.005 c0.- NA NA NA 10.01 NA -.1<0.W5 W W5 <O.00S NA NA <0.001 NA NA NA NA 0-1<0.005 <0.N)5 [:A NA -.1 NA ...5m.Wl m.005 <0.005 IA<0.005 NA NA NA NA -.5-.5 <O.W5 NA NA NA -01 NA 916W <0.003 �.W5 m.O05 <0.005 <O.00s NA NA NA NA c0.Op5 <0.003 <0.005 NA NA NA - NA 10,6109 <0.005 �.Ws -5 W.005 10.005 NA NA NA<0.005 <DA05 <0.ws NA NA NA -01 NA L3.'10 <O.WS W.005 <0.003 W.003 NA NA <0.Ws N. NA N.4 <OA05 W.WS <.M NA NA NA -01 NA d:m�10 0W5 ­5 -.1 0.WlIJ NA NA c0.005 NA NA I NA -5 <O.M I 10.W5 J NA NA NA 0.00723 NA 713110 O.Ws W005 -1 <0.005 N I NA -5 NA NA NA NA <Om5 <0.005 <..1 NA NA NA m.01 NA 1N 10 <o,w5 <Om5 <0.005 <0.005 NA NA <4)m5 NA NA N I NA <Om5 10 WS 10.W5 NA NA NA -01 NA 4'25/ll <0.001 0.W27M <0.005 W.003 \A NA <U.005 NA NA k -5 <Om5 <0.003 NA N X AAA NA MW-Z3 11211 <O.00S <0,005 <0.005 <0.005 NA NA <0.005 NA NA <OA05 <O WS <O.WS NA k <0.01 NA MIU12 <...5 <0005 <O.WS <O.W5 NA N.1 .5 NA NA NA NA c0.Op5 <O WS <0 W5 NA -1 NA tl.- <OM5 <0.005 <O.WS 00W61 N:A NA .5 NA NA NA NA 4.005 <OWS <6.W5 \:\ NA -01 NA 2RU13 <0.005 <0.005 <0.005I I N.1<0.0p5 NA N:\ NA NA -- m.00S <O.WS NA NA NA -1 NA 1-13 <0.M5 <OA05 <0.005 <0.M NA IA NA NA -5 <O.00S <0.W5 Ni NA NA W.01 NA UII/13 4.ws ­5 <0.005 �OWS NA NA NA NA m.005 <O.00S <0.W5 NA NA NA -ol NA 1211U13 <OA05 <O.WS <0.005 W.003 11 NA <0.005 NA NA NA NA <0.005 <0.005 4.W5 NA NA NA - NA 3125114 <0.0005o -omo <0p0050 NA W.0010 <0.00050 <O.W 10 c0001U �O.W50 <o.01110 <Omm w.00m <0.0010 <O W050 <o.00050 W.0010 <O.00m <o.0010 6: IU14 <0.00050 <O.W50 <0.00050 00.00J0 <0.W10 -10 <000050 -lo N.0010 -,owso <D.WIO <0.0050 <0.00m <0.0010 <O.WI <0.00050 <0.0010 <O.00m < W10 92111 <0.00050 <0.0050 <0.00050KlO..5 m.0010 <0.0010 e0w5 W.0010 m.W1U <00050 <O.mlo m.00m <O.O <OAOIo <O.WIO <o.mO <0.wlo <O.00m -mlo 1218: IJ W.00050 ©.0050 <0.00050 <OA010 A.0010 <O OOo50 <9A010 <O.W10 <00050 ..0010 W.00m W.W20 <OA010 <OA020 �.00050 <0.0010 W.00m <0.0010 \ 1915 W.0o050 <Om50 -50 <0.0010 W.O010 <000050 <0.0010 <Omlo <O.W50 <0.0010 c0.00m ..0010 <0.0010 W.ODm <O.000So <o.mlo <Omm <O.00IO 6.1615 <0.00050 9.005o m.o0030 <O.WIO cO.W IU -o ws0 <0.0010 <o.0010 10.0050 <omlo d1.00m W.00'm <0.0010 <O.WIO <o.00050 N.00Io W.00m <O.00Io 2.12 <0.005 <0.005 <OAOS N.A N.A -0005 NA NA N.A NA <O.o05 <0.005 <O.WS NA NA NA W.01 NA113012 <0.005 <0.005 -5 NA NA <0.003 NA NA NA NA <0.005 m.005 W 5 N.A NA NA ®.01 NA..m <OA05 <OAOSNA NA <00p5 NA N:\ NA NA m.005 c0.0o5 <Om5 NA NA NA <0.01- NA 5/2A13 <Om5 <0M <0.005 <O.WS NA NA -1 NA NA NA NA Wm5 <0.005 <O.00S NA NA NA <0.01 NA MIM13 <0005 <0..5 -5 <0.005 NA NA _ Wm5 NA NA NA:: NA <O.o05 <O.WS <Om3 NA NA NA <0.01 NA M1IW-34S 1-13 <0.005 Nm5 4m5 <0.005 NA NA <0.005 NA NA NA NA W.o05 <O W5 <o.03 NA NA NA m.01 NA M- <0.00050 m.O050 <0.00050 NA <0.0010 W.0010 106W 0 <0.0010 -0 <0.W% <0,0010 m.00m <O Oom <00010rNAt <OOW50 W.Mo <O.00m W.00Io -14 <OAW50 W.o050 <&MI50 <o.0010 -mlo W.0010 <0.0005 -lo Na02o <0.0050 <o.00lo W.00m <O.Wm <0.0010 <0.00050 <O.aow m.Wm <O.00Io Ali/14 <o.00050 W.0050 -50 ..olo m.0010 -lo <0,0005 -lo <Omlo <O.00so <0.W10 �.00m <O.Oom N.0o10 <0.00050 <0.0010 <O.00m <0.0010 121714 <Om% -so W.OW50 <0.0040 <Om10 Amlo W.00050 W.0010 <0.0010 <o.W50 <o.0010 <O.00m <o.00m <0.0010 <OA0050 <O.Mo c0.00m <0.0010 31715 -000050 m.0050 <O.OW<0 <0.0050 <0.0010 m.0010 <0.00p50 <O.00m WA010 <O.WSU <U.WIO m.00m W.00m W.0010 <0.00050 W.00Io W.00m <.wlo 61515 -O.p0p5p 4.w. <O.000So W.0010 <0.0010 -lo <O.OW50 <0.0010 -o <O W50 <0.0010 <OAOm <OOo20 <0.0010 W.00050 W.0010 -w" <O.00Io <0005 m.005 W.005 <I)dW5 NA NA <0 W5 NA NA NA NA <O.WS <0005 <0.005 NA NA N.01 NA 3012 <0.005 �.001 W,005 <0.005 NA NA <0.005 NA NA NA NA 4.005 <0,005 <Om5 NA NA -ol NA 22713 <o.ws -1 <0.005 <0..5 NA NA <0,005 NA NA NA NA ­W3 4.W5 <O.W5 NA NA NA <0.01 NA 5,2A13 <0.005 <0.003 <O,W5 <0.005 NA NA <Om5 NA NA NA NA -1 10.005 1 <Om3 NA NA NA -01 NA UIMl3 4.o05 -.5 m,W5 <0.005 NA NA <OM NA NA NA NA <O.00S <0,005 <Om5 NA NA NA W.OI NA AfW2AD IUIM13 <0.005 -5 W.005 <0.005 NA NA w.W5 NA NA NA NA �m5 <OA05 1.11 NA NA NA �.01 NA 3/21- <0.00050 W.005o <, 5. NA <.Oolo �.0010 <O WO50 <0.0010 -lo <0.0050 <0.0010 m.6om <0.m20 �.wlo W.0o050 <0. so <0.mlo W.00m <0.0010 fi 19'Id <O.W050 m.0050 W.0005o W.0040 -mlo �.0010 <o.OW50 <0.0010 <00010 <Om50 <OA010 <0.0050 W.0020 <0.0010 <0.Wl <0.000311 <0.WIO <O.W20 <0.0010 23 id <0.00050 <0.0050 <0.0005o <0.010 W.00Io <o.W10 <0.0005 <0.0010 <O..to cO-o W.0010 -20 a.00m <0.0010 < WIO <0.00050 < Wll) <O.W20 <0.0010 12' Id <O.OW50 <0.0 <0.00050 �.0010 <Om10 m 0 <O.OW50 mm10 <0.0010 <0.W50 cOmlo <O.w" m.00m m.0010 4.1. <O.OW50 '9.0010 <Om20 <0.0010 ? 1815 <O.OW50 <om50 <0.00050 W.00IO <0.0010 <0.0010 <O.W. <OA010 <o,0010 <0.0030 W.O010 <p,OOm <O.00m W.O010 <O.00m <OOWNI �.0010 <0.00v -wlo 61515 <O.W050 <Om10 <0.00050 N.00W <0.0010 �.0010 W.000SO A.0010 �.00m <0.0030 <0.0010 �.00m W.00m �.0010 <0.0010 m.00030 -lo <O.Oom <0.0010 Page 66 of 127 Table 8 1 : Analvtical Data for Groundwater User Specified Chemicals DSCA ID No.: 920001 U E m L IR'-1 R16 W.021 -w 1.025 0.00371 NA NA 1.025 NA NA NA NA W.025 W.M <0125 NA NA NA -5 NA 12�- 0.000131 <0005 W..5 W005 NA NA 1.005 NA NA NA NA W.00J NA NA NA O.Oaaw NA 2/5/09 W005 <p005 1.005 1.00J NA NA W.005 NA NA NA NA W.005 5 NA NA NA III NA NJ09 <.003 1.- <0.003 <0.003 NA NA <.003 NA NA NA NA 0.00111 1 ,S NA NA NA Iol ]/1609 <0.003 c00o5 W.005 0.003 NA NA W.003 NA NA N.4 NA <.005 $0-5- , NA NA NA Wof M-3 IV1/09 1.005 W.005 <0.005 W..5 NA NA <0.005 NA NA NA NA W.O05 5 NA NA NA W01n1l0 <0.005 W.005 WA05 W.005 NA NA W.005 NA NA NA NA W.005 05 NA NA NA <0.01 NA 420/10 W005 W.005 WA05 <.003 NA NA W.005 NA NA NA NA W.005 NA NA NA Wal NA ]ll3/10 <0005 W.005 W005 W.005 NA NA -5 NA NA NA NA W005 1.005 0.005 NA NA NA W01 NA 1021/10 <a 005 WOOS 1.005 WO05 NA NA <.005 NA NA NA 0.005 W005 W.003 NA NA NA W..I NA IN3110. 1.1 000171 1.005 W.00J N.4 NA W.005 NA NA NA NA W005 <A05 <0.WS NA NA NA 0.000791 NA 25/09 <0.005 1.001 W.005 <.005 NA NA W.005 NA NA NA NA <.005 0.005 - NA NA NA <.01 NA 42/09 <0005 <0.005 c0.00J <.00l NA -a.1 NA NA NA <0005 <.005 <0.005 NA NA NA III NA 7/IV09 <0.005 W.005 W.005 W.005 NA NA N:\ NA -.1 <.005 0.005 NA NA NA <.01 I 107/09 1-1 1 0.005 W.001 W.005 NA NA I I NA 'a., W.005 W.005 NA NA N:A Imo 23/10 1.005 0.005 1.005 0.005 NA NA 0.005 NA NA 0.005 <005 <.005 N':\ NA <001 .1111 0.005 WOOS W.005 W.003 NA NA 1..5 NA N.4 NA <.005 <.003 <.003 NA NA <001 M'd 7/I3.30 1.003 W.005 W.005 W.003 NA NA 0.005 NA N.4 NA N.\ <.005 <.003 <.003 NA <0.01 1.21I10 0.005 W.005 W.005 W005 NA N.A W.m NA NA NA NA W.O05 1.005 W.005 NA NA I k Wal I NA 7/19'12 0.005 1.005 2005 W005 N.A W.005 NA NA NA N.\ <O.NS <.005 W005 W.Ol NA 11/30/12 0.005 <0.005 <0.005 1.005 NA \A 10005 NA NA NA N.\ <a.1 W.005 <0.005 11 1 1 \'A III NA 228/13 <0.005 0a5 1.005 W.00i N':\ N:q <0.005 NA NA NA 1-1 0.005 W.m NA <001 NA "a'13 1.005 III, <0.005 NA N.{ W.005 NA NA NA <awl W.005 W..5 NA III NA 11111 1.001 <111, aaa, 0.001 NA NA NA NA NA W.005 W.005 W.003 NA W.01 NA 1231IS <0.005 <.0U5 W.005 <0.005 NA NA NA NArNA NA W.005 <0.005 <.005 NA NA III NA <.005 <.005 W.005 <.005 NA NA NA NANA <.005 <0.005 <.00S NA NA Wal NA -1 W005 WAOS NA NA F-3 NA NANA <.005 <.005 <.001 NA NA -oal7II- moos W.005 <.005 <.005 NA NA NA NANA W005 <.005 <.005 NA NA IM/09 <O.00S <0105 <.W5 <0.003 NA NA NA NANA <.005 W.005 WW NA NA NA <001 2V10 c0.005 1105 <.00S <.005 NA NA NA N.qNA <.005 <0003 -a005 NA - I N:q LllllO c0.005 <0.005 <0005 <0..1 N'A NA <.0U5 NA NANA W.005 0003 NA I I NA 10.01 NA ]ll3/l0 c0.005 <0005 1.005 1105 NA <.005 NA 1A NA W.005 1.005 <a MIS NA 1A - <001 NA 1R21/10 <.005 <0.0U5 <..5 <.005 NA NA <.005 NA NA W.003 1.005 <0005 NA NA 11 0.01 NA 711V12 W.005 <.005 <.00S <.005 NA NA <005 NA NA <A05 W005 <0005 I NA -0.01 NA 1\\-5 .1-2 W.005 1A05 <.005 1005 NA NA <.005 NA N.A N.q <D.O05 W005[...1 .005 NA NA -0.01 NA MV13 W005 -5 1.001 1.001 NA NA <0.005 NA NA NA WA05 W005.003 NA NA -0.01 5/30'13 <0.005 <.005 <.005 <.005 NA NA 1005 NA NA NA <a.1 W.m.005 NA NA -0.01 9IIV13 Y.MW W.005 10.005 10.005 N.4 NA 1.005 NA NA NA 1.- <.005005 NA NA <0.01 12/1V13 1.005 10105 1-5 1.005 NA NA <.005 NA NA NA NA WM 1.003 NA NA NA W.01 N'A 325/14 <00050 <.0050 1.000NI NA W.- 1.001. <.00050 <0.0010 1.0010 <.00" <.0010 <0.0020 <.0020.0010 <.0010 <.00050 <.00I0 W.0020A'1R14 1-50 W.0050 <000050 0.00131 <.0010 <.0010 OADOW <0010 <.0010 <.0050 <.00IO 0.000561 <.0020.O010 <0.0010 <.000SO W.0010 <.00IDR 5I11 <.OW50 <A050 <.00050 W010 W 10 <00010 <.0005 <.0010 W.0010 <.0050 <.0010 <.0020 <.00200010 W00I0 <0.00030 W.0010 <.0020 <.0010 111. 11 W.00050 <0.0050 <.00050 <.0010 ""a W0010 <.00030 <.00m0 <.0010 <.0030 <.0010 <.0020 <..20..10 <0.0010 <.0 " <.0010 <.0020 <.0010 3 13 IS <a OOOS0 W... <.00050 <.0010 D.001. <0.0010 111. <.00)0 <.0010 <.OUSO W.0010 W0020 <.0020 <.0010 W.0020 <.000SO <.Wlo W.00ID <.- 6 I] I5 W.M% <.0050 <0.000SO W0010 <.0010 W.0010 1.00050 1.0010 <.0010 <.0050 ...,a <0.W. <0.0020 I <.0010 <0010 W.00050 <.0010 I <00020 I' - Page 67 of 127 a � Y — � C � 6 C � p 3 $ � � � - ? � '� E 3 ! Y � 'E e N Samvlme Da�.lmm ,l.l „ '• 3 ik � °� $ _ � N _ $ � $ $ — a A A a a ^ A A 9 A A A A A A A A A 6 e a a A 9 a A a A ' A A A A A 8 A A A A A 8 A 6 6^^ € o e a c 8 4 A 9 a a 6 A 8 a a 8 a 8 8 A a S^ A A z z o a x z o a 8 o$ a$ 8$ 8$$ 8$$$ 8 8 8"ovmvrlmnm g$$$ x x x x§ a i>> 'Sg 8� g A S S 8 A g E 8 8 8 8 8 8 8 6 A tl A g Ag S $ 8 e P 8 8 8 8 8 8 e i 8 3 8 •`n"^ aamra° "c 8 = a ;x z x i 8 8 z z x x z z z z 8 8 A A 8 z z z a z. i z z A A A A^ z z z �,a,a rrn"°mrium�..<°" 9 a r o a r__ 8 5 8 a E a a a a a a r S 88 88 8 a a a r>> 8 8 o 8 8 0 o 8 a e a a ^ x a a c 8 8 z 8 a> x x a x z a a o A 8 88 8 A 88 8 z z a> z z a a z z a a z a> a 8 8 8 8 x 8 a>> x BJ rr:"emy�um,.°°. =i s _ YY^ pp pp pp^ pp pp YII 3rom°chbromMane A o i zd i A s A A A a i a i i a a A a A 8 a e 8 8 a a a a a a>> A 8 8 8 a 8 8 A i i i •Buryibm:a° _ $ 8S 8 8 _ 88 88 _ _ _ _ 8 _ a Y. Y. A A a A z z z z z z z z S"""" z z z za z z z A a 9 a S z z z 'g o> o a x a 8 8 8 r a D a> a a a a 88 g a a a a a a> 88 8$$$>>> zaro;asm. F. z z z z z A A A z z z z z z A A A A z z x z 8& 8 A A z z z o r o>> g 8 8>>>>> IZIZ a a a e 8 g a >> a a> ,zr.rnbmnm�m� a 8 A S A A 8 8 a a 8 S o a$ a z t 8 8 8>>> a>>>> 88 88 8$> a i a> a a i$$ 8$$ a i i $. z z z zll.l A^^ A S A 6 A 6 6 69 A S A A 8 8 8 a^ 8 6 a^ 8 ""^ 8 A 8 8 g 8 S 8$ 8 8 8 e C `a 88 8 8 z g g a .nMmmmn."° 8 g a A S 6 a A a A A S A A 6 a a AA A S a A A A A A A A A A a 8 6 > i i r 8 S d 6 8 A z z z z A A A 6 A S S S S a a 6 Ag A A A^ a S S a A A 8 a A A A^ 6 a S a $ a> a r§ 8$ 8$$ 8 8 8 8 8 x x 8 8 8$$$$$ 8$$$$$ S z x a>> z, i A 8$ a 'a z 8 a$$ A a A 8 x z a a z �. z > a 8^^^ 8 s$$$ z r z z a a ^ z z z z z^^ z z z z z z z z a a a 8 A 'r 's z x z z z 8 A 8 8 g >> a a a 8$ a>>> a a a a$ $$ a a a> a> 6 g z g z z A A x z x z z x x z A 8 8 8 A z z z z z z z 9 A S z z z w > > > g $ $ $ D > > D D D a D g �, $ > D D D > > r r A$ A a a a s 6 e o ao s s ass rBly*— x z z x x 6^ 8 6 z z z z z z z ^ z A A 6 6 z z z z z a 6 6 a S z z z a a a a 8 8 8 a>>> a a a a 8$ a> a a> a a 8$$$$>>> Table 10: Water Wells Survey Data DSCA ID No.: 920001 Distance Direction Property Owner Well Screen Status Ref, No./ Sampling Location Tenant Name Address, from Source of Well (downgradient, Name, Address, and Depth Interval Use of Well (Active/ Well ID Name and Address and Phone Number Source Identification upgradient, etc., Phone Number [feet] [feet] Inactive) feet to source area Kelli Barbour, 8400 Residence, 8400 Camellia Drive, Same as Owner 480 Unknown Unknown Drinking Water Receptor Survey Downgradient Abandoned Camellia 8400 Camellia Drive Raleigh, NC, 27613, 919-772-5160 Charles & Carole Vish, 8401 Residence, 8401 Camellia Drive, Same as Owner 680 111 Unknown Drinking Water Receptor Survey Downgradient Active Camellia 8401 Camellia Drive Raleigh, 27613, 919-847-7632 Andrew & Noma Kleitsch. 