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HomeMy WebLinkAboutWI0400033_Underground Injection Summary Report '09 - '13_20130805DUNCKLEE & DUNHAM By email to: Thomas.slusser@ncdenr.gov August 5, 2013 ENVIRONMENTALGEOLOGISTS & ENGINEERS 511 KEISLER DRIVE — SUITE 102 CARY, NORTH CAROLINA 27518 OFFICE: (919) 858-9898 W W W. DUNCKLEEDUNHAM.COM Mr. Thomas Slusser, UIC Program Manager Underground Injection Control Program Division of Water Resources North Carolina Department of Environment and Natural Resources 1617 Mail Service Center Raleigh, North Carolina 27699-1617 Reference: Transmittal Letter Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility k/,DDO�%pp.13 Asheboro, North Carolina Dear Mr. Slusser: On behalf of Kayser -Roth Corporation, Duncklee & Dunham, P.C. submits this Underground Injection Summary Report for 2009 through 2013 for the above -referenced site. This report presents a summary of injection activities from our last summary report in 2009 through the expiration of the permit on March 31, 2013. Please contact Dave Duncklee at dave@dunckleedunham.com or (919) 858-9898 if you have any questions. Sincerely, Duncklee & Dunham, P. C. W' - Richard A. Kolb, L.G. Senior Geologist c: Laval Choiniere, Kayser -Roth Corporation Janet Macdonald, NCDENR IHSB Doris Osborne P:\Kayser-Roth\Asheboro-02600\Complia=\Permits\2010 UIC Permiffransmittal Letter - Mrs. Osborne - 13165.doc MAILING ADDRESS — POST OFFICE BOX 639 — CARY, NORTH CAROLINA 27512 NORTH CAROLINA BOARD OF EXAMINERS FOR ENGINEF,RS AND SURVEYORS LICENSE C-3559 NORTH CAROLINA BOARD FOR LICENSING OF GEOLOGISTS LICENSF C-261 NC DENR REGISTERED F.NVIRONMENTAI, CONSULTANT NUMBER 00061 ENVIRONMENTAL GEOLOGISTS & ENGINEERS DUNCKLEE 511 KEISLER DRIVE — SUrrE 102 �Jt.. D T T� T C RY.OFFICE: NORTH CAROLINA 85 27518 U N �M OFFICE: (919) 858-9898 WWW.D IN KLE .D IN AM.COM July 22, 2013 Mr. Laval Choiniere Kayser -Roth Corporation 102 Corporation Center Blvd. Greensboro, North Carolina 27408 Reference: Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina Incident Number 21340 Dear Mr. Choiniere: Duncklee & Dunham, P.C. submits this Underground Injection Summary Report for 2009 through 2013 for the above -referenced site. This report presents a summary of injection activities from our last summary report in 2009 through the expiration of the permit on March 31, 2013. The potassium permanganate we injected at the site is remediating the source -area plume to the remediation goals specified in the Corrective Action Plan. However, we will need to make adjustments to our remedial approach to enhance delivery of the oxidant throughout the plume. A copy of this report must be sent to the Inactive Hazardous Sites Branch of the North Carolina Department of Environment and Natural Resources. Please contact Dave Duncklee at dave@dunckleedunham.com or (919) 858-9898 if you have any questions. Sincerely, Duncklee & Dunham, P. C. --05,-ram. Richard A. Kolb, L.G. Senior Geologist Senior Peer Review Bryson D. Trexler, Jr., Ph.D., P.G., R.S.M. Senior Hydrogeologist David L. Duncklee, P.G., R.S.M. Senior Hydrogeologist P:\Kayser-Roth\Asheboro-02600\Compliance\Permits\2010 UIC Permit\UIC Summary Repoli-13108.doc MAILING ADDRESS — POST OFFICE BOX 639 — CARY, NORTH CAROLINA 27512 NORTH CAROLINA BOARD OF EXAMINERS FOR ENGINEERS AND SURVEYORS LICENSE C-3559 NORTH CAROLINA BOARD FOR I.ICFNSIN(i OF GEOLOGISTS LICENSE C-261 NC DEN R REGISTERED ENVIRONMENTAL CONSULTANT NUMBER 00061 Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina Incident No. 21340 Site Priority Ranking 60/1) Prepared For: Kayser -Roth Corporation Greensboro, North Carolina Prepared By: Duncklee & Dunham, P.C. Cary, North Carolina July 22, 2013 IDDUNCKLEE & DUNHAM, P.C. Table of Contents 1 Introduction 1 1.1 Site Background 1 1.2 Corrective