8404 Residence, 8404 Camellia Drive, Same as Owner 68 Unknown Unknown Drinking Water Receptor Survey Downgradient Actirc Camellia 8404 Camellia Drive Raleigh, NC, 27613, 919-848-0222 John M. Rogers, 8405 Residence, 8405 Camellia Drive, Same as Owner 820 Unknown Unknown Drinking Water Receptor Survey Downgradient \cticc Camellia 8405 Camellia Drive Raleigh, NC, 27613, Unlisted Daniel & Tara Whitley, 8408 Residence, 8408 Camellia Drive, Same as Owner 880 200 Unkno- n Drinking Water Receptor Survey Downgradient Actin c Camellia 8408 Camellia Drive Raleigh, NC, 27613, Unlisted Gregory & Amanda 8409 Residence, Williams, Camellia 8409 Camellia Drive 8409 Camellia Drive, Same as Owner 980 Unknown Unknown Drinking Water Receptor Survey Downgradient \dice Raleigh, NC, 27613, Unlisted Frank & Brenda Ham, 8412 Residence, 8412 Camellia Drive, Same as Owner 1040 210 Unknown Drinking Water Receptor Survey Downgradient Active Camellia 8412 Camellia Drive Raleigh, NC, 27613, 919-847-4121 Gene R. & Sandra T. 8413 Residence, Soyars, Camellia 8413 Camellia Drive 8413 Camellia Drive, Same as Owner 1 140 l lnl<nown Unknown Drinking Water Receptor Survey Downgradient Active Raleigh, NC, 27613, 919-847-4142 Debian & Matthew 8416 Residence, Thacker, Camellia 8416 Camellia Drive 8416 Camellia Drive, Same as Owner 1140 Unknown Unknown Drinking Water Receptor Survey Downgradient Actix e Raleigh, NC, 27613, 919-917-7393 Page 71 of 127 Table 10: NNater Wells Survey Data DSCA Ill No.: 92 �,9 Distance Direction Property Owner Well Screen Status Ref. No./ Sampling Location Tenant Name Address from Source of Well (downgradient, Name, Address, and Depth Interval Use of Well (Active/ Well ID Name and Address and Phone Number Source Identification upgradient, etc., Phone Number [feet] [feet] Inactive) feet to source area) Michael E. & Virginia H. 8417 Residence, Richardson, Camellia 8417 Camellia Drive 8417 Camellia Drive, Same as Owner I O0 Clnknown Unknown Drinking Water Receptor Survc} Downgradient Active Raleigh, NC, 27613, 919-848-6743 Lorraine Tomasino, 8420 Residence, 8420 Camellia Drive, Same as Owner 1200 >150 Unknown Drinking Water Receptor Survey Downgradient Active Camellia 8420 Camellia Drive Raleigh, NC, 27613, 919-841-9338 James W., Jr. & Louise 1). 8421 Residence, Knox Camellia 8421 Camellia Drive 8421 Camellia Drive, Same as Owner 1440 139 Unknown I )rinl:in \1 to Receptor Survey Downgradient Active Raleigh, NC, 27613, 919-847-5098 John & Goldie R. 8425 Residence, Duperock, Camellia 8425 Camellia Drive 8425 Camellia Drive, Same as Owner 1440 Unknown Unknown Drinking Water Receptor Survey Downgradient Actioc Raleigh, NC, 27613, 919-847-5153 Betty Rogerson, 8429 Residence, 8429 Camellia Drive, Same as Owner 1420 Unknown Unknown Drinking Water Receptor Survey Downgradient Actin c Camellia 8429 Camellia Drive Raleigh, NC, 27613, 919-847-5613 Elizabeth M. Mercer, 8433 Residence, 8433 Camellia Drive, Same as Owner 1440 Unknown Unknown Drinking Water Receptor Survey Downgradient Acme Camellia 8433 Camellia Drive Raleigh, NC, 27613, 919-847-5754 Eugene Kennedy, 8400 Residence, 8400 Azalea Place, Same as Owner 400 150 Unknown NA Receptor Survey Downgradient Abandoned Azalea 8400 Azalea Place Raleigh, NC, 27613, 919-847-7575 Bruce Blackwell, 8401 Residence, 8401 Azalea Place, Same as Owner 0 173 Unknown NA Receptor Survey Downgradient A:, n,,d, „ d Azalea 8401 Azalea Place Raleigh, NC, 27613, 919-524-4765 Frederick Schwartz, 8404 Residence, 8404 Azalea Place, Same as Owner 000 Unknown Unknown Drinking Water Receptor Survey Downgradient Activc Azalea 8404 Azalea Place Raleigh, NC, 27613, 919-676-1249 Page 72 of 127 "Cable 10: Water Wells Survey Data DSCA ID No.: 920001 , Distance Direction Property Owner Well Screen Status Ref. Nod Sampling Location Tenant Name, Address, from Source of Well (downgradient, Name, Address, and Depth Interval Use of Well (Active/ Well ID Name and Address and Phone Number Source Identification upgradient, etc., Phone Number [feet] [feet] Inactive) feet to source area Elias Schnegelberger, 8405 Residence, 8405 Azalea Place, Same as Owner 600 Unknown Unknown Drinking Water Receptor Survey Downgradient \cticc Azalea 8405 Azalea Place Raleigh, NC, 27613, 919-847-4828 Richard Lemert, 8408 Residence, 8408 Azalea Place, Azalea 8408 Azalea Place Raleigh, NC, 27613, Same as Owner i 80 Unknown Unknown Drinking Water Receptor Survey Downgradient Active 919-846-0558 Jaswantrai Patel, 8409 Residence, 8409 Azalea Place, Azalea 8409 Azalea Place Raleigh, NC, 27613, Same as Owner 780 Unknown Unknown Drinking Water Receptor Survey Downgradicnt Active 919-846-7173 Vance Kennedy, 8412 Residence, 8412 Azalea Place, Same as Owner 930 Unknown Unknown Drinking Water Receptor Survey Downgradient Active Azalea 8412 Azalea Place Raleigh, NC, 27613, 919-847-4055 Richard & Danielle Lang, Kenneth & Donna 8413 Residence, 9329 Tamarack Drive, Hunsinger, Azalea 8413 Azalea Place Meadville, PA, 16335, 8413 Azalea Place, 960 Unknown Unknown Drinking Water Receptor Survey Downgradient Actk c Unlisted Raleigh, NC, 27613, 919-8474159 Annie B. Johnson 8416 Azalea Residence, 8416 Azalea Place 8416 Azalea Place, Raleigh, NC, 27613, Same as Owner I I-10 Unknown Unknown Drinking Water Receptor Survey Downgradient Active 919-847-5675 Farlow & Metcalf LLC, 2949 Unknown, 7420 Matherly Drive, Unknown 1000 Unknown Unknown Drinking Water ENSR Receptor Upgradient Active Brennan 2949 Brennan Drive Wake Forest, NC, 27587, Survey 919-556-9677 el is were at I reportedly cased to bedrOCK surface and ten dri I IMinto the bedrock until the tust zone capa e ot producing sufficient water flow was encountere . the well at2949 Brennan Drive was oreviously addressed as 8217 Creedmoor, Page 73 of 127 e � SampleID � m A F� vz ^' Sampling Date (mm/ddly. m v o v vvv v o Benzene O m e vvvvvvvv is-1,2-Dichloroethyl v m A C v v v v v v v v v v v v v v v v e v Ethylbenzene Methyltert- utyl 6 6 6 o ether v y MTBE A C g'ovvvvvvvv vvva1vvvv Naphthalene s8vv61.666666666v0 vvv etrachloroethylene 8 8 §vvv v v v v v v 6 'av v v v v v v Toluene 8886666600v66666666666 s-1,2-Dichloroeth, g g 3 v v v v v v Z. o v v v v v o v v- richloroethylene a a g 8$ a a 8 v v v z v z zv v z v v z v v z z v v v v z z c r z z r. Vinyl chloride v z o v v a v v v v v v v v v v v v v v v v v v Ylenes (total) asaa v v zzzvv v v o z v vBvvvvvvv Z Z. 1,1,1-Trichloroethane 3 6 a$ v v z v v z z v v z v v z o v z v v z z v v z v v z v v 1,1,2-Trichloroethane 8 v v v v v vvv v v v v v v v v v v 1,1- D i c h l o roe t h a n e a a v v c c z v v v o v v v v v v v z. 1, 2D- D i c h l o ro e t h a n e v v v ) 8 8 8 v v vz o o 6v v v v v v v v v v v `c Carbon tetrachloride v v v v v v v v 3 v v v g & v hloroform v v v v o v v v v S v v v v o c '- romomethane =88,vvvvvovvvvvvvavvv.- a ichlorodifluorometh e 8888vvvvvvovv8vvvvvvv= hloromethane z HIM- OU0103V z z z z PH- <z < z 9 apuo14j aualxgp z z z �Z z z z Fees ououenn a' a< z z a a z z < z z < z z a< z 3 a a< 3 z z z e a z z a< z z a< z z S < z P � auazuagl,gng-ya i g °z z z °z g �Z z z z c z z c °z f F a Pz .7 P G auazuagaol4 g g o g g g i 9 9 9 °z 9 9 2 e Q a 9ige9<z'z9999zzzzzggg�s � eylawmo�yoowaq_ Z U aP31ns!Q uogie <z z z z z z z z z z z z z z z z zz< z z o = s F auazuaql6ylawu �Z �Z z z z u i' auazuagaolgou c z z 98 8 u z F P 9& auazuagaojgou z z z z `z z z z i z z 3 auozuagmotgo!U-p'I g g g g g z g g g g g 9 g g g 9 9 9 9 auazua ao o� 4 �4az`i � c c c zzzgggz��zzzeeee c � a a a o� o 6 gg�gzzz 3' `e awzuaqj/4nEj-aas 9 Q Q ez g z 9 9 9 i 9 °z 9 z z z z z 2 Qp? y? y W - Q Ei P 4 aueglaao y 9 9 z z 9 z i 9 i i 9 i 9 9 9 9 9 z z z e o A z � o o N m A/PP/ww) aTeU 8ugdwe$ gg z a s � a - UI aldwes W x x x F � S m Sample ID y� Sampling Date (mm/ddly, _ m 8 A d A 6 d A¢ a 8 A A a 2 r3 8 6 0 0 C S ertune m a = A 8 8 8 A A 6 6 d 8 A d 6 a a 8 A a __ 8 8$ — 8 8 8 8 8 8 8 8 8 8 8 A is-1,2-Dichloroethyl m A 6 A a a 9 A a 6 6 e3 0 6 A A g A 6 A d thylben 'Azene � 8 8 8 8 8 8 er E m C 0 � 6 d^ v a 6 6 A 6 6 d 6 A A a e�§��� 8 8� r 8 8 8 8 8 8 8 8 8� g aphthalene A 8 A a 6 d A 6 6 A 8 A 0 8 8 6 d etrachloroethylene 8 8 8_ $ 8 8$ 8 8 A oluene d_- 3 6 b a = _ = 8 8 8 8 s-1,2-Dichlorceth _ 8 3 E 9 8 8 rrichloroethylene A a a a a A 6 d A 6 6 d 6 A A S 6 A A A A 8 8 d 8 8 e 2 2 v e� 8 8 v 9 Vinyl chloride A 6 6 A 0 0 6 A A b 6 A 8 6 A 6 o A 8 6 8 8 8 8 8 � 8 8 8� Ylenes (total) eaaaa6o 3 8 8 8 _ 8 8 a 8 8 S 8 o A 1, l,l-Trichloroethane 6 A d a A A a a 6 6 a A b A 6 8 a 6 a A A 1,1,2-Trichloroethatic A b d A A 6 A 8 6 6 A A A 8 A 6 a A 9 a e 8 8 8 8 g 8 8 e 8 8 8 a ],I-Dichloroethane g$ 8 g 8 6 A b 6 a 6 6 d 1,2-Dichloroethane A DC) 6 2 0 A 9 A A d a 6 d B 6 A A d 6 A arbon tetrachloride 6 a A A 8 8 A________ 8 d 6 g A b a Chloroform 6 6 6 romomethane e g d 6 3 A 6 a 6 a ichlorodifluorometh $ S g 6 a A z a a a i a a a o e e B d A A 0 0 6 d A 6 A 8 8 0 6$ g$$ 8 8 8 8 hloromethane S ro G" Sample ID n Sampling Date (mm/ddly m > a $ hloroethme o m t b d 8 8 b a 8 8 a A 8 8 z z > r z a > z za > z > > z z r > z z > > z > -Bu Ibrnzene ty m e �- $ 8 8 $ $ a > a a a a > > > > > > a 1,2-Dichlorobenzene 8 8 8 8 8 8 z z a>>> z z a>>> z z z z a a z z a>> z$ ],4-Dichlorobenzene d a d e a a A z z z z z z z z z za z z a z$ 1,2,4- $ $ 8$$ a a> a a> a a r a> a a g' richlorobenzene [ o e e e e>> > >> z z a a z z> a a z > z a a 1,2,3- a richlorobenzene M B a b A A A z z z z z z z z z z z z z a 1,2,4_ $$ - - S 8$ - - o a> r a a a a a a a a a a `g a g rimethylbenzene M. m a 6 a A a& a a 3 6 a d A A g A a g a A w w A a g i Carbon Disulfide 9 ro b Dibromochlorometha 8 8 s a 8 8 8 8 a e 6 6= A 8 a b a b& a 8 6 a hlorobenzene b d A a a b z z z z z z z z z z z z A a t" z > ert-ButY (benzene 6 i3 b At; e 8 a A a A A A A -- - a -Butanone - - - - - - - - - - - - AAeaaa b. g > Methylene Chloride Acetone S m 3 Sample ID i e Z Sampling Date (mm/dd/y _ - - g g_ _ g - M m a a A 3 A a 6 6 6 a a a A A a a A a a A A 6 a a A A a a a a O j E o S e e§ e v e e 8 o§ e enune m e $$$ 3 8$ y d 6 8 C 8 y C 8_ 8 $ is-1,2-Dichloroethy le - zd m A d a 6 a A 6 I a B a a I a 6 a I a 6 8 a 6 a a 1 6 1 a a A 1 a a a A Ethylbenzene % S $ methyltent-butyl other zd 6 a d a a 6 a a 6 a a A a a a a a ap hthalene z a- A_ 6 a e a a a a A a a 8 8 a Bg ag 3A Sa etrachloroethylene - 6 a A a A a a 6 d 6 B a a a 6 a 9 A3A A a 6 a a A % 8 % % % % % e o x Toluene 8 g 6 A a a 6 a a A a a b a b 8 a A a a 6 a a a a a _1,2-DichloroetM zd % - _ $ 8 8 $ 8 8 8 8 8 a richloroethylene a �aeaeaAeaaaa6Aa�aeaaaAaa Vinyl chloride z o 1,1,1-Trichloroethanc 6- _ __ e3 e3 8 8 6 a a 6 S 6 A 8 8 8 6 +a 6 6 a S R 112-Trichloroethane I,I-Dichloroethane 1,2-Dichloroethane - - - - - - - - - - - - DC) Carbon tetrachloride c Q a 6 A a a A 6 a A a= a A 8 a 9 6 a A 9 a 8 a a hlorofo xd rm _ e 8 6 _ _ _ _ 6 Is_ romomethane zd = = S� z z a a z x a a z a z z > a> z z a z z a> z z a>> z z a> z z a z z v a> z z a 'chlorodifluorometh o e e :eaaaaaaaaeaaeaaaa� aaeaaaaaaa hloromethane S tz m Sample B) n — a � a � a � S Sarnpling Date .. U g e g g g g (mm/dd/y, N O n 8 8 8 g a b b a= 6 a d a a a 6 a e b z a v o hloroethane p - - - - - - - e n a 8 8 8 8 8 z z z z z z TIT z z z z z z z z z z z $ z 8 zsec-B uty (benzene z 6 8$ 8 8 z z a z> z z>> i a a i i i z a z a a a z 8 8 0 1,2-Dichlorobenzene 3 U G I > > z i > z z > > z z > a z z > > z z > z< - z z > a z z r a z° a 'g g zd 1,4-Dichlorobenzene — 2. e_> 1,24- 9 >z za z> za ric,hlorobenzene a a 1,2,3- $ o = 8 z 8> z z z z z z > a z z z z z z z z z z z z z richlorobenzene avaaaaz 8 $ $ > z<<zzzzzzzzzzzzzzzzaa > r > > > > a a a a a > a a > a > > a zd 1,2,4- _ _ - rimethylbenzene n a 88 6 8 b 3 a 6 a 6 a a 8. a a A a a A a A 6 a 6 a A gg Carbon Disulfide 3 — b a a a a 6 b 6 a a 6 a A a A A a a 6 a- ` a a 6 a A a Dibromochlorometha e aaaaaaa=aaaaaaaaaasAaaaaaaaaa hlorobenzene a v a a a a z a s r 0 8 8 8 zr z> r > r a a z z a zr ert-Butylbenzene8 8 a 6 a a 6 a 6 6 d e a o A g a d a A a a A a A a a 6 a g g g ethylene Chloride s=_ aaAaA_=essz 3 - - > crone S m Sample ID g S N f3 s g g o ti g g g$ Sampling Date (mm/d -zz 7z g P m_ Benmne m is-1,2-Dichloroeth I Yr C 8 6 8- 8 8 8 s s 8 8 8 8 8$ 8 s 8 2 = 8 8 8 8 8 'g o Ethylbenzene 6 d 3 A A b g 6 A 6 n 8 A d d 6=--- d 8 8 9 b 6 Y tert- ury - - - -I oether zd (MPBE)re A $ a 9 8 $ 9 d 8 6 A b $ 8 A d $ $ 9 9 $ $ d 8 8 $ 8 A $ $ A A $ 8 5 9 $ $ 9 A $ $ 9 d 8 $ 6 A $ $ d :9 $ 8 6 d 8 Naphthalene dg A 8 8 6 9 8 A 6 9 9 8 8 9 6 A o 8 8 8 S 8 8 0 8 g 8 S 8 8 zd etrachloroethylene .MPEMMB PE 3 B d 9 3 9 6 9 6 6 8 8 8 d 6 d 6 A A 9 9 A 8 6 d 9 6 9 B S 8 8 8 g 8 8 e 8$ 8 8 8 S 8 e S$ 8 S 8 3 zd Toluene 9 8 A 9 8 8 A d 8 $ 6 8 8 9 A A A= e A 8 A A b 9 A 6 A A 8 2 d A B 8 8 8 8 $ 8 8 $ 8 8 $ 8 ans-1,2-Dichloroeth� richloroethylene A B 8 9 A A A A A A 9 9 9 8 A 6 8 6 0 d d 6 d A 9 5 g g 8 g e 8 8 8 8 8 8 g Mal o 8 8 zdVinyl zd chloride 8 8 8 8 8 8 8 8 8 8 8 - $ = 8 8 Ylenes (total) 8 8 9 8 8 9 6 9 9 6 8 g__ 8 = g 9 9 A A A 8 9 9 d l,l,l-Trichloroethane 8 8 $ $ 8 8 8 8 8 $ $ 8 $ zd 1,1,2-Trichloroethane A d=___-_ 9 8 d d 9 8 b A A 9 b 8 d 8 8 B = = = = 8g 8 S 8 g 8 8 8 11-Dichloroethane 8 8 8 8= 8 g A 8 8 A A g$ - 1,2-Dichloroethane - - - e e _- EDC) 9 A d b 6 A 8 8 o 8 8 8 8 8 8 8 8 8 8 8 8 8 oCarbon tetrachloride $ $ $ __ _ = 8 $ Chloroform ti g6 g= 9 A A e__ romomethane z o 8 d d d5 e a 8 6 z 88 a z z a a 4z r z z a a z z a> z a z a z4 z z a a z z a a z z a a> z z a z4 a ichlorodifluorometh 8 e A d= A 6 g g 8 A L $ $ 88888A 'S u m 3 5" SampleID Sampling Date (mm/dd/y. m _ 7 e g g g g e B a a a A 6 A A B B B a - 6 A& o> 6 zd hloroethane C m A 8 B= 8 e= s z z r r z z r a z a z z a a z z a z z r>>>> z z z z z >>> z i zd ec-Bu (benzene tY - - - - _ - m az z a� o 1,2-Dichlorobenzene -� f9 e -= g g> za z z a a z z r a> z z a z z a a> z z a z z a a z z a s z z a a z z a a> z z a a 8 zd 1,4-Dichlorobenzene A A e z z z z z z z z _ z 8 e z z r r z a zi z �. >� z a a a a a> z a z z a z a a z a a z z a>� o rrichl richlorobenzene 1.2.3- [ 0 8 = 0 A 6 8 8 z z a a z z a a z z a>> z z z a a z z a a z a a> z z z z z z A richlorobenzene o A 8 A 8 8 8 A e 8 z z a z z a a z z a a z z a a z z r a> z z s> z z a z z a> z z a>> z z a z z a a zd 1,2,4- 0 - - - - fl a rimethylbenzene r a S A A 6 A 6 6 a = 6 A B B A 6 d A 6 A 8e A a b g O arbon Disulfide � a m A A A d B B a A A d A d a 8 a zd Dibmmchlorometha 8 8 8 8 8 e - d A A A a b B A 4 a a a A A A a A A a a A B A 8 B B B B hlorobenzene 8 8 A 8 8 8 ±3 6 8 8 z z a a z z a> z a>> z z I z a z z r r i> z z z z z z a z r ert-Bu zene tY(ben A A B B A B b A d b= a a b g z -Butanone - dtg ethylene Chloride Acetone S m Sample ID _ g - - ' e Sampling Date (mm/dd/y, _ A 8 6 A d 8 A d A A A 8 a A A d d b a a A A b 6 8 o a a A b d C z 8$$$ B$ a$ N$ 8 e 3 0 8$$$$$ e o e 8 8 is-1,2-Dichloroethyl -itC L N p A thylbenzene y tert- uty C - d S d 3 b d d 8 8 8 8 A d 8 8 8 a 8 b 8 8 A A 8 6 6 8 8 8 B z -ether (MTBE) $ $ $ $ $ 8 S S 3 � 'dNaphthalene 8 8 8 3 8 8 8 8 8 etrachloroethylene S s e e 8 o Toluene -1,2-Dichloroeth A--= 8zd 9 A A richloroethylene - _ ti u 8 Vinyl chloride = 8 $ 8 8 8 0 8 8 $ $ $g g g $ 8 XYlenes (total) - $ g $ $ $ Y 8 0 1,1,1-Trichloroethane d B d A A d a 8 8 A A 8 8 8 6 8 8 A A d A 8 8 8 8 A 1,1,2-Trichloroethane 8 8 8 8 8 8 8 8 8 8 8 8 8g g8 zd 1,1-Dichloroethane = o$$$ A d 8 a 8 g 3 8 8 8 A a 8 8 A 8§ A 8 a 8$$§9 8 a= 8 d 8 8 8a 6 d b 8 8 :8 1,2-Dichloroethane N o D) Carbon tetrachloride Chloroform romomethane 8 8 d 8 a>> z z z a a z a z a z z a a z z a a z z a> a g 3 ichlorodifluorometh e s S 8 S 8 g g 8 A A A 8 8 8$9 A a 8$ S e- d 8 8 hloromethane s k S m G' Sample ID g Sampling Date (mm/dd/y e - - g - 5 S § °f o hloroethane C ro e a a b a a e z z z z a z > z z > > z > z z a > z > z az a z ,- z z > � >z a 8 �dsec-Bub lbenzene m m e - _ - - - - a a a a za i 6ti 1,2-Dichlorobenzene v 3 8 z a a z z9 a>> z z z z a a z z a> z z a a z z a a>> z z z z a>>>>>> z z z z z zi a 'd l,q-Dichlorobenzene $ a a a a a> a a z z z z z z z z x z z z z z z° z 1,2,4- _ a a r > a a > a a > > > > o richlorobenzene m i Sz a a a a a i a a a i a a 'd Irichlorobenzene = ": rn y = "' o z z a> z z a a> z z a z z a a z z a a z z a a> z z a z z a> z z a a z z a a z z a a z z a a 1,2,q- _ rimethylbenzene n a Disulfide arbon 3 A 3 6 v a a a a 6 6 a 6 8 a A a d a a a 6 a d A d A a d 6 a a ibromochlorometha 6 8 6 A A A a a A a a a 8 A 6 a a 8 a a a 8 d A a A 8 8 8 8 a hlorobenzene 8 Big z > z z a a z z a a>>>>> z z z z z za z z a a> z z a> z z z a a z z a a z z a a a z o r ert-Butylbenzene a - -- z -Butanone 6 9 a A a a A d a a - 8 8 a ethylene Chloride a d 6 A a 9 6 a d A 6 a a a 6 6 g ____ _-__ z Acetone § � E _Am — ' Sarn ®-Date®mld® Benzene � ® %§§§§\)\) §§§)/\\�® ®'� ® !!!!§t/§i!!!!|§2§})!\; i+_ — a, \,»a a a64n A a� '` ® !:! ■!■;,l; ,!l ; _ E Naphthalme;���„ _ A a 8 a §}li§!4AA A A Aa8 A a a A A a a a a A 8 !!!■!!!!!l;;;;:!!_;!|; _e_yleri, w— a:94¥aAaA�,¥ ■9s89as !!§!!!!•r!!;!|® „ aaaA „ *A J ®� (§§|§||§§!|!!! aAa8aa °�© ~` m !||||||!!!|§!!;§I§!!§�, �4aaaA8A1: A 66 ? |!§fKt!((})a8a-16 la!||atexyleriesWk m _— 616 a A a a 9 a a aaaa# 1,1,2-T __than. :;!!!!`>:>zz:!|a u-Dic +__. A::_::.*4A4; . ___ ------!!® D Aaaaaa; Carbon tetrachloride )!�!\;E>/!!t4*— ®,�a�e:}®�� !!!!§}jl7a ..elb— ;=;7; " °° ane ' A4!!!§§}§§!!!!§§>t}§|! ___. C" Sample ID N N p N N Sampling Date (mm/d o g g S e g g a b 6 a 6 b 3 6 a a a 8' a b a a g Chlomethme 0 p m z e 8 8 a 8 8 a z i a a i z i a a?$ vsec-Butylbenzene fD a a b a e B z z z z z z z z z z z z z z 8 z 8 8 8 8$> a a a a a> a a a>>>> 1,2-Dichlorobenzene C S 8 8 8 8 8 i i za > a a y a z " c 1,4-Dichlorobeozene A z= i z y z z a z z; z a$ 0 rric richlorobenzene m f9i a a 6 A A e �Z z a z z a > z zy > a a a a a 8 zd 1,2,3- richlorobenzene a a $ e a b b z z z z z z a a z z a a z z a a> z z a z z a a a g 1,2,4- rimethylbenzene =i !� A 9 b A b b 3 a= a a a a a a a a a a a z Carbon Disulfide � 3 ibmm chlommetha e 8 a 8 8 v A a a S a= o 8 's 8� 8 8 8 8 $�� hlombenzene --- a 8 8 8 8 S z z z z z z z z> b z r i i i � p a a a a a z $ o ert-Buty I benzene B A A a& A a A 8 a A b a a a A a 6_ o -Butanone a a 8 S e s a a b a 3 o a b a A b 8 8$ o ethylene Chlonde 8 b a___ A A a A A a b A A g; cetone = � m SamplelD Y ti o g S w S 5 g S w s N= S= g Sampling Date (mm/d m_ m s-1,2-Dichloroethyl A A a a 8 6 d b A A 8 8 8 a b 6 9 8 A 8 6 g g e��� a 3 8 8 A A 8 8 b A 8$ e a 8$ A r 8 6 a 9 A d a 6 9 a d a a a 6 a 6 a 8 .`d 6 8 6 6 8 8 6 a 8 g d 9 g 8 a d 8 A 8 a d 8 thylbenzene y ten- uty 8 8 ether t c (MTBE)e a& 9 8 A 6 a 6 3== a A A A A 8 '' 6 6 A a 8 8 a 8 8 a a a a a Naphthalene Tetrachloroethylene A 6 A 8 A 6 A b 6 A A a a A d A 8 H 9 A A A B A a° a ,. a A z Toluene g 98 8 8 8 ans-1,2-Dichloroethx 8 9_ - A 6 _ - 8 g 9 b R a 8 a 8 8 89 9 9 6 8 8 83 d 8 g Trichloroethylene 2 A Ag B a B 8 S 8 8 S 8 S S 8 8 5 8 8 Vinyl chloride u 8 A A 8 8 A 6 A A a A A A A 8 6 8 A A 0 A 8 A 8 8 8 d= A A 8 A 9 a u g 8 8 8- 8 a -- =- Yleases (total) A 8% 8 - _= 8 8 8 8 8 8 8 = d a _ l,l,l-Trichloroethme 8 8 8 $ 8 8 _ % $ 1,1,2-Trichloroethanc A 8 8 a 6 A A 8 B a $ $ � � � 1,1-Dichloroethane A a a A A _-_ a s 1,2-Dichloroethane DC) A B A A a a d a e 6& 6 A a B a A A 8 A A 6 d A b A A g g8 8 8 88 8 88 8 8 Carbon tetrachloride 8= A e zd S o 8&5_-_ A A 8 8 A 8 A 8 6 9 A A 8888 A A hlomform �tgs romomethane o a 8 a z z ichlorodiftuorometh >> z z a> z z a z z a a z z a a 5 88 8% z a a z z a a z z a a z z a a z a a e A g a 8 A 6 A A A 8 a_ A A A A A A 8 a A g 8 A A 6 a A P A hloromethane m d a Sample ID — tv Sampling Date (mm/d 8 g$ 6 a a A d 6 6 a 6 b$ a 8 e d b A& 8 A b 8 A d hloroethane � n > m i; > ZzaZa06zzz zyz > > za ZbAaezxzz�z:zzz a 8 88 _ > a > a > a a > sec-Butylbenzene r f9 z z z a z a 6 a$ a z za az za 6 6 d a 1,2-Dichlorobenene z a � � i a a a a u A o 8 b z 8 a z z a a z z a s z z a> z z a a z a o= a 8 z 8 a z z a> z z a a z z s a z z s s 1,4-Dichlorobenzene a >= i a r$ zd 8$$ a z r a? a a i a g$$ e r i i a a Z> z 1,2,4 - - - - z richlorobenzene r- i i i a a zd A 8 B z 8 a z z a a> z z z a a> z za z 6 a$ 6 A 8 8 b z 8 a z z s a z z a a z za a z z s>> 1,2,3- z richlorobenzene I a> a a a a g �d A o v e b z 8 a z z a a> z z a z z a a z z a a d z a g e e e_ b z o a z z a s a r_ z r a z z a a 1.2.4- a B rimedrylbenzene A $$$$$ 6 A 8 A A $ b o S g Ag 6 S A 8 B A 6 a $$ A 6 8 8 e S S$ 8 == $ A A a Carbon Disulfide 8 3 — 6 8 b A 8 $ 6 A a z o e g$ g d a g$ 6 6 d 6 g A $ g d b----_ d$ Dibromochlorometha A e 8 8 A a a A A 6 d a b A A A d b A .'a A A 6 A A a 6 A a A 6 d hlorobenzene a y z a z >� zd e e z 8 a> z z r z f> z z a r z r �' z A a g 6 a 8 8_>�> e z z z z a> ,>z z r z z a a z r s A ert-Butylbenzene b -Butanone A 8== 6 a d 8 6 a g A 9 A g a a A 8 8 g A 8 F?; 6 A '8 b d 8 e a b 8 g A a ethylene Chloride � 8 d i - - _ - - - - a Acetone g P SampleID N_$ g g g N N a N Sampling Date (mm/d geg m g b d A 6 6 A b b b A b A 8 9 A A 6 6 A A O � � 8a � � � e � e s `8 enzene m e is-1,2-Dichlorcethyl $ 8 g m ee 8 8 8 s '_ '_ 8 e 8 8 8 8 8 g g 8 8 8� g thylbervene � seaA�-- eAgAaAb?Abeag y`e"-ua 8 8 $ = _ _9 S`g3 98 g $ 8 ether a E n A b g 6 6 6 A b b A g 6 A b 6 g b b A Naphthalene 8 8 8 8$ 8 8 g 8 8 8 8 s 8 8 8 g d 8 A 8 8 8 8 8 A A g B A a 8 B 8 A A s 8 8 S s$$$ 8 2 1 0 8 8 0 S 8 8 A etrachloroethylene g b A 8 6 8 A 8 6 b 3 6 A g 6 g g 8 A A ?3 Toluene A b A 3 6 o A A A A e e b trans-1,2-Dichloroeth A b g g b& g g g b A 8 A 6 8 8 $ 8 8 S 8 g 8 8 8 8 8 richloroethylene >3 vb % it >3 >x 5 b A e A A A B g 6 8 A A b A A b A A A A b A Vinyl chloride 3 6 b A A 6 A 6 8 A 8 8 A A 6 8 Ylenes (total) 1,1,1-Trichloroethane B 1,1,2-Trichloroethane A A b b A 8 8 8 A A A 8 6& 8 6 B A 8 $ $ g 3 $ $ $ g& $ $ $ $ l,l-Dichloroethane 1,2-Dichloroethane 8 $ $ $ $ 8 8 a DC) A 6 g 6 6 6 A 6 6 A g 6 r3 A b A d 6 A A 8 $ $ $ 8 $ $ S Carbon tetrachloride hloroform C d = b g b=_= 8 8 8 romomethane — — — A z z A z z z ichlorodifluoromedh a e g$ggA$AAg$ggA- ABggg Chloromethme p Sample ID e Sampling Date (mm/dd/y e o o A 8 8 8 8 A 6$ 8a A A 8 8 8 8$ hloroethane o 8 m ' o z a z z > > z r z z > a 8 > z z > > z z > > z A > z z > > z z > > -Butylbenzene 8 m A z z z z z z z z z A z z z z z 8 z z z z a> a a a> a a a$> a a a a e a a>>� 8 8 1,2-Dichlorobenzene ..� rn C z z > z z > > z z > > z z a a z a z z > > z z a > z �' a d z z a > z > > l,q-Dichlorobenzene a `— G A z z z z z z z z A z z z z z 8 z z z z > a a> a+ a r a$ a a a a a$ a>++� A a mchl richlorobenzene mM rn ef0i z z a > z z > > z a > z z a a A > z > a z z > > z- a z z > a z z > a 1,2.3- richlorobenzene z z z z z z z z z 8 z z z z z e z z z z 1,2,q- a a a a a a a a> e a a r r> v a a a a 'g S rimethylbenzene m 6 8 8 8 8 = g$ 8 8$ Sg g $ arbon Disulfide A 3 Dibromchlommetha e hlorobenzene z > z > > z z > > > > > Ag, r ert-Butylbenzene d _ _Butanone 6 ethylene Chloride cetone Sample ID 0 8 ;_ g i¢F Sampling Date (mm/dd/y_ S Q g 6 6 6 6 6 6v o 'd "� zd 'd o enzene d m 0 0 ro ro C is-1,2-Dichloroethyle v Z.Yd 'd zd v o v 0 thylbenune ,, y tert- uty e a 'd 'd zd zd o 0 3 3 zd o 3 o a ether ,. a MTBE A 'gg Yd Yd Yd zd �d o 0 zd Yd 8 'd Yd aphtlWme 6 3 6 a A 0 0 0 c zd o o c Z. 0 Tetrachlomethylme 6 9 6 3 .B zd 7d 'd _ u$ g g g o o a o 0 0 0_ 1++1 � z toluene trans-1,2-Dichlor6eth. $ 8 zd o Z. Yd 0 0 �d �d o z' z richloroethylene B 9 B g g o 0 0 zd �d o 0 Z. G 0 0 0 0 Vinyl chloride 0 0 0 0 6 6 6 6 v 0 6 o o 6 'd 6 Xyleries (total) b d& e3 3 8 � 0 c c c z z z z z. z z 0 l,l,l-Trichloroe[hane 8esae o 0 0` 0 1,1,2-Trichloroethane B S 68£ d a 3 3 3 6 = 6`_ = dY v 0 1,1-Dichlomethane S e a v 3- 0 zd c z 0-= z z 0 1,2-Dichlomethme 8 iCarbon DC) e 'g a e a o o v 0 v 0 0 0 0 `o o `o 0 0 0 tetrachloride S� $i666d66666666o6 66 Z Chlomfom e s$ EEg Zo 1.z Z Z Z o 6 z rommethane z �3 8 e3 } z 0 z 0 o z z e e `c 0_ a �d 'd 'z i6chlorodifluommeth e S�ggg66666 6 So6666 hlommethane SampleID e Sampling Date (mm/dd/y o- o v i i i zd zd zd zd dz 'd o '� > y > :sec-Butylbenzene Chloroethane "" c zd o o zd o zd �d zd a zd zd v o o zd c v z '—' zd R g o o v v> 1,2-Dichlorobenzene a z i a 9 6 3$ d b e zd o c o 0 0 o e 3 zd o 1,4-Dichlorobenzene 8 g 8 8 zd zd 'd 3 a o zd 'd zd c 1 > z o richlorobenzene I n �. 