Action Plan and Injection Permitting 1 2 Injection Activities 1 3 Construction of Additional Monitoring Wells 2 4 Direction of Groundwater Flow 2 5 Laboratory Test Results 2 6 Conclusions and Recommendations 4 6.1 Conclusions 4 6.2 Recommendations 5 7 UIC Documents Produced 6 Figures 1 Site Topographic Map 2 Site Map with Well Locations 3 Site Plan with Locations of Water-Inj ection Points — July 2011 4 Potentiometric Map, Saprolite Aquifer — November 2012 5 Potentiometric Map, Fractured -Rock Aquifer — November 2012 6 PCE Plume in Saprolite Aquifer 7 PCE Plume in Fractured -Rock Aquifer Tables 1 Summary of Field Parameters 2 Summary of Water-Table/Potentiometric Elevations 3 Summary of Laboratory Test Results 4 Summary of Laboratory Test Results, HSL Metals 5 Summary of Laboratory Test Results, Non -Chlorinated VOCs Appendix A Laboratory Test Reports Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina July 22, 2013 Introduction 1.1 Site Background The Asheboro plant of the Kayser -Roth Corporation (Kayser -Roth) is located at 515 West Balfour Avenue in Asheboro, Randolph County, North Carolina (Figure 1). Kayser -Roth manufactures socks at the plant. The subject site is developed with the plant building and several, smaller outbuildings south and southeast of the plant (Figure 2). Assessments in 1999 found several chlorinated volatile organic compounds (VOCs) in groundwater at concentrations that exceeded the North Carolina groundwater quality standards. The primary constituent detected was tetrachloroethene, which is also called perchloroethene or PCE. Duncklee & Dunham injected potassium permanganate at the site as part of our remedial efforts. We prepared an Underground Injection Summary Report dated June 22, 2010 in which we summarized injection activities from 2003 through 2009. This report summarizes injection activities and sampling results since our previous report. L2 Corrective Action Plan and Injection Permitting In 2001; Duncklee & Dunham, P.C. (Duncklee & Dunham) continued the site -assessment activities that Gaia Tech, Inc. had begun in 1999 with a soil and groundwater assessment. Subsequently, we prepared a Corrective Action Plan (CAP) to address groundwater remediation and submitted it to the North Carolina Department of Environment and Natural Resources (NCDENR) in 2002. The CAP outlined a plan to address the dissolved PCE plume through in -situ chemical oxidation (ISCO) by the injection of potassium permanganate. NCDENR issued injection permit W10400033 to Kayser -Roth in early 2003, _and the permit was amended in 2005 and 2007. Duncklee & Dunham conducted four injection events between 2003 and 2009, and prepared an Underground Injection Summary Report for 2003 through 2009, dated June 22, 2010, that summarized the results of those events. Subsequent to our fourth injection event in 2009, Duncklee & Dunham submitted a request to renew the injection permit in 2010 and requested an amendment to allow a second injection of potable water. The purpose of the injection was to improve distribution and contact of residual potassium permanganate with the aquifer by moving the slurry further from the injection zones. NCDENR renewed the permit and approved the amendment on April 15, 2011, and extended the permit to expire on March 31-, 2013. We conducted one injection event during this period and have not renewed the permit. Thus, it expired on March 31, 2013. 