9 & 9 9 o o o d' zd zd & o zd zd o 1,2,3- richlorobenzene z a , z z zz z z'z rimethylbenzene 9 8$ aA 9 z 8> z z a a z z a a zz a a zb a> z z a z a arbon Disulfide 9 u n 6 3 e A z z z z z z z zd z d z z z v v v Dibromchloromedia e 6 9 a a o c I c c 'd zd zd hlorobenzene � 8 8 zd zd rd zd Z. 0 o zd o 0 o v 7d zd a Zq- i r a $ 9 ert-Butylbenzene b z > z z a> z z a a z z a> z n> z i a a z a z> -Butanone a 9 9 9 a .4 8 8 zd > d % - o zd o o zd zd zd zd ethylene Chloride 9=- e = z z > > II z z > > z z a a z z a a z z > a z z a > z z a > z z > > Acetone € m i Sample ID Sampling Date (mm/dd/y_ N O m e88888 'e d A A d a b a A b a A o S b A 8 8 A �� a a $80000oov0o00000 6 ° o d m m 0 i e o .- a A 8 b a A $888 A a a A G. 8 A a $88$8 6 a b a 6 a A o 8 go 18e g z00zd0000000000cis- 1,2-DichloroethyIe $$$ 8 8 3 8$ 8$ 8$$$$$� '� ���$ '� 0 0 0 0 0 0 0 0 0 0 0 0 Ethylbenzene __ __ - - 8 8 0 8> g 0 0 0 0 0 0 0 0 0 0 a i a e y tert- uty ether MTBE ro g�$�ges8888888-_ A b A' A a a b a b = a s g0ggg0000000000o00i A A a A Naphthalene v o g g g o A A A a a A A 8 6= o A b a A A - 0 0 za zd 'd 'd 'd etrachloroethylene 0 0 0 8 8 8$ 8 8 0$ g o 0 0 0 o v o 0 0 S 0 0 3 Toluene 0 0 0 0 0 s-1,2-Dichlorcethy - $9 9 9 3 9 9 0 - o o 'd o z 0 0 0 z z z z richloroethylane 0 g g 0 'g v o 0 0 0 z z v o z 0 0 z z 0 0 0 `0 inyl chloride B8 0 0 0 g 8 8 8 8 ' 8 g a 8 8 8 8 g 8$ 0 e " 0 0 0 0 0 0 0 0 Z. Z. 0 0 0 ylenes (total) c 3' 8 8 A 0 0 0 0 0 0 c z = 0 0 0 1,1,1-Trichloroethane 6 B 6 6. a a b a a 6 a A b a A b a b A 9 b 0 0 0z o o `o `d 0 1,1,2-Trichloroethane 6l,l-Dichloroethane 0 g 8 8 8 8 g 0 8g 8 g0 0 0 0 0 0 0 0 0 0 'd 0 0 _ _ _ d a _ 6.00000�z 666 1,2-Dichloroethme DC) = A 8 s$$ A 6 8 8 $8 9 8 P$ B A A d b a 8 8$$ A A A 0$ A a 8 0 0 0 0 0 0 0 o c o `o 0 0 Carbon tetrachloride 6 00 a 6 0 o 0 o 00000 Chlorofom z 0 _ g=_= 0 -_ z 0 v z 0 0 z z 0 0 z 7d 0 z z 0 0 z zd 0 Brurnomethane R z A a g 8$ b b 8 1 8 a b 8 8 8 9 a i> a a a i z a a a i a zY $ B 0 g a a g 1 o 0 0 0 0 0 0 0 0 c o 0 0 0 ichlorodiBuorometh e A A $$8$$ A 8 a b A b a 8 A A A 8 A 88 B A A zd a 9 $ B 0000000080000 0 hlorcnethane � S S m f: SampleID 5 z Q _ e S o e 2_ a o_ c_ e_ g Sampling Date (mm/dd/y, y Y g grg ge ge gg?gg� S 8 i zd zd zd zd zd o o 'd zd zd i s Chloroethane d ;. m a: i az i a a a a a o $ 8 61616 'd 3 zd 3 o zd zd 66 6i -Butylbenzene a m C 6 8 8 8 A 6 8 8 8 A 8 8 az b a 8 d A 8 zd d d zd z. z. z. z.zz 1,2-Dichlorobenne & 8 8 8 8 8>> a> i H a a a a e 3 8 =d zd zd zd 'd o 0 o o 'd 'd 3 1.4-Ihchlorobenzene i fDC 6 8 0 6 A 8 8 d A 8 8 �> > r i i i a i i a a a A a$ A o$$ g d 8 zd zd 'd $ zd dz zd 'd zd zd zd zd 'd 1,2,4 richlorobenzene 6 8 A A A B a 8 a g A o A 8 'g 8 $ o 66zd 3 z. z. 6 6 6 6 6 6a 1,2,3- i richlorobenzene rn 9 6 8 8$ 6 A 8 8 g A 8$ z z a a a za z z z a a>> z z z z a a a za z d z 8 a b zd A d 8 '8 6 '8 6 6 6 g 6 6 6 e o 6 66 6 1,2,4- - - - - - z o o r methylbenzene M m a m a 8 S 8 6 bg S 8 A 8 8 d 8 $ 3 6 8 8 3 8 8 6 8 8 8 5 6 8 ,8 6 8 6? F b zd g z z a s>> z z z z a z z > a z z a a z z a>>> z z Carbon Disulfide S a S 8 6 A 8 d b g g 9 6 d g 8 8 6 8 g A g 6 b d $ 6 zd S d 8 8 gdz o zd zd v 6 o 0 o zd" o zd zd ibrornochlorometha s e B A ss8s8'sgg A A 8 8 g g g 8 s§88s8 A A b g t A g g b $�'a 'S8 end 6 6 6 3 6 c'da�d6 6'd hlorobenzene 6 g 8 8 6 8 8 8 d b 8 8 a a a r r> a: i a> a 8 a 6 o 8 d 6 p v zd 'd 'd v zd 6 zd zd 6$ 'a zd [" i z ert-Butylbenzene 6 d b B d 6 g d 8 6 A 6 8 6--- a 'g z Z. a z 'g z z z z z z z z z z z z - a a a a a AAcetone -Butanone 6 d A B $ $ A A 8 8 g d g o 8 8 8 $ A 8 g g e _ = 6 A 8 A zd 88 8 g a zd a zd zd > o 0 o c a zd zd zd ethylene Chloride 0 8 b -= b d A 8 A A___= a 8 8 z a i a> i> i a i z a i z � m s SamplelD Sampling Date (mm/dd/y, m_ A A 8 8 a a 8 gg a a 8 8$ a 0 d a 8 8 a a 8 8 9 6 8 8 A a g 8 8 8 'g a 6 8 8 A 3 g' 'g a Benzene tv w e ti cis- 1,2-Dichloroethyle A � A 8 d a a a 6 B a 6 a B B a a A A 8 6 A A thylbenzene = a A a A A A 6 a Methyl tert- uty _ 8 8 0 k 8$__- _ 8 8 8 0 her MTBE a A 8 N8�s8g 3 a a A 08g8 A A A A A 6 88g8888t! aphthalene A a A a 3 A A A a 6 a?& a a b 8 A 6 a 3 etrachloroethylene 0 Toluene 8 8 8 8$ 8 8 8 8 8 8 8 8 8 8 8 8 8 8 0trans-1,2-Dichloroeth, 8$ 8$ 8 8 0 g 8 8 G g 8 g 8 g g Frichloroethylene, 0 e 8 0$ 8 0 8 8 e g eg Vinyl chloride g g 8 8$ - B 0 A a a 8 A$ 0 B A b a 8 8 A a 8 8 6 A 8 8 a 6 8 8 b a g Xylenes (total) A688- z_8 ==_aAAa�aA� I, l,l-Trichloroethane tl 1,1,2-Trichloroethane $ o$ A g 0 A a v e a a 3 8 a 6 8 A d 8 b b 8 S a 8 8$ a a 8 l,l-Dichloroethane _= a b 3 ;3 8 a a 8 A A A A a A B A 1,2-Dichloroethane 0Carbon DC) d e o A A 6 d A A $ A a $ 8 88 $ a 8 $ A a tetrachloride 0 8 8 8 8 a Chlorofornt g g 8 8 romomethane 0 A 8 a a z a i A 0 d d 8 g b A 88 3 A a z i a a a a a 'chlorodifluorometh 8 8 88 0 e 8 8 8 A a? 8 0 a 8 8 8 A A g g A a g g a A hloromethane Z Sample ID n Z3 g 8 Sampling Date (mm/d 8 m ii hloroethana z 0 88 z o m e -� 6 z 8 r z r z a z z a a$ z v e e o 0 8 d 8 8 9& 8 8 z z r r z z > a>> z a z z a sec-B uty(benzene zd e 8 8 e z0 6A 'a za0 1,2-Diehlorobenene A z $> z z a a z z a a z v S o> z a z z a> z z r>> z a 1,4-Dichlombenune &Y>Z$�gegeaA>Z>zZ>>z 1,z,4_ g - - richlorobenzene 9 a> a>> 6 a 6 a 3 6 z z z z z z z 1,2,3- richlorobenzene - U2 3 e>10 >>>>$ �d $ 8 A a 8 8 a $ o z z > a z z > > z z > a z,_ r 1,2,4- _ -_ oCarbon rimethylbenzene a veeaaaA S $$ 8 8B saaAasaeAaaaa 8 S g$ 8$ Disulfide v A a A A g 6 z A A b a a v a a 8 A Dibromochlommetha �d e A A $ 8 A g 8$$� A A A �d A A A A 8 a 6 8$ 8 a g$ A A e 8 A 8 8 8 8 8 0� hlorobenzene _ A z> r z z a z > z z z z a z z a z r o ert-Butylbenzene -Butanone zd g^ Methylene Chloride i� >Acetone > _ _ _ _ _ _ A a s a b Sample ID A A A � g SamP linB Date (Y. mm/dd�' •:- 3 � 7 n _ N baeaAababesasaaaaabAaa o'd Benzene '3 0 is-1,2-Dichlorcethyle m A $ a g g g § $ g b a d Ethylbenzene 6 d b b d a 6 d 6 A d 6 d d a 5 a 6 A b d e y tert- uty $ $ $ g $ g S_ $ g ether (MTBE)A b A 8 B d a 9 g b A d b A d a d a d 6 6 d Naphthalene A d A 6= A d 6 A d b a A d 9 A A 6 A A e1 $ g 9 3$ o o$ 8 3 S$$ g Tetrachloroethylene A A A A d a A d A a d a d a b d 6 A A A oluene trans-1,2-Dichlorcethr g g g g 8 = 8 _ g $ g g2 Trichloroethylene 6 d A A A A 6 6 A A A a 8 6 a 6 6 A A Vinyl chloride 6 e1 A b d a b A 6 6 d A d d B a 6 d b A A a zd $ $ g $ $ $ g � g $ Ylenes (total) A e A 6 A A !3 s b= d h A a a d 8 d 8 B e e y I,1,1-Trichloroethane b a b A d a A d 6 6 d b d d a A 1,1,2-Trichloroethane A a A A A d 8 8 6 8 a a d A A 8 A== A A 9 e v g g'g g e c I,1-Dichloroethane A d a A -- -_- a A a 6 =_ _ 1,2-Dichloroethane g$ 3 8 e e g = _- a __ _- EDC) B A 6 A a A A a 6 6 d 8 A A d a 6 d 6 6 6 a Carbon tetrachloride g 5 g§ 8$$ 8 d A 9 d b b 8$ zdChloroform rornomethane 8r3 ichloroditluorometh an z a z z a a z z a z a z z a a z z a z z a a z z a a> z z$ a z� hloromethane b B g A d$ $ 8 e a 6 g $ g d & g 3 g b a g S$ zd a e�ii v e Semple ID n - > Q C _ z �.g..�N N c g g o g$ c c o o o c o? c o ��, g 8 „—� a o .QQZR 2 ampling Date (mm:'i,i� — o — — 2 A V W solved osygrn (DO) ., D D»a D D 90 oo o 'o^ oo D>>,:>a,>> D>N3 irrete ,p a>>>>>>> — = =ApAAAAw �zzzzzzzzzz-z^_zTzzW nlre aaaaaaaaaaa-aoaaa>W - X Z Z Z Z Z Z Z Z Z Z z z z X Z Z Z Z Z Z z z z Z T Z T T z X X z X z Z z Z Z Z 3 jor Cations — aaaaa>>>>aaaaaaa >aa>aaaaaaaaaaaaaaaaaaaa s zzazz�+181A a `� $ $ >8 9 8zzzzz sass>>aaaaag8tiaa zzzzzz�88zz $9 Hans >>>azda>azdzd>c�3� 'd U �dzd zd zdzdaa>>>a>>>>zd>'d>>a>�3 0°"�U°" 6.potential idation red=on a>>>�>>>=>>>>>> a > as > >>a>>>>>>>>>�>�>a>>> e"in' a>>>=>aaoaaa>>> > a >> a >a>>>>>>>>>>�>�>>>>'a hlode(optional) �>>>> ga a> s o> o >>> p and -wit.. 3 — — N > — — — — — — — — w > N a S > m emperature gdW ^oZzz X z Z3 Totalorganic carbonzX >>aa s �> aZa a> ) a88 8 9 S 8zzzzzzzzzzz��gzz88A3 zzzzozzaa8 a aaa�aa$P8$$8$$$aw$Wa>>aaaaaaaaP$gaa$8N z8 lnene A 8 g>Z S 6 - zzzzgzzA888S aaaatiaa$g888$$ $ $ a W =bza>>>>>aaaaP$Paa$§P zzzzzzzzzzogozzga9 ^e"e I o ■.■■0 :i 111 nl■■�■■■el■m I m — Sample m > D Y —,I., De4 (mm/ v y u —Di..Icd oxygen (IX11 Z XT D D goc a — ^ W A oc,c TZ p a ZZZTZZZTg3 D D D D D D D D D o i,mte D Z>>Z o -A �aA��zzzzzzzzzz_ -Pa>aaaaaaa>o wrar ' 0 TXT aaaaaaaaa TTX XT X X ayaaaaaaaaaaaaaay XTXTT XX XXTTZT XTT3 )orc.,iona '�- � 8 8 9 8888 8 8 zS98zzTzzzzzzza� $8$g$$$$ 8 o a===aaaaaaaaaa8N em""' >azd>c c zd a zd'dzd3�>aaaaaaaa>zd aaUO" a a sv = - - > z; - = a > < idalion mdae,ron temial (oxr) aaaaaaaa a a aa> aaaaaaaaa>aa� alinity aaaaaaaa a a aaaaaaaa>aaaaaa� Chloride (optioval) c ondactm 3 H jp am mnurc 9 D>> W a '> D y oral organic carbon mC�(oe) 8 8 9 8 A 8 9 9 ^ 8 ^^ z688zzzzzzzzZ> »aaaa>>>>_,one!pp18__N I 0 m a - �ooSti 0 00000��oggg$„ wphngDat<ca✓a o oN ldd+ -14- 1-1-1- 1p [ii­- .--n a>�g� - zti 0zzzzzzzzzzzzP a ao >aaaaaaaaaaaam ppp�pp za A Pzzzz>Z2> wrt< - a»aaa>aaaaaao 3 Z ZZ Z Z Z Z Z Z Z Z ZZ ZZZ ZZZZZZ3 Cations D D> a D D D D D D a D TIT D D A TIT D a A A D ggggg $ $ Z? 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O >>»>>acao 00 > ? azzzz ZZZ > a a a ZZ a a ZZZZ a a a a asoh-ed Man g°Oei° z zzzzzzo -- - - - 8 zzzzzzzzzzzzz ->>>>aaaaaaaaax 1--, Manganea>aaaa y - zzzzzz888o88 aaasaa W 8 ->aaaaaaaaaa>a zzzzzzzxzzzz ° n;a(rlirogen) zzzzzzo a a a a a a w 'zoa a_ 2z a 8zzzzzzzzzzzzz gaaaaaaaaaaaaa �1e b _ xxxxxxpp�aap l I e a a e 8 8zxzxxxxxxxxxx w,;de a>>aaao >lll _ zzzzzz >>aaaaN ozo aa�-zd z o z -_' zzzz tiaaaa>aaaaaaaa zzzzzzzz o�lhon zza a>aaaN zzzz °oz� Nam zd zd zd zd z�zaazzzIT zzzzzzz aaaaaaa ssolvadlmn >>»>>zdzdzdNzdzd xd = zd xd zd zd>>>>>>>>>>>>>3 °°�ea'°aL°n >> Z>azdzdzdzd'd'd zd zd zd zd zd'daaaaaaaaaaaaa .1-dF.R-I— >>>>>> C c z �C zd>>>>> a>>>>>>> Phophate Table 12 1 : A-I,tical Data for Natural \Ilenuation Parameters (I/ser Specified Parameters) _ _ US( \ ID No.: 920(O1 � A C � Uni s 3/112005 NA NA NA NA NA NA NA NA NA 2/62006 NA NA NA NA NA NA NA NA NA 7/14/2009 NA NA NA NA NA NA NA NA NA 10/7/2009 NA NA INA NA NA NA NA NA NA NA 2/4/2010 NA NA NA NA NA NA NA NA NA 4/2112010 NA NA NA NA NA NA NA NA NA 7/13/2010 NA NA NA NA NA NA NA NA NA 10/20/2010 NA NA I NA NA NA NA NA NA NA NA 426/2011 NA NA NA NA NA NA NA NA NA NA 7272011 NA NA NA NA NA NA NA NA NA NA 11/12011 NA NA NA NA NA NA NA NA NA NA 112512012 NA NA 0.0171 <0,01 <0,05 NA NA NA NA NA MW-IOA 7202012 �O.01 0.0121 0.245 <0.01 <0.05 ND ND 0.07 ND ND 12/32012 �.002 0.0191 0.016J <0.01 <0.05 0.8 ND ND ND ND 2272013 1 0.0436 1 0.0645 0.014J 0.324 <0.05 0.14 ND ND ND ND 5292013 0.00195J (10245 0.012J <0.01 <0.05 0.2 ND ND ND ND 9/122013 NA 0.0243 0.032J 0.907 <0.05 NA NA NA NA NA 12/132013 0.0165 0.166 0.0081 <0.05 <0.05 0.14 ND ND ND ND 3262014 0.0031 0.022 <0.30 <O.010 <2.0 0.1 ND ND ND ND 6/172014 0.0012 0.02 <0.30 NA <2.0 0.75 ND ND ND ND 9252014 0.0018J 0.029 <0.30 0.0045J <2.0 NA NA ND ND ND 12/162014 .00133 0,0017 <0.30 0.0040J <2.0 ND ND ND ND ND 3/182015 OD097 r 0.031 0.15J 0.00471 <2 n ND ND ND ND ND 6/182015 0.0012J 0.017 <030 0,0025J � 211 NID ND ND ND ND 211 NA NA NA NA NA NA NA NA NA NA MW IOB A 2162006 NA NA NA NA NA NA NA NA I NA NA Page 115 of 127 ITa6k 12(11! Analvtieal Data for Natural Attenuation Param t- (I laer q.