2 Injection Activities Geologic Exploration of Statesville, North Carolina (Geologic) advanced probes with a Geoprobe® at seven locations in the source area on July 6-8, 2011. The locations of these seven points — Pt 2, Pt 5, Pt 6, Pt 7, Pt 5-2, Pt 6-2, and Pt 7-2 — are shown on Figure 3. Geologic used a direct -push rig with two-inch rods to advance each,point to a depth of 27 feet below land surface (bls). We injected potable water from the City of Asheboro into the shallow, saprolite portion of the aquifer at depths between 23 and 27 feet DUNCKLEE & DUNHAM, P.C. Underground Injection Summary Report for 2009 through 2013 . Kayser -Roth Facility Asheboro, North Carolina July 22, 2013 Page 2 of 7 bls. Pump pressures ranged from approximately 50 to 170 pounds per. square inch, and the pump rate was six to eight gallons per minute. We injected 5,920 gallons of potable water into the shallow aquifer. Construction of Additional Monitoring Wells Subsequent to the water injection, Duncklee & Dunham oversaw construction of additional monitoring wells by Geologic in our effort to delineate the lateral and vertical extent of the contaminant plume. Geologic constructed well numbers MW-23, DW-6 through -13, and CW-1 and -2 in 2011. Duncklee & Dunham sampled the following wells in 2011: MW-1, -2b, -3, -4, -6b, -7, -8, -1 Ob, -11, -13, -17, -21, -22, -23, and DW-1 through -9. Upon receipt of laboratory test results, Geologic constructed well nos. MW- 26 through -28, DW-14 through -18, and CW-3 through -6 in 2012. Duncklee & Dunham sampled the following wells in 2012: MW-4, -12, -13, -17, and -20 through -28; DW-5 through -18; and CW-1 through -6. During the groundwater -sampling process, we measured geochemical parameters of the groundwater samples in the field. These data are summarized in Table 1. During well construction in 2012, we used the Color-Tec® Method in the field to test groundwater samples for PCE to help determine the depths to set well screens. 4 Direction of Groundwater Flow Prior to sampling the monitoring wells during each event, we measured the depths to the water table in the accessible monitoring wells at the site. Table 2 summarizes the depths to the water table in the wells. We converted the depths measured in November 2012 to elevations and prepared potentiometric maps for the saprolite and fractured -`rock aquifer (Figures 4 and 5, respectively). These maps show groundwater in the shallow surficial aquifer flows to the southeast, and groundwater in the fractured -rock aquifer flows primarily to the southeast and secondarily to the northeast. The flow directions are similar to past events. 5 Laboratory Test Results The laboratory tested the groundwater samples from sampling events in 2010, 2011, and 2012 for several chlorinated VOCs, and tested select samples for total chromium, total manganese, and chloride. Table 3 summarizes the test results from monitoring events since our previous injection . summary report, and includes historical test results prior to these monitoring events. Laboratory test reports are in Appendix A. The laboratory tested the sample collected from MW-3 in September 2011 for the HSL metals, the results of which are shown on Table 4. The sample exhibited manganese and zinc at concentrations that did not exceed the groundwater quality standards. The laboratory tested selected samples collected in 2010, 2011, and 2012 for VOCs, the results of which are shown on Table 5. Three samples exhibited one analyte each at concentrations that did not exceed the respective groundwater quality standards. DUNCKLEE & DUNHANi, P.C. Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina July 22, 2013 Page 3 of 7 PCE remains the primary analyte in groundwater at the site. Figures 6 and 7 show PCE concentrations in the groundwater samples we collected in November 2012 from wells completed in the saprolite and fractured -bedrock aquifers. PCE concentrations decreased in groundwater samples from the two of the three saprolite wells in the injection area — MW-8 and -10b — whereas the PCE concentration increased in the sample from the third saprolite well, MW-6b. PCE concentrations decreased in groundwater samples collected from