-MM Paramrt-1 �11 1y I" TM o R o & Units 3/11/2005 NA NA NA NA NA NA NA NA NA NA 11/11/2008 NA NA NA NA NA NA NA NA NA NA 2/4/2009 NA NA NA NA NA NA NA NA NA NA 422009 NA NA NA NA NA NA NA NA NA NA 711412009 NA NA NA NA NA NA NA NA NA NA lo/7/2009 NA NA NA NA NA NA NA NA NA NA 2/42OLO NA NA NA NA NA NA NA NA NA NA 42I2010 NA NA NA NA NA NA NA NA NA NA 7/142010 NA NA NA NA NA NA NA NA NA NA 10202010 NA NA NA NA NA NA NA NA NA NA 7/27/2011 NA. NA NA NA NA NA NA NA NA NA 11/2/2011 NA NA NA NA NA NA NA NA NA NA 1252012 <0.01 0.0133 NA NA NA NA NA NA NA NA MW-IOB 720/2012 NA NA 0.079 0.003J 10.05 ND ND 0.2 ND ND 12/3/2012 NA 0.45 NA < .Ol <0.05 1.2 NA ND NA ND 2272013 NA 3.81 NA 0.637 <0.05 NA NA NA NA NA 5/31/2013 NA 0.211 NA NA NA NA NA NA NA NA 9/122013 NA 0.209 0.042J 1.2 <0.05 NA NA NA NA NA I M I/2013 NA 8.69 NA <0.05 <0.05 NA NA NA NA NA 3/27/2014 0.15 5.4 <0.30 0.0060J <20 NA NA NA NA NA 6/182014 0.081 0.6 <0.30 NA Q.0 0.4 NA ND NA NA 9252014 NA 0.31 <0.30 0.0072J <2.0 NA NA ND ND ND 12/18/2014 NA 0.63 <0.30 <0.010 <2.0 NA NA. 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If you have any questions concerning this report, please feel free to contact me. Sincerely, Lisa A. Worthington Project Manager Table of C ontctits Page 1 of 50 Table of Contents Sample Summary Case Narrative Sample Results 15F0751-01 15F0751-02 15F0751-03 15F0751-04 15F0751-05 15F0751-06 15F0751-07 15F0751-08 15F0751-09 Sample Preparation Information QC Data Volatile Organic Compounds by GUMS B 124590 Miscellaneous Organic Analyses B 124549 Metals Analyses (Total) B 124627 Metals Analyses (Dissolved) B 124344 Conventional Chemistry Parameters by EPA/APHA/SW-846 Methods (Total) B 124259 B 124369 B 124383 4 5 6 6 8 10 12 14 16 18 24 30 32 34 34 34 38 38 39 39 40 40 41 41 41 41 Page 2 of 50 Table of Contents (continued) B 124441 B124521 B 124620 Flag/Qualifier Summary Certifications Chain of Custody/Sample Receipt 41 42 42 43 44 47 Page 3 of 50 con-toto ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 4131525-6405' TEL. 413/525-2332 Cardno ATC Associates - Raleigh NC 2725 East Millbrook Road, Ste 121 REPORT DATE: 6/23/2015 Raleigh, INC 27604 PURCHASE ORDER NUMBER: ATTN: Justin Ballard PROJECT NUMBER: [none] ANALYTICAL SUMMARY WORK ORDER NUMBER: 15FO751 The results of analyses performed on the following samples submitted to the CON -TEST Analytical Laboratory are found in this report. PROJECT LOCATION: Pro Cleaners FIELD SAMPLE # LAB ID: MATRIX SAMPLE DESCRIPTION TEST SUB LAB 8401 Camellia 15FO751-01 Water SW-846 8260B 8404 Camellia 15F0751-02 Water SW-846 8260B 8405 Camellia 15F0751-03 Water SW-846 8260B 8408 Camellia 15FO751-04 Water SW-846 8260B 8404Azalea 15FO751-05 Water SW-8468260B 8405 Azalea 15F0751-06 Water SW-846 8260B MW-24S 15F0751-07 Ground Water 3810-RSK175 ASTM D516-90, 02 SM 21-22 4500 NO2 B SM 21-22 4500 NO3 F SM 5310C SM 19-22 4500 NH3 C SM21-22 450OS-F SW-846 6020A SW-846 8260B MW-24D 15FO751-08 Ground Water 3810-RSK175 ASTM D516-90, 02 SM 21-22 4500 NO2 B SM 21-22 4500 NO3 F SM 5310C SM19-22 4500 NH3 C SM21-22 450OS-F S W-846 6020A S W-846 8260B 8409 Camellia 15FO751-09 Water SW-846 8260B Page 4 of 50 ion-te tO ANALYTICAL LABORATORY 39 Spruce Street ` East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 CASE NARRATIVE SUMMARY All reported results are within defined laboratory quality control objectives unless listed below or otherwise qualified in this report. For method 6020, 2x dilutions performed due to standard operating procedures. SM 5310C Qualifications: MS-11 Matrix spike recovery outside of control limits. Possibility of sample matrix effects that lead to a high bias for reported result or non -homogeneous sample aliquots cannot be eliminated. Analyte & Samples(s) Qualified: Total Organic Carbon 15F0751-07[MW-24S],B124383-MSI SW-846 8260B Qualifications: L-02 Laboratory fortified blank/laboratory control sample recovery and duplicate recoveries outside of control limits. Data validation is not affected since all results are "not detected" for associated samples in this batch and bias is on the high side. Analyte & Samples(s) Qualified: Acetone B124590-BS1,B124590-BSD1 V-05 Continuing calibration did not meet method specifications and was biased on the low side for this compound. Increased uncertainty is associated with the reported value which is likely to be biased on the low side. Analyte & Samples(s) Qualified: 2,2-Dichloropropane 15F0751-01[8401 Camellia], 15F0751-02[8404 Camellia], 15F0751-03[8405 Camellia], 15F0751-04[8408 Camellia], 15F0751-05[8404 Azalea], 15F0751-06[8405 Azalea], 15F0751-07[MW-24S], 15F0751-08[MW-24D], 15F0751-09[8409 Camellia], B124590-BLKI, B124590-BSI, B124590-BSDI The results of analyses reported only relate to samples submitted to the Con -Test Analytical Laboratory for testing. I certify that the analyses listed above, unless specifically listed as subcontracted, if any, were performed under my direction according to the approved methodologies listed in this document, and that based upon my inquiry of those individuals immediately responsible for obtaining the information, the material contained in this report is, to the best of my knowledge and belief, accurate and complete. Daren J. Damboragian Laboratory Manager Page 5 of 50 acon-atesto ANALYTICAL LABORATORY Table of Contents 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/16/2015 Field Sample #: 9401 Camellia Sampled: 6/15/2015 11:30 Sample ID: 15FO751-01 Sample Matrix: Water Volatile Organic Compounds by CC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Acetone ND 0.050 0.0047 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD Benzene ND 0.0010 0.000079 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD Bromobenzene ND 0.0010 0.000044 mg/L 1 SW-846 8260B 6/22/15 6/23/15 2:41 LBD Bromochloromethane ND 0.0010 0.00022 mg/L 1 SW-846 8260B 6/22/15 6/23/15 2:41 LBD Bromodichloromethane ND 0.00050 0.000088 mg/L 1 SW-846 8260B 6/22/15 6/23/15 2:41 LBD Bromoform ND 0.0010 0.00021 mg/L 1 SW-846 8260B 6/22/15 6/23115 2:41 LBD Bromomethane ND 0.0020 0.00094 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD 2-Butanone (MEK) ND 0.020 0.0024 mg/L 1 SW-846 8260B 6/22/15 6/23/15 2:41 LBD n-Butylbenzene ND 0.0010 0.000054 mg/L 1 SW-846 8260B 6/22/15 6/23/15 2:41 LED sec-Butylbenzene ND 0.0010 0.000084 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD tert-Butylbenzene ND 0.0010 0.000096 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD Carbon Disulfide ND 0.0040 0.0010 mg/L 1 SW-846 8260B 6/22/15 6/23/15 2:41 LBD Carbon Tetrachloride ND 0.0050 0.00010 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD Chlorobenzene ND 0.0010 0.00012 mg/L 1 SW-8468260E 622/15 6/23/15 2:41 LBD Chlorodibromomethane ND 0.00050 0.000054 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD Chloroethane ND 0.0020 0.00016 mg/L 1 SW-846 8260B 6/22115 6/23/15 2:41 LBD Chloroform ND 0.0020 0.00014 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD Chloromethane ND 0.0020 0.00032 mg/L 1 SW-9468260B 622/15 623/15 2:41 LBD 2-Chlorotoluene ND 0.0010 0.000070 mg/L 1 SW-8468260B 622/15 623/15 2:41 LBD 4-Chlorotoluene ND 0.0010 0.000074 mg/L 1 SW-8468260B 6/22/15 623/15 2:41 LBD 1,2-Dibromoethane (EDB) ND 0.00050 0.000089 mg/L 1 SW-846 8260B 6/22/15 623/15 2:41 LBD 1,2-Dichlorobenzene ND 0.0010 0.000076 mg/L I SW-8468260B 6/22/15 623/15 2:41 LBD 1,3-Dichlorobenzene ND 0.0010 0.000079 mg/L 1 SW-846 8260B 6/22/15 623/15 2:41 LBD 1,4-Dichlorobenzene ND 0.0010 0.000046 mg/L I SW-8468260B 6/22/15 6/23/15 2:41 LBD Dichlorodifluoromethane (Freon 12) ND 0.0020 0.00012 mg/L I SW-846 8260B 622/15 623/15 2:41 LBD 1,1-Dichloroethane ND 0.0010 0.00016 mg/L 1 SW-8468260B 622/15 623/15 2:41 LBD 1,2-Dichloroethane ND 0.0010 0.00019 mg/L I SW-846 8260B 622/15 623/15 2:41 LBD 1,1-Dichloroethylene ND 0.0010 0.00021 mg/L 1 SW-8468260B 622115 6/23/15 2:41 LBD cis-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L 1 SW-8468260B 622/15 623/15 2:41 LBD trans-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L 1 SW-846 8260B 622J15 623/15 2:41 LBD 1,2-Dichloropropane ND 0.0010 0.00011 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD 1,3-Dichloropropane ND 0.00050 0.000099 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD 2,2-Dichloropropane ND 0.0010 0.000072 mg/L 1 V-05 SW-846 8260B 622/15 623/15 2:41 LBD 1,1-Dichloropropene ND 0.0020 0.00013 mg/L I SW-846 8260B 6/22/15 623/15 2:41 LBD cis-1,3-Dichloropropene ND 0.00050 0.000062 mg/L 1 SW-8468260B 622/15 623/15 2:41 LBD hens-1,3-Dichloropropene ND 0.00050 0.000056 mg/L I SW-846 8260B 622/15 623/15 2:41 LBD Diisopropyl Ether (RIPE) ND 0.00050 0.00018 mg/L 1 SW-846 8260E 622/15 623/15 2:41 LBD Ethylbenzene ND 0.0010 0.000092 mg/L 1 SW-8468260B 622/15 623/15 2:41 LBD 2-Hexanone (MBK) ND 0.010 0.0015 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD Isopropylbenzene (Cumene) ND 0.0010 0.00011 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD p-Isopropyltoluene (p-Cymene) ND 0.0010 0.00012 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD Methyl tert-Butyl Ether (MTBE) ND 0.0010 0.00W90 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD Methylene Chloride ND 0.0050 0.0032 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD 4-Methyl-2-pentanone(MIBK) ND 0.010 0.0015 mg/L 1 SW-8468260B 6/22/15 623/15 2:41 LBD Page 6 of 50 �1 I con-Usto ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/1612015 Field Sample M: 8401 Camellia Sampled: 6/15/2015 11:30 Sample ID: 15FO751-01 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/rime Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Naphthalene ND 0.0050 0.00012 mg/L 1 SW-846 8260B 6/22/15 6/23/15 2:41 LBD n-Propylbenzene ND 0.0010 0.000094 mg/L I SW-846 8260B 6/22/15 6/23/15 2:41 LBD Styrene NO 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD 1,1,2,2-Tetmchloroethane ND 0.00050 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 2:41 LBD Tetrachloroethylene ND 0.00050 0.000080 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD Toluene ND 0.0010 0.000090 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD 1,2,3-Trichlorobenzene ND 0.0050 0.00014 mg/L I SW-846 8260B 6/22/15 6/23/15 2:41 LBD 1,2,4-Trichlorobenzene ND 0.0020 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD 1,1,1-Trichloroethane ND 0.0010 0.000094 mg/L I SW-8468260B 6/22/15 6/23/15 2:41 LBD 1,1,2-Trichloroethane ND 0.0010 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 2:41 LBD Trichloroethylene ND 0.0010 0.000077 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD Trichlorofluoromethane(Freon 11) ND 0,0020 0.00015 mg/1, 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD 1,2,3-Trichloropropane ND 0.0020 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 2:41 LBD 1,2,4-Trimethylbenzene ND 0.0010 0.00018 mg/L 1 SW-8468260B 6/22/15 6/23/15 2:41 LBD 1,3,5-Trimethylbenzene ND 0.0010 0.00010 mg/L 1 SW-8468260B 622/15 6/23/15 2:41 LBD Vmyl Acetate ND 0.020 0.0013 mg/L 1 SW-8468260B 622/15 623/15 2:41 LBD Vinyl Chloride ND 0.0020 0.00013 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD m+p Xylene ND 0.0020 0.00018 mg/L 1 SW-846 8260B 622/15 623/15 2:41 LBD o-Xylene ND 0.0010 0.00011 mg/L 1 SW-846 8260B 622/15 6/23/15 2:41 LBD Surrogates % Recovery Recovery Limits Flag/Qua] I,2-Dichloroethane-d4 106 70-130 623/15 2:41 Toluene-d8 101 70-130 6/23/15 2:41 4-Bromofluorobenzene 95.8 70-130 6/23/15 2:41 Page 7 of 50 I con -test® ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15FO751 Date Received: 6/16/2015 Field Sample #: 8404 Camellia Sampled: 6/15/2015 12:35 Sample ID: 15F0751-02 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qua] Method Prepared Analyzed Analyst Acetone ND 0.050 0.0047 mg/L 1 SW-846 8260B 6/22/15 623/15 3:13 LBD Benzene ND 0.0010 0.000079 mg/L 1 SW-846 8260B 6/22/15 623/15 3:13 LBD Bromobenzene ND 0.0010 0.000044 mg/L 1 SW-846 8260B 6/22/15 623/15 3:13 LBD Bromochloromethane ND 0.0010 0.00022 mg/L 1 SW-846 8260B 6/22/15 623/15 3:13 LBD Bromodichloromethane ND 0.00050 0.000088 mg/L 1 SW-8468260B 6/22/15 623/15 3:13 LBD Bromoform ND 0.0010 0.00021 mg/L I SW-8468260B 6/22/15 6/23/15 3:13 LBD Bromomethane ND 0.0020 0.00094 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD 2-Butanone(MEK) ND 0.020 0.0024 mg/L 1 SW-8468260B 6/22/15 623/15 3:13 LBD n-Butylbenzene ND 0.0010 0.000054 mg/L I SW-8468260B 622/15 6/23/15 3:13 LBD sec-Butylbenzene ND 0.0010 0.000084 mg/L I SW-8468260B 622/15 6/23/15 3:13 LBD tert-Butylbenzene ND 0.0010 0.000096 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD Carbon Disulfide ND 0.0040 0.0010 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD Carbon Tetrachloride ND 0.0050 0.00010 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD Chlorobenzene ND 0.0010 0.00012 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD Chlorodibromomethane ND 0.00050 0.000054 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD Chloroethane ND 0.0020 0.00016 mg/L 1 SW-8468260B 622/15 6/23/15 3:13 LBD Chloroform 0.00026 0.0020 0.00014 mg/L I J SW-8468260B 6/22/15 6/23/15 3:13 LBD Chloromethane ND 0.0020 0.00032 mg/L I SW-8468260B 622/15 623/15 3:13 LBD 2-Chlorotoluene ND 0.0010 0.000070 mg/L 1 SW-8468260B 6/22/15 623/15 3:13 LBD 4-Chlorotoluene ND 0.0010 0.000074 mg/L 1 SW-8468260B 6/22/15 623/15 3:13 LBD 1,2-Dibromoethane (EDB) ND 0.00050 0.000089 mg/L 1 SW-846 8260B 622/15 623/15 3:13 LBD 1,2-Dichlorobenzene ND 0.0010 0.000076 mg/L 1 SW-8468260B 6/22/15 623/15 3:13 LBD 1,3-Dichlorobenzene ND 0.0010 0.000079 mg/L 1 SW-846 8260B 622/15 623/15 3:13 LBD 1,4-Dichlorobenzene ND 0.0010 0.000046 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD Dichlorodifluoromethane(Freon 12) ND 0.0020 0.00012 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD 1,1-Dichloroethane ND 0.0010 0.00016 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD 1,2-Dichloroethane ND 0.0010 0.00019 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD I,I-Dichloroethylene ND 0.0010 0.00021 mg/L I SW-8468260B 622/15 623/15 3:13 LBD cis-1,2-Dichloroethylene 0.0080 0.0010 0.00015 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD trans-1,2-Dichloroethylene 0.00031 0.0010 0.00015 mg/L 1 J SW-8468260B 6/22/15 623/15 3:13 LBD 1,2-Dichloropropane ND 0.0010 0.00011 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD 1,3-Dichloropropane ND 0.00050 0.000099 mg/L 1 SW-8468260B 6/22/15 623/15 3:13 LBD 2,2-Dichloropropane ND 0.0010 0.000072 mg/L 1 V-05 SW-8468260B 6/22/15 623/15 3:13 LBD 1,1-Dichloropropene ND 0.0020 0.00013 mg/L 1 SW-8468260B 622/15 623/15 3:13 LBD cis-1,3-Dichloropropene ND 0.00050 0.000062 mg/L I SW-8468260B 622/15 623/15 3:13 LED trans-1,3-Dichloropropene ND 0.00050 0.00W56 mg/L I SW-8468260B 622/15 623/15 3:13 LBD Diisopropyl Ether (RIPE) ND 0.00050 0.00018 mg/L I SW-846 8260B 622/15 623/15 3:13 LBD Ethylbenzene ND 0.0010 0.000092 mg/L 1 SW-846 8260B 622/15 623/15 3:13 LBD 2-Hexanone (MBK) ND 0.010 0.0015 mg/L I SW-846 8260B 6/22/15 623/15 3:13 LBD Isopropylbenzene (Cumene) ND 0.0010 0.00011 mg/L 1 SW-846 8260B 622/15 623/15 3:13 LBD p-Isopropyltoluene (p-Cymene) ND 0.0010 0.00012 mg/L 1 SW-846 8260B 622/15 6/23/15 3:13 LBD Methyl tert-Butyl Ether (MTBE) ND 0.0010 0.000090 mg/L 1 SW-846 8260B 622/15 623/15 3:13 LBD Methylene Chloride ND 0.0050 0.0032 mg/L 1 SW-846 8260B 622/15 623/15 3:13 LBD 4-Methyl-2-pentanone (MIBK) ND 0.010 0.0015 mg/L 1 SW-846 8260B 622/15 623/15 3:13 LBD Page 8 of 50 III on -at` t© ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/16/2015 Field Sample N: 8404 Camellia Sampled: 6/15/2015 12:35 Sample ID: 15F0751-02 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Naphthalene ND 0.0050 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD n-Propylbenzene ND 0.0010 0.000094 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD Styrene ND 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD 1,1,2,2-Tetmchloroethane ND 0.00050 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 3:13 LBD Tetr-achloroethylene ND 0.00050 0.000080 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD Toluene ND 0.0010 0.000090 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:13 LBD 1,2,3-Trichlorobenzene ND 0.0050 0.00014 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD 1,2,4-Trichlorobenzene ND 0.0020 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD 1, 1, 1 -Trichloroethane ND 0.0010 0.000094 mg/L I SW-8468260B 6/22/15 6/23/15 3:13 LBD 1,1,2-Trichloroethane ND 0.0010 0.00012 mg/L l SW-8468260B 6/22/15 6/23/15 3:13 LBD Trichlomethylene 0.0023 0.0010 0.000077 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD Trichlomfluoromethane (Freon 11) ND 0.0020 0.00015 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD 1,2,3-Trichloropropane ND 0.0020 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 3:13 LBD 1,2,4-Trimethylbenzene ND 0.0010 0.00018 mg/L I SW-8468260B 6/22/15 6/23/15 3:13 LBD 1,3,5-Trimethylbenzene ND 0.0010 0.00010 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD Vinyl Acetate ND 0.020 0.0013 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:13 LBD Vinyl Chloride ND 0.0020 0.00013 mg/L t SW-8468260B 6/22/15 6/23/15 3:13 LBD m+pXylene ND 0.0020 0.00018 mg/L I SW-8468260B 6/22/15 6/23/15 3:13 LBD o-Xylene ND 0.0010 0.00011 mg/L I SW-846 8260B 6/22/15 6/23/15 3:13 LBD Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 103 70-I30 6/23/15 3:13 Toluene-d8 101 70-130 6/23/15 3:13 4-Bromofluorobenzene 95.1 70-130 6/23/15 3:13 Page 9 of 50 con-atesto ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15FO751 Date Received: 6/16/2015 Field Sample #: 8405 Camellia Sampled: 6/15/2015 11:50 Sample ID: 15F0751-03 Sample Matrix: Water Volatile Organic Compounds by GC/MS Analyte Results RL DL Units Dilution Flag/Qual Method Date Prepared Date/Time Analyzed Analyst Acetone ND 0.050 0.0047 mg/L l SW-846 8260B 6/22/15 6/23/15 3:45 LBD Benzene ND 0.0010 0.000079 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD Bromobenzene ND 0.0010 0.000044 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD Bromochloromethane ND 0.0010 0.00022 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD Bromodichloromethane ND 0.00050 0.000088 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD Bromofonn ND 0.0010 0.00021 mg/L I SW-8468260B 6/22/15 6/23/15 3:45 LBD Bromomethane ND 0.0020 0.00094 mg/L I SW-8468260B 622/15 6/23/15 3:45 LBD 2-Butanone (MEK) ND 0.020 0.0024 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD n-Butylbenzene ND 0.0010 0.000054 mg/L 1 SW-8468260B 622/15 623/15 3:45 LBD sec-Butylbenzene ND 0.0010 0.000084 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD tert-Butylbenzene ND 0.0010 0.000096 mg/L 1 SW-8468260B 622/15 623/15 3:45 LBD Carbon Disulfide ND 0.0040 0.0010 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD Carbon Tetrachloride ND 0.0050 0.00010 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD Chlorobenzene ND 0.0010 0.00012 mg/L 1 SW-846 8260B 6/22/15 623/15 3:45 LBD Chlorodibromomethane 0.00026 0.00050 0.000054 mg/L 1 J SW-8468260B 622/15 623/15 3:45 LBD Chloroethane ND 0.0020 0.00016 mg/L 1 SW-8468260B 622/15 623/15 3:45 LBD Chloroform 0.00049 0.0020 0.00014 mg/L 1 J SW-8468260B 622/15 6/23/15 3:45 LBD Chloromethane ND 0.0020 0.00032 mg/L 1 SW-8468260B 622/15 6/23/15 3:45 LBD 2-Chlorotoluene ND 0.0010 0,000070 mg/L 1 SW-8468260B 622/15 6/23/15 3:45 LBD 4-Chlorotoluene ND 0.0010 0.000074 mg/L 1 SW-846 8260B 622/15 6/23/15 3:45 LBD 1,2-Dibromoethane(EDB) ND 0.00050 0.000089 mg/L 1 SW-8468260B 622/15 6/23/15 3:45 LBD 1,2-Dichlorobenzene ND 0.0010 0.000076 mg/L 1 SW-8468260B 622/15 623/15 3:45 LBD 1,3-Dichlorobenzene ND 0.0010 0.000079 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD 1,4-Dichlorobenzene ND 0.0010 0.000046 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD Dichlorodifluoromethane (Freon 12) ND 0.0020 0.00012 mg/L 1 SW-846 8260B 6/22/15 623/15 3:45 LBD 1,1-Dichloroethane ND 0.0010 0.00016 mg/L 1 SW-8468260E 6/22/15 623/15 3:45 LBD 1,2-Dichloroethane ND 0.0010 0.00019 mg/L 1 SW-8468260B 622/15 623/15 3:45 LBD 1,1-Dichloroethylene ND 0.0010 0.00021 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD cis-1,2-Dichloroethylene 0.00033 0.0010 0.00015 mg/L 1 J SW-846 8260B 622/15 623/15 3:45 LBD trans-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L 1 SW-8468260B 6/22/15 623/15 3:45 LBD 1,2-Dichloropropane ND 0.0010 0.00011 mg/L 1 SW-8468260E 622/15 623/15 3:45 LBD 1,3-Dichloropropane ND 0.00050 0.000099 mg/L I SW-8468260B 622/15 623/15 3:45 LBD 2,2-Dichloropropane ND 0.0010 0.000072 mg/L I V-05 SW-9468260B 622/15 623/15 3:45 LBD 1,1-Dichloropropene ND 0.0020 0.00013 mg/L 1 SW-8468260E 622/15 623/15 3:45 LBD cis-1,3-Dichloropropene ND 0.00050 0.000062 mg/L I SW-8468260E 622/15 623/15 3:45 LBD trans-1,3-Dichloropropene ND 0.00050 0.000056 mg/L 1 SW-8468260B 622/15 623/15 3:45 LBD Diisopropyl Ether (DIPE) ND 0.00050 0.00018 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD Euylbenzene ND 0.0010 0.000092 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD 2-Hexanone (MBK) ND 0.010 0.0015 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD Isopropylbenzene(Cumene) ND 0.0010 0.00011 mg/L 1 SW-8468260B 622/15 623/15 3:45 LBD p-Isopropyltoluene (p-Cymene) ND 0.0010 0.00012 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD Methyl tert-Butyl Ether (MTBE) ND 0.0010 0.000090 mg/L 1 SW-846 8260B 622/15 623/15 3:45 LBD Methylene Chloride ND 0.0050 0.0032 mg/L 1 SW-8468260B 622/15 623/15 3:45 -LBD 4-Methyl-2-pentanone(MIBK) ND 0.010 0.0015 mg/L 1 SW-8468260B 622/15 6/23/15 3:45 LBD Page 10 & 50 core -test° ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15FO751 Date Received: 6/16/2015 Field Sample N: 8405 Camellia Sampled: 6/15/2015 11:50 Sample ID: 15FO751-03 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Naphthalene ND 0.0050 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD n-Propylbenzene ND 0.0010 0.000094 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD Styrene NO 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD 1,1,2,2-Tetrachloroethane ND 0.00050 0.00012 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD Tetrachloroethylene ND 0.00050 0.000080 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD Toluene ND 0.0010 0.000090 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD 1,2,3-Trichlorobenzene ND 0.0050 0.00014 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD 1,2,4-Trichlorobenzene ND 0.0020 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD 1, 1, 1 -Trichloroethane ND 0.0010 0.000094 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD 1,1,2-Trichloroethane ND 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD Trichloroethylene ND 0.0010 0.000077 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD Trichlorofluoromethane (Freon 11) ND 0.0020 0.00015 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD 1,2,3-Trichloropropane ND 0.0020 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD 1,2,4-Trimethylbenzene ND 0.0010 0.00018 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD 1,3,5-Trimethylbenzene ND 0.0010 0.00010 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD Vinyl Acetate ND 0.020 0.0013 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD Vinyl Chloride ND 0.0020 0.00013 mg/L 1 SW-8468260B 6/22/15 6/23/15 3:45 LBD m+p Xylene ND 0.0020 0.00018 mg/L 1 SW-846 8260B 6/22/15 6/23/15 3:45 LBD o-Xylene ND 0.0010 0.00011 mg/L I SW-8468260B 6/22/15 6/23/15 3:45 LBD Surrogates % Recovery Recovery Limits Flag/Qua] 1,2-Dichloroethane-d4 105 70-130 6/23/15 3:45 Toluene-d8 99.7 70-130 