three nearby saprolite wells -- MW-3, -13, and -17 -- immediately after injection, but the concentrations in samples from two of these wells increased during the following sampling event. Based on the laboratory and field test results, Duncklee & Dunham makes following observations: • The monitoring wells constructed in saprolite (MW-1 through -28) have delineated the lateral extent of PCE at concentrations that exceed the North Carolina groundwater quality standard except to the southeast, where the sample from MW-26 exhibited PCE at a concentration of 4.6 µg/L. We plan to resample that well this summer to confirm the presence of PCE at this location. • The monitoring wells constructed in fractured bedrock (DW-1 through -18) and competent bedrock (CW-1 through -6) have delineated the extent of PCE at concentrations that exceed the groundwater quality standard to the northwest, nearly so to the northeast -and southeast, and nearly so vertically. However, the wells have not delineated the extent to the southwest. Duncklee & Dunham plans to construct additional monitoring wells to the southwest in an attempt to delineate the extent of PCE in that direction. • The laboratory detected PCE in samples from 10 of the saprolite wells, 12 of the fractured -bedrock wells, and one of the competent -bedrock wells. Each of these 23 samples exhibited PCE at a concentration that exceeded the groundwater quality standard. The samples from MW-17 exhibited the highest PCE concentrations. The sample collected in April 2010 exhibited PCE at a concentration of 5,740 µg/L, but the concentrations decreased in each of the successive sampling events to 2,190 µg/L during the event in February 2012. • The laboratory detected trichloroethene (TCE), a degradation product of PCE, in samples from three saprolite wells, 14 fractured -bedrock wells, and four competent -bedrock wells. All but one of these samples exhibited TCE at concentrations that exceeded the groundwater quality standard. The highest concentration was detected in the sample from DW-8, which exhibited TCE at a concentration of 49.6 µg/L. The laboratory detected cis-1,2-dichloroethene, another degradation product of PCE, in the sample from one saprolite well, but the concentration detected did not exceed the groundwater quality standard. • The laboratory detected chloroform in samples from 24 of the monitoring wells. However, the concentrations detected did not exceed the groundwater quality standard. The laboratory also detected acetone in one sample, 2-butanone in one sample, and trichlorofluoromethane in one sample collected in 2012. The laboratory did not detect other chlorinated VOCs at concentrations that exceeded the laboratory detection limits. I' DUNCKLEE & DUNHAIv1, P.C. Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina July 22, 2013 Page 4 of 7 Chloride is used to evaluate PCE degradation, and manganese and chromium are used as tracers to evaluate the distribution and impact of the oxidant to the aquifer. Duncklee & Dunham used the results of the samples collected from the three saprolite wells in the injection area -- MW-6b, -8, and -10b -- to evaluate the effectiveness of the injection of potable water to disperse the oxidant into the aquifer. We expect fractures control the efficiency of this flushing mechanism, whereby the samples that showed the greatest decreases in concentrations may be better connected hydraulically to the injection area. We compared the results from the sampling event in April 2010, before injection in July 17, 2011, with the results from the first sampling event after the event, in September 2011. We make the following observations: • Manganese concentrations in the samples from MW-6b, -8, and -10b remained elevated but decreased, possibly due in part to the flushing of the oxidant