6/23/15 3:45 4-Bromofluorobenzene 93.4 70-130 6/23/15 3:45 Page 11 of 50 40 con-Usto ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/16/2015 Field Sample #: 8408 Camellia Sampled: 6/15/2015 12:20 Sample 1D: 15FO751-04 Sample Matrix: Water Volatile Organic Compounds by GC/MS Analyse Results RL DL Units Dilution Flag/Qual Method Date Prepared Date/Time Analyzed Analyst Acetone ND 0.050 0.0047 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Benzene ND 0.0010 0.000079 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Bromobenzene ND 0.0010 0.000044 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD Bromochloromethane ND 0.0010 0.00022 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Bromodichloromethane ND 0.00050 0.000088 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD Bromoform ND 0.0010 0.00021 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD Bromomethane ND 0.0020 0.00094 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD 2-Butanone (MEK) ND 0.020 0.0024 mg/L 1 SW-846 8260B 6/22115 6/23/15 4:17 LBD n-Butylbenzene ND 0.0010 0.000054 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD sec-Butylbenzene ND 0.0010 0.000084 mg/L 1 SW-8468260B 622/15 6/23/15 4:17 LBD tert-Butylbenzene ND 0.0010 0.000096 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD Carbon Disulfide ND 0.0040 0.0010 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD Carbon Tetrachloride ND 0.0050 0.00010 mg/L 1 SW-8468260E 622/15 623/15 4:17 LBD Chlorobenzene ND 0.0010 0.00012 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD Chlorodibromomethane ND 0.00050 0.000054 mg/L 1 SW-8468260B 6/22115 623/15 4:17 LBD Chloroethane ND 0.0020 0.00016 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Chloroform 0.00038 0.0020 0.00014 mg/L 1 J SW-8468260B 6/22/15 623/15 4:17 LBD Chlommethane ND 0.0020 0.00032 mg/L 1 SW-8468260B 6/22/15 623/15 4:17 LBD 2-Chlorotoluene ND 0.0010 0.000070 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD 4-Chlorotoluene ND 0.0010 0.000074 mg/L I SW-8468260B 622/15 623/15 4:17 LBD 1,2-Dibromoethane (EDB) ND 0.00050 0.000089 mg/L I SW-846 8260B 622/15 623/15 4:17 LBD 1,2-Dichlorobenzene ND 0.0010 0.000076 mg/L 1 SW-846 8260B 622/15 623/15 4:17 LBD 1,3-Dichlorobenzene ND 0.0010 0.000079 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD 1,4-Dichlorobenzene ND 0.0010 0.000046 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD Dichlorodifluoromethane (Freon 12) ND 0.0020 0.00012 mg/L 1 SW-846 8260B 6/22/15 623/15 4:17 LBD l,l-Dichloroethane ND 0.0010 0.00016 mg/L I SW-8468260E 622/15 623/15 4:17 LBD 1,2-Dichloroethane ND 0.0010 0.00019 mg/L 1 SW-846 8260B 622/15 6/23/15 4:17 LBD 1,1-Dichloroethylene ND 0.0010 0.00021 mg/L 1 SW-846 8260B 6/22/15 623/15 4:17 LBD cis-1,2-Dichloroethylene 0.0032 0.0010 0.00015 mg/L 1 SW-846 8260E 6/22/15 623/15 4:17 LBD trans-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L I SW-946 8260B 622115 623/15 4:17 LBD 1,2-Dichloropropene ND 0.0010 0.00011 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD 1,3-Dichloropropene ND 0.00050 0.000099 mg/L 1 SW-846 8260B 622/15 623/15 4:17 LBD 2,2-Dichloropropane ND 0.0010 0.000072 mg/L 1 V-05 SW-8468260B 6/22/15 6/23/15 4:17 LBD 1, 1 -Dichloropropene ND 0.0020 0.00013 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD cis-1,3-Dichloropropene ND 0.00050 0.000062 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD trans-1,3-Dichloropropene ND 0.00050 0.000056 mg/L 1 SW-846 8260B 622/15 623/15 4:17 LBD Diisopropyl Ether (RIPE) ND 0.00050 0.00018 mg/L 1 SW-846 8260B 622/15 623/15 4:17 LBD Ethylbenzene ND 0.0010 0.000092 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD 2-Hexanone(MBK) ND 0.010 0.0015 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD Isopropylbenzene(Cumene) ND 0.0010 0.00011 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD p-Isopropyltoluene(p-Ctymene) ND 0.0010 0.00012 mg/L 1 SW-8468260B 622115 623/15 4:17 LBD Methyl tert-Butyl Ether (MTBE) ND 0.0010 0.000090 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD Methylene Chloride ND 0.0050 0.0032 mg/L 1 SW-8468260B 622/15 623/15 4:17 LBD 4-Methyl-2-pentanone(MIBK) ND 0.010 0.0015 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Page 12 of 50 Table of Contents on-te to ANALYTICAL LABORATORY 39 Spruce Street* East Longmeadow, MA 01028' FAX 413/525-6405 'TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/16/2015 Field Sample #: 8408 Camellia Sampled: 6/15/2015 12:20 Sample ID: 15FO751-04 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/Time Analyse Results RL DL Units Dilution Flag/Qua[ Method Prepared Analyzed Analyst Naphthalene ND 0.0050 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD n-Propylbenzene ND 0.0010 0.000094 mg/L 1 SW-8468260B 6/22115 6/23/15 4:17 LBD Styrene ND 0.0010 0.00012 mg/L l SW-8468260B 6/22/15 6/23/15 4:17 LBD 1,1,2,2-Tetrachloroethane ND 0.00050 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Tetrachloroethylene ND 0.00050 0.000080 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Toluene ND 0.0010 0.000090 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD 1,2,3-Trichlorobenzene ND 0.0050 0.00014 mg/L I SW-8468260B 6/22/15 6/23/15 4:17 LBD 1,2,4-Trichlorobenzene ND 0.0020 0.00012 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD 1, 1, 1 -Trichloroethane ND 0.0010 0.000094 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:17 LBD 1,1,2-Trichloroethane ND 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Trichloroethylene 0.00061 0.0010 0.000077 mg/L 1 J SW-846 8260B 6/22/15 6/23/15 4:17 LBD Trichlorofluoromethane (Freon 11) ND 0.0020 0.00015 mg/L I SW-846 8260B 6/22/15 6/23/15 4:17 LBD 1,2,3-Trichloropropane ND 0.0020 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 4:17 LBD 1,2,4-Trimethylbenzene ND 0.0010 0.00018 mg/L I SW-8468260B 6/22/15 6/23/15 4:17 LBD 1,3,5-Trimethylbenzene ND 0.0010 0.00010 mg/L I SW-8468260B 6/22/15 6/23/15 4:17 LBD Vinyl Acetate ND 0.020 0.0013 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:17 LBD Vinyl Chloride ND 0.0020 0.00013 mg/L I SW-846 8260E 6/22/15 6/23/15 4:17 LBD m+p Xylene ND 0.0020 0.00018 mg/L I SW-846 8260B 6/22/15 6/23/15 4:17 LBD o-Xylene ND 0.0010 0.00011 mg/L I SW-846 8260B 6/22/15 6/23/15 4:17 LBD Surrogates % Recovery Recovery Limits Flag/Qua] 1,2-Dichloroethane-d4 105 70-130 6/23/15 4:17 Toluene-d8 101 70-130 6/23/15 4:17 4-Bromofluorobenzene 94.8 70-130 6/23/15 4:17 Page 13 of 50 con-te tO ANALYTICAL LABORATORY 39 Spruce Street • East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/16/2015 Field Sample #: 8404 Azalea Sampled: 6/15/2015 11:00 Sample ID: 15FO751-05 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Acetone ND 0.050 0.0047 mg/L 1 SW-8468260E 6/22/15 6/23/15 4:48 LED Benzene ND 0.0010 0.000079 mg/L 1 SW-8468260E 6/22/15 6/23/15 4:48 LBD Bromobenzene NO 0.0010 0.000044 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Bromochloromethane NO 0.0010 0.00022 mg/L I SW-8468260B 6/22115 6/23/15 4:48 LBD Bromodichloromethane NO 0.00050 0.000088 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Bromofonn ND 0,0010 0.00021 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD Bromomethane ND 0.0020 0.00094 mg/L I SW-846 8260B 6/22115 6/23115 4:48 LBD 2-Butanone(MEK) ND 0.020 0.0024 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD n-Butylbenzene ND 0.0010 0.000054 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD sec-Butylbenzene ND 0.0010 0.000084 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD tert-Butylbenzene ND 0.0010 0.000096 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Carbon Disulfide ND 0.0040 0.0010 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:48 LBD Carbon Tetrachloride ND 0.0050 0.00010 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:48 LBD Chlorobenzene ND 0.0010 0.00012 mg/L I SW-846 8260B 6/22/15 6/23/15 4:48 LBD Chlorodibromomethane ND 0.00050 0.000054 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Chloroethane ND 0.0020 0.00016 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD Chloroform 0.0017 0.0020 0.00014 mg/L 1 J SW-8468260B 6/22/15 6/23/15 4:48 LBD Chloromethane ND 0.0020 0.00032 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 2-Chlorotoluene ND 0.0010 0.000070 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 4-Chlorotoluene ND 0.0010 0.000074 mg/L I SW-8468260B 6/22115 6/23/15 4:48 LBD 1,2-Dibromoethane(EDB) ND 0.00050 0.000089 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,2-Dichlorobenzene ND 0.0010 0.000076 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,3-Dichlorobeozene ND 0.0010 0.000079 mg/L 1 SW-8468260B 6/22115 6/23/15 4:48 LBD 1,4-Dichlorobenzene ND 0.0010 0.000046 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD Dichlorodifluoromethane (Freon 12) ND 0.0020 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,1-Dichloroethane ND 0.0010 0.00016 mg/L I SW-8468260B 6/22115 6/23/15 4:48 LBD 1,2-Dichloroethane ND 0.0010 0.00019 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,1-Dichloroethylene ND 0.0010 0.00021 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD cis-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD trans-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,2-Dicbloropropene ND 0.0010 0.00011 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:48 LBD 1,3-Dichloropropene ND 0.00050 0.000099 mg/L I SW-8468260B 6/22115 6/23/15 4:48 LBD 2,2-Dicbloropropane ND 0.0010 0.000072 mg/L I V-05 SW-8468260E 6/22/15 6/23/15 4:48 LBD 1,1-Dichloropropene ND 0.0020 0.00013 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD cis-1,3-Dichloropropene ND 0.00050 0.000062 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD trans-1,3-Dichloropropene ND 0.00050 0.000056 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD Diisopropyl Ether (DIPE) ND 0.00050 0.00018 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD Ethylbenzene ND 0.0010 0.000092 mg/L I SW-846 8260B 6/22115 6/23/15 4:48 LBD 2-Hexanone (MBK) ND 0.010 0.0015 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:48 LBD Isopropylbenzene (Cumene) ND 0.0010 0.00011 mg/L 1 SW-846 8260E 6/22/15 6/23/15 4:48 LBD p-Isopropyltoluene(p-Cymene) ND 0.0010 0.00012 mg/L l SW-8468260B 6/22/15 6/23/15 4:48 LBD Methyl tert-Butyl Ether (MTBE) ND 0.0010 0.000090 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:48 LBD Methylene Chloride ND 0.0050 0.0032 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 4-Methyl-2-pentanone(MIBK) ND 0.010 0.0015 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD Page 14 of 50 n-tot° ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA01028' FAX 413/525-0405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/16/2015 Field Sample #: 8404 Azalea Sampled: 6/15/2015 11:00 Sample 1D: 15F0751-05 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Naphthalene ND 0.0050 0.00012 mg/L 1 SW-8468260B 6/22115 6/23/15 4:48 LBD n-Propylbenzene ND 0.0010 0.000094 mg/L 1 SW-846 8260B 6/22/15 6/23/15 4:48 LBD Styrene ND 0.0010 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,1,2,2-Tetrachloroethane ND 0.00050 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Tetrachloroethylene ND 0.00050 0.000080 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Toluene ND 0.0010 0.000090 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,2,3-Trichlorobenzene ND 0.0050 0.00O14 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,2,4-Trichlorobenzene ND 0.0020 0.00O12 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 1, 1, 1 -Trichloroethane ND 0.0010 0.000094 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,1,2-Trichloroethane ND 0.0010 0.00012 mg/L l SW-8468260B 6/22/15 6/23/15 4:48 LBD Trichloroethylene ND 0.0010 0.000077 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Trichlorofluoromethane(Freon 11) ND 0.0020 0.00O15 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,2,3-Trichloropropane ND 0.0020 0.00O12 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,2,4-Trimethylbenzene ND 0.0010 0.00018 mg/L I SW-8468260B 6/22/15 6/23/15 4:48 LBD 1,3,5-Trimethylbenzene ND 0.0010 0.00010 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Vinyl Acetate ND 0.020 0.0013 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Vinyl Chloride ND 0.0020 0.00013 mg/L 1 SW-846 8260B 6/22115 6/23/15 4:48 LBD m+pXylene ND 0.0020 0.00018 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD o-Xylene ND 0.0010 0.00011 mg/L 1 SW-8468260B 6/22/15 6/23/15 4:48 LBD Surrogates % Recovery Recovery Limits Flag/Qua] 1,2-Dichloroethane-d4 106 70-130 6/23/15 4:48 Toluene-d8 99.8 70-130 6/23/15 4:48 4-Bromofluorobenzene 94.0 70-130 6/23/15 4:48 Page 15 of 50 con-tE t® ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405 .TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/16/2015 Field Sample #: 8405 Azalea Sampled: 6/15/2015 10:50 Sample ID: 15FO751-06 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/rime Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Acetone ND 0.050 0.0047 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Benzene ND 0.0010 0.000079 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Bromobenzene ND 0.0010 0.000044 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD Bromochloromethane ND 0.0010 0.00022 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Bromodichloromethane ND 0.00050 0.000088 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Bromoform ND 0.0010 0.00021 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Bromomethane ND 0.0020 0.00094 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 2-Butanone(MEK) ND 0.020 0.0024 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD n-Butylbenzene ND 0.0010 0.000054 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD sec-Butylbenzene ND 0.0010 0.000084 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD tert-Butylbenzene ND 0.0010 0.000096 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD Carbon Disulfide ND 0.0040 0.0010 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD Carbon Tetrachloride ND 0.0050 0.00010 mg/L I SW-846 8260B 6/22/15 6/23/15 5:20 LBD Chlorobenzene ND 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Chlorodibromomethane ND 0.00050 0.000054 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Chloroethane ND 0.0020 0.00016 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD Chloroform ND 0.0020 0.00014 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Chloromethane ND 0.0020 0.00032 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 2-Chlorotoluene ND 0.0010 0.000070 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD 4-Chlorotoluene ND 0.0010 0.000074 mg/L I SW-846 8260B 6/22/15 6/23/15 5:20 LBD 1,2-Dibromoethane (EDB) ND 0.00050 0.000089 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD 1,2-Dichlorobenzene ND 0.0010 0.000076 mg/L I SW-846 8260B 6/22/15 6/23/15 5:20 LBD 1,3-Dichlorobenzene ND 0.0010 0.000079 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,4-Dichlorobenzene ND 0.0010 0.000046 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Dichlorodifluoromethane (Freon 12) ND 0.0020 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,1-Dichloroethane ND 0.0010 0.00016 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,2-Dichloroethane ND 0.0010 0.00019 mg/L 1 SW-8468260E 6/22/15 6/23/15 5:20 LBD 1,1-Dichloroethylene ND 0.0010 0.00021 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD cis-1,2-Dichloroethylene 0.0020 0.0010 0.00015 mg/L I SW-846 8260B 6/22/15 6123/15 5:20 LBD trans-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD 1,2-Dichloropropane ND 0.0010 0.00011 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,3-Dichloropropane ND 0.00050 0.000099 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 2,2-Dichloropropane ND 0.0010 0.000072 mg/L 1 V-05 SW-846 8260B 6/22115 6/23/15 5:20 LBD 1,1-Dichloropropene ND 0.0020 0.00013 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD cis-1,3-Dichloropropene ND 0.00050 0.000062 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD trans-1,3-Dichloropropene ND 0.00050 0.000056 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Diisopropyl Ether (DIPE) ND 0.00050 0.00018 mg/L 1 SW-8468260E 6/22/15 6/23/15 5:20 LBD Ethylbenzene ND 0.0010 0.000092 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD 2-Hexanone (MBK) ND 0.010 0.0015 mg/L 1 SW-846 8260B 6/22115 6/23/15 5:20 LBD Isopropylbenzene (Cumene) ND 0.0010 d.000I I mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD p-Isopropyltoluene (p-Cymene) ND 0.0010 0.00012 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD Methyl tert-Butyl Ether (MTBE) ND 0.0010 0.000090 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD Methylene Chloride ND 0.0050 0.0032 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD 4-Methyl-2-pentanone(MIBK) ND 0.010 0.0015 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Page 16 of 50 Tahle of C:ontents con -test© ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405 ' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15FO751 Date Received: 6/16/2015 Field Sample #: 8405 Azalea Sampled: 6/15/2015 10:50 Sample ID: 15F0751-06 Sample Matrix: Water Volatile Organic Compounds by GC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qua] Method Prepared Analyzed Analyst Naphthalene ND 0.0050 0.00012 mg/L 1 SW-8468260E 6/22/15 6/23/15 5:20 LBD n-Propylbenzene ND 0.0010 0.000094 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Styrene ND 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,1,2,2-Tetrachloroethane ND 0.00050 0.00012 mg/L 1 SW-8468260B 6/22115 6/23/15 5:20 LBD Tehachloroethylene ND 0.00050 0.000080 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD Toluene ND 0.0010 0.000090 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD 1,2,3-Trichlorobenzene ND 0.0050 0.00014 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,2,4-Trichlorobenzene ND 0.0020 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,1,1-Trichloroethane ND 0.0010 0.000094 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,1,2-Trichloroethane ND 0.0010 0.00012 mg/L I SW-8468260B 6/22/15 6/23/15 5:20 LBD Trichloreethylene 0.00041 0.0010 0.000077 mg/L 1 J SW-8468260B 6/22/15 6/23/15 5:20 LBD Trichlorofluoromethane (Freon 11) ND 0.0020 0.00015 mg/L 1 SW-8468260E 6/22/15 6/23/15 5:20 LBD 1,2,3-Trichloropropane ND 0.0020 0.00012 mg/L 1 SW-8468260E 6/22/15 6/23/15 5:20 LBD 1,2,4-Trimethylbenzene ND 0.0010 0.00018 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD 1,3,5-Trimethylbenzene ND 0.0010 0.00010 mg/L 1 SW-8468260B 6/22115 6/23/15 5:20 LBD Vinyl Acetate ND 0.020 0.0013 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Vinyl Chloride ND 0.0020 0.00013 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD m+p Xylene ND 0.0020 0.00018 mg/L 1 SW-846 8260B 6/22/15 6/23/15 5:20 LBD o-Xylene ND 0.0010 0.00011 mg/L 1 SW-8468260B 6/22/15 6/23/15 5:20 LBD Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 105 70-130 6/23/15 5:20 Toluene-d8 99.7 70-130 6/23/15 5:20 4-Bromofluorobenzene 95.5 70-130 6/23/15 5:20 Page 17 of 50 40 con --testa ANALYTICAL LABORATORY 39 Spruce Street' East Longmeadow, MA 01028' FAX 413/525-6405' TEL. 413/525-2332 Project Location: Pro Cleaners Sample Description: Work Order: 15F0751 Date Received: 6/1612015 Field Sample M MW-24S Sampled: 6/15/2015 14:10 Sample 1D: 15FO751-07 Sample Matrix: Ground Water Volatile Organic Compounds by GC/MS Date Date/Time Analyte Results RL DL Units Dilution Flag/Qual Method Prepared Analyzed Analyst Acetone ND 0.050 0.0047 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Benzene ND 0.0010 0.000079 mg/L I SW-8468260B 6/22/15 6/23/15 6:25 LBD Bromobenzene ND 0.0010 0.000044 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Bromochloromethane ND 0.0010 0.00022 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Bromodichloromethane ND 0.00050 0.000088 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Bromoform ND 0.0010 0.00021 mg/L I SW-8468260B 6/22/15 6/23/15 6:25 LBD Bromomethane ND 0.0020 0.00094 mg/L I SW-8468260E 6/22/15 6/23/I5 6:25 LBD 2-Butanone(MEK) ND 0.020 0.0024 mg/L I SW-8468260B 6/22/15 6/23/15 6:25 LBD n-Butylbenzene ND 0.0010 0.000054 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD sec-Butylbenzene ND 0.0010 0.000084 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD tert-Butylbenzene ND 0.0010 0.000096 mg/L I SW-8468260B 6/22/15 6/23/15 6:25 LBD Carbon Disulfide ND 0.0040 0.0010 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD Carbon Tetrachloride ND 0.0050 0.00010 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Chlorobenzene ND 0.0010 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Chlorodibromomethane ND 0.00050 0.000054 mg/L 1 SW-8468260B 6/22/I5 6/23/15 6:25 LBD Chloroethane ND 0.0020 0.00016 mg/L 1 SW-846 8260B 6/22/I5 6/23/15 6:25 LBD Chloroform 0.00017 0.0020 0.00014 mg/L 1 J SW-846 8260B 6/22/15 6/23/15 6:25 LBD Chloromethane ND 0.0020 0.00032 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD 2-Chlorotoluene ND 0.0010 0.000070 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD 4-Chlorotoluene ND 0.0010 0.000074 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD 1,2-Dibromoethane (EDB) ND 0.00050 0.000089 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD 1,2-Dichlorobenzene NO 0.0010 0.000076 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD 1,3-Dichlorobenzene ND 0.0010 0.000079 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD 1,4-Dichlorobenzene NO 0.0010 0.000046 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Dichlorodifluoromethane (Freon 12) NO 0.0020 0.00012 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD 1,1-Dichloroethane ND 0.0010 0.00016 mg/L I SW-8468260B 6/22/15 6/23/15 6:25 LBD 1,2-Dichloroethane ND 0.0010 0.00019 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD l,l-Dichloroethylene ND 0.0010 0.00021 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD cis-1,2-Dichloroethylene ND 0.0010 0.00015 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD trans-1,2-Dichloroethylene NO 0.0010 0.00015 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD 1,2-Dichloropropane NO 0.0010 0.00011 mg/L I SW-846 8260B 6/22/15 6/23/15 6:25 LBD 1,3-Dichloropropane NO 0.00050 0.000099 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD 2,2-Dichloropropane NO 0.0010 0.000072 mg/L 1 V-05 SW-8468260B 6/22115 6/23/15 6:25 LBD 1,1-Dichlompropene ND 0.0020 0.00013 mg/L I SW-8468260B 6/22/15 6/23/15 6:25 LBD cis-1,3-Dichloropropene NO 0.00050 0.000062 mg/L I SW-8468260B 6/22/15 6/23/15 6:25 LBD trans-1,3-Dichloropropene ND 0.00050 0.000056 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Diisopropyl Ether (RIPE) ND 0.00050 0.00018 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD Ethylbenzene ND 0.0010 0.000092 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD 2-Hexanone(MBK) NO 0.010 0.0015 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD Isopropylbenzene(Cumene) ND 0.0010 0.00011 mg/L 1 SW-8468260B 6/22/15 6/23/15 6:25 LBD p-Isopropyltoluene (p-Cymene) ND 0.0010 0.00012 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD Methyl tert-Butyl Ether (MTBE) ND 0.0010 0.000090 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD Methylene Chloride NO 0.0050 0.0032 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD 4-Methyl-2-pentanone (MIBK) NO 0.010 0.0015 mg/L 1 SW-846 8260B 6/22/15 6/23/15 6:25 LBD Page 18 of 50