further into the aquifer. However, manganese concentrations also decreased in samples from wells near the injection locations -- MW-3, -13, and -17 -- and from MW-21, which is more distant to the injection locations. The decrease in manganese concentrations in the samples from these wells coincides with a decrease in PCE concentrations. • Chromium concentrations decreased in samples from MW-6b and -17 and increased in, samples from MW-8 and -10b. Samples from three of the four wells away from the injection zone -- MW-3, -13, and -21 -- did not exhibit chromium whereas the sample from the fourth, MW-17, exhibited chromium at similar concentrations in the events both before and after injection. , Chloride concentrations decreased in samples from two of the wells in the injection area and increased in the sample from the third well. The samples from wells outside the source area -- MW-3 and -17 -- increased, and continue to be elevated in source -area well MW-8. Field parameters measured during the sampling events in 2010, 2011, and 2012 are shown on Table 1. The ORP readings for samples from only one well in the injection area, MW-6b, showed an increase, whereas the ORP reading decreased in the samples from MW-8 and -10b. This contrasts with the consistent increases in ORP readings after the previous water -injection event. The sample from MW-6b exhibited the highest ORP reading. 6 Conclusions and Recommendations 6.1 Conclusions Based on the 2011 injection event and the groundwater -monitoring results, Duncklee & Dunham concludes the following: • The permanganate solution and slurry have been effective in treating the PCE and TCE, and has reduced a large mass of PCE. • Test results show two degradation compounds, TCE and cis-1,2-dichloroethene, in samples from one saprolite well, and TCE in samples from three other saprolite wells. DUNCKLEE & DUNHAM, P.C. Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina 'July 22, 2013 Page 5 of 7 The sample from MW-17 exhibited the highest PCE concentration in the last sampling event. However, PCE concentrations in the samples from that well have decreased in each of the three events since water injection in July 2011. The injection of water appears to have had the desired effect of flushing the oxidant from the injection area to this well, but additional activation of the permanganate slurry is needed: The PCE concentrations, in the samples from MW-8 have continued to decrease since our sampling event in October 2007. The concentration in September 2011 was less than 46.0 µg/L, which is the lowest since sampling began in 1999. This well is adjacent to and hydraulically downgradient of the slurry -injection and water -injection area. Although we did not sample this well in 2012, the water - injection events appear to have had an impact in this well, but additional data are needed to evaluate the long-term effects. • PCE concentrations in the samples from DW-7, the only fractured -bedrock well in the injection area, have increased slightly since the water injection in July 2011. PCE concentrations in the two of the three nearest fractured -bedrock wells, DW-2 and -6, also increased .slightly after water injection. These increases may be the result of the formation of PCE-concentration gradients in the aquifer that formed by the injection of permanganate. 6.2 Recommendations Based on the 2011 injection event and the groundwater test results, Duncklee & Dunham recommends the following: • Continue to use potassium permanganate as the injectate for the remediation of PCE and TCE in the saprolite and bedrock plumes. • Collect soil samples from the injection area and test the samples to determine if injectate/injection slurry remains in the soil. • Test water samples from select saprolite wells in the water -injection area to ascertain remaining oxidative strength of the permanganate injectate slurry. If sufficient oxidant is available, conduct a pilot test by extracting water from DW-1 and/or -2 and injecting it into on -site saprolite wells where water with permanganate remains and can be used to oxidize the contaminants. If successful, this closed loop process may be used as an ongoing remedial method and expanded to offsite wells. • Conduct a sampling event of all wells to evaluate the effectiveness of remediation since previous sampling events. DUNCKLEE & DUNHAM, P.C. Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina July 22, 2013 Page 6 of 7 7 UIC Documents Produced Duncklee & Dunham has provided the documents inthe following list to the Underground Injection Control Program. We used information in these documents to prepare this report. Duncklee & Dunham, P.C., 2002, Application for Permit to Construct and/or Use a Well(s) for Injection, Class 51 Wells, 515 W. Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 60ID: Prepared for Kayser -Roth Corporation and Submitted to NC Department of Environment and Natural Resources, Division of Water Quality, Underground Injection Control Program, Raleigh, August 26. Duncklee & Dunham, P.C., 2004, Semiannual Ground Water Monitoring Report, Asheboro Sock Facility, 515 W Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 60ID: Prepared for Kayser -Roth Corporation and Submitted to NC Department of Environment and Natural Resources, Division of Water Quality, Groundwater Section, Winston-Salem, March 9. Duncklee & Dunham, P.C., 2004, Injection Pilot Study Status Report and Permit Amendment Request, Asheboro Sock Facility, 515 W. Balfour Avenue, Asheboro, Randolph County, North Carolina: Prepared for Kayser -Roth Corporation and Submitted to Department of Environment and Natural Resources, Division of Water Quality, Aquifer Protection Section, Raleigh, September 27. Duncklee & Dunham, P.C., 2004, Semiannual Ground Water Monitoring Report, Asheboro Sock Facility, 515 W Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 60ID: Prepared for Kayser -Roth ,Corporation and Submitted to NC Department of Environment and Natural Resources, Division of Water Quality, Groundwater Section, Winston-Salem, October 15. Duncklee & Dunham, P.C., 2004, Semiannual Ground Water Monitoring Report, Asheboro Sock Facility, 515 W Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 601D: Prepared for Kayser -Roth Corporation and Submitted to NC Department of Environment and Natural Resources, Division of Water Quality, Groundwater Section, Winston-Salem, November 10. Duncklee & Dunham, P.C., 2006, Semiannual Ground Water Monitoring Report, Asheboro Sock Facility, 515 W Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 601D: Prepared for Kayser -Roth Corporation and Submitted to NC Department of Environment and Natural Resources, Division of Water Quality, Aquifer Protection' Section, Winston-Salem, February 24. Duncklee & Dunham, P.C., 2007, Semiannual Monitoring and Injection Report, Asheboro Sock Facility, 515 W. Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 60ID: Prepared for Kayser -Roth Corporation and Submitted to NC Department of Environment and Natural Resources, Division of Waste Management, Superfund Section, Winston-Salem, May 31. Duncklee & Dunham, P.C., 2007, Application for Permit to Construct and/or Use a Well(s) for Injection, Class 51 Wells, 515 W. Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 60ID: Prepared for Kayser -Roth Corporation and Submitted to NC Department of Environment and Natural Resources, Division of Water Quality, Underground Injection Control Program, Raleigh, February 6. 11 7DUNICKLEE & DLTNHAN1, P.C. .f Underground Injection Summary Report for 2009 through 2013 Kayser -Roth Facility Asheboro, North Carolina July 22, 2013 Page 7 of 7 Duncklee & Dunham, P.C., 2008, October 2007 Semiannual Ground Water Monitoring and Injection Evaluation Report, Asheboro Sock Facility, SI S W. Balfour Avenue, Asheboro, Randolph County, North Carolina, Groundwater Incident Number 21340, Site Priority Ranking 60ID: Prepared for Kayser -Roth Corporation and Submitted to Department of Environment and Natural Resources, Division of Waste Management, Superfund Section, Inactive Hazardous Sites Branch, Winston- Salem, March 14. Duncklee & Dunham, P.C., 2010, Underground Injection Summary Report for 2003 through 2009, Asheboro Sock , Facility, 5I5 W. Balfour Avenue, Asheboro, Randolph County, North Carolina, Ground Water Incident Number 21340, Site Priority Ranking 60ID: Prepared for Kayser -Roth Corporation and Submitted to Department of Environment and Natural Resources, Division of Water Quality, Underground Injection Control Program, Raleigh, June 22. DUNCKLEE & DUNHAM, P.C. Figures \ t i�� -` �,�� i •'•` �,(i ( d. �.t I1 -ids J `� � r ' � ^ti lr a� Bm 68 AP )ij r. ` ti f • or 1!1 ; � i � � "i. .6 � • 1 ( `t i . i! r' i rf � f �,, t - - ; i j Site r w zz f �. • -. \� tr North `• ;... j ��� :: a ')1 � E< %i'Cem � •' ��r� _ = r - B"Vl r _ i, �� �1 Y � �-? 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N s C��rA M W-21 , - •_ d a a DW-10 Mom, V1 s MW-22 '- SSW-26 f U IA Legend �.�e� $ MW-1 Saprolite Monitoring Well DW-I 4 DW-9 Fractured -Rock Monitoring Well *CW-1 Competent -Rock Monitoring Well ^i Boundary of Subject Site A Boundary of Tax Parcel Figure 0 200 400 2 Graphic Scale: 1" = 200' N � I t ul MW-6b MW-11 M W-10c MW-10b Pt 1 TP Pt 8 Pt 10 • • Pt 3 • Pt 9 MW-8 s; ,.'b.,..:. MW-3 Legend Boundary of Subject Site MW-3 Monitoring Well in Saprolite Unit Pt 8 • Water -Injection Point in 2007 M W-13 Ro-� Water -Injection Point in 2011 0 30 60 Site Plan with Locations of Water -Injection Points - July 2011 '17 Kayser -Roth Facility Asheboro,,North Carolina DUNCKLEE & DUNHAM (�) ENvutoNMEN7 u cEOLOGISTs & ENc1NEERs Drawn By: Checked By: Project Number Date: Reference: 511 Keisler Drive Suite 102 (919) 858-9898 Wmf 02600 June2013 Randolph County GIs, Survey Data, Field Notes Cary, North Carolina 27518 www.dunckleedunham.com NC Eng. License No. 63559 NC Geo. License No. C-261 Scale: Size: Layers: Filename: P:\Kayser RothWsheboro - 02600\8 Field and Technical Documentation\8.8 CAD and GIS Maps\8.8.5 I" = 30' 8.5" K 11" 0,1,87 Working Folder\New Site_Map Zlz� � & � # % 7 0 \ & % / \ \ � CD / a CD P0te nbome 9C Map,SapfOhte Aquifer - November2012 Kayser -Roth a�kRkmh£aƒI E> DUNCKL£3 & DUNHAM Asheboro, North Carolina ENVIRONMENTAL GEOLOGISTS&EN o@Rb Dawn By: Checked By: Project Number: Date: References: »m£ 02600 June 2013 Randolph CouRGIS,s # Data 5 11 Keisler DriveSuite 102 @!%s%9aa9 c,A#c ±e 2es _: b6 _ S ge Size: Layers: Filename: w� _eNo. Gal9! 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License No. C-261 a IO lie O MW-27 Legend BMW-1 Saprolite Monitoring Well Boundary of Subject Site Boundary of Tax Parcel PCE Concentration 500-5,000 ppb PCE Concentration 100-500 ppb _w PCE Concentration 10-100 ppb PCE Concentration 0.7-10 ppb PCE Concentration in µg/L (ppb) September 2011 (211) PCE Concentration in µg/L (ppb) February 2012 0 200 400 Graphic Scale: P = 200' rA W G W coi N O\ V 00 � G z 0.0 W. U z W� U� O ..�� ate+ N v .s z W qU d �zW 'U�z A U � U � E t"+ a � 9 Wpyy i'•1 Fil � � O - u' 3 t O �U A w v� oo �z NozN 0*1 r� -U a o x 0 DW-13 � � U � o z -m_ _ a (U �U A w 7 IZI ) rA M Legend y P, a o DW-9 Fractured -Rock Monitoring Well Boundary of Subject Site A Boundary of Tax Parcel -a pq b r, PCE Concentration 500-5,000 ppb U ® PCE Concentration 100-500 ppb Q'+ U N PCE Concentration 10-100 ppb GS f�ell PCE Concentration 0.7-10 ppb o ; �a5 PCE Concentration in µg/L (ppb) pq 4� � (678) September2011 3 �� PCE Concentration in µg/L (ppb) ~ [24.71 February 2012 Q ® PCE Concentration in µg/L (ppb) November 2012 Figure 0 200 400 _ Graphic Scale: P = 200' Table 1 Summary of Field Parameters Kayser -Roth Facility Asheboro, North Carolina NIV1'-I Sample Date Temperature pH Conductivity ORP Dissolved Oxygen (Deg. Celsius) (Standard Units) (PS/CM) (mV) (mg/L) 414'2010 19.29 5.61 857 - Water Injection July 2011 9.15'2011 21.73 4.65 70 47.5 3.06 VItii'-lb Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/CM)(mV) ORP Dissolved Oxygen (mp,It.) 5'10'2010 20 9 S61 857 - 14'ater Injection Jul_v 2011 9;15l2011 21 0 4 58 160 491 5 42 b'IR'-3 Sample Bate Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/cm) ORI, (mV) Dissolved Oxygen (mg/L) 414!2010 17.56 5.72 "; Water Injection Julc 2011 7'131 1_0I 1 19.55 6.17 60 M) 0 '0 9!15i2011 18.86 4.73 160 458 6.49 \1�V-1 Sample Date Temperature (Deg. Celsius) PH Conductivity (Standard Units) I (pSICm) ORP (mV) DissolvedOxygen Water Injection July 2011 9/14/2011 18.86 4.73 01615s 6.49 11282012 19.37 533 4- 274_' 6.14 <I1V-6b Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/CM) ORP (mV) Dissolved Oxygen (-g/L) 4/14/2010 1754 5.84 00 >67 5.01 _Suter Injection July 2011 9/15/2011 19 KB 5.46 20 409 0 82 !1IW'-7 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (pS/cm) . ORP (mV) Dissolved Oxygen (mg/L) 4,'13'-010 20 i4 5 42 793 �37 5 20 Water Injection .1uly 2011 9i30,'2011 NM NM NM NM NM hIW-8 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/ cm) ORP (mV) Dissoh ed Oxygen (mg/L) 4,14/1010 18.12 5 43 I.1 ?0 779 8.56 Water Injection July 2011 9/15/201 1 2 L31 5.59 150 407 2.46 mgL =milligrams per liter S/cm=microseimens per centimeter ORP = Oxidation Reduction Potentud measured in mill —Its \\bmsT"des\Projear\Kayxr-RothWshebom - 0260OW Complia \4.7 Permits (Well and Other)\2010 UIC Permit\UIC Summary Repons\2009-2013 Summary Rcpo&Tables\Table t - Field Parameters.xlsx Table 1 Summary of Field Parameters Kayser -Roth Facility Asheboro, North Carolina NIW-10b Sample Date Temperature (Deg. Celsius) pII (Standard Units) Conductivih (PS/CM) 01 (mV) Dissolved Oxygen 4 14'2010 17.66 5.54 62 000 834 3.09 Water Injection July 2011 9,15,2011 21 7.-, 4.6i 7O 47 5 3.06 NIN'-11 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/CM) ORP (mV) Dissolved Oxygen (mg/L) 414'22010 15 17 6 _1 151' ,'91 5.87 Water Injection July 2011 9;15.'2011 17.IS 5.12 10 478 2.16 NNW-12 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/cm) ORP Qn�) Dissolved Oxygen (mg/►,) I 1 'S 2M 1 1624 5.60 - 211- ` S43 14W-13 Sample Date temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/CM) ORP (mV) Dissolved Oxygen (mg/L) 4'1 , Ni l0 I S 56 5.15 'S' 331 0.00 Water Injection July 2011 9'1S'ol1 17.IS 5.12 10 478 2.16 1 l-_ 010 1 2 16.44 5.70 54 169.8 8.43 NIW-17 Sample Date Temperature (Deg. Celsius) PH (Standard Units) Conductivity (PS/cm) ORP (mV) Dissolved Oxygen (mg/L) 4:14'2010 16.77 5.87 20,000 684 4 89 Water Injection July 2011 7/13/201 1 18 64 6.01 60 452 0.58 9/16/2011 1634 4.93 50 536 19.99 2/28/2012 NM NM NM NM NM MAV-20 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/CM) ORP Dssolved Oxygen (mg/L) 4i13n010 1940 5.15 81 400 Water Injection July 2011 9/16/2011 1 16S9 5.14 0 470 2.8 11/27 2012 16.83 it 281.9 6.18 11N'-21 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/CM) ORP (mV) Dissolved Oxygen (mg/L) 4/13/2010 20.33 5.82 830 304 2.30 Water Injection July 2011 9/16/2011 16.59 1 10 470 2.84 71/30/2012 1795 3 93 97.2 i.03 MW-22 Sample Date Temperature (lleg. Celsius) pH (Standard Units) Conductivity (PS/cm) ORP (mV) Dissolved Oxygen (tng(1.) 4/13'2010 pi 7 5 22 393 311 5.12 Water InIce on 2011 9/16/2011 19.56 4.52 20 516 6.66 11/272012 16.80 5.17 1(i 2443 5.69 mg - milligrams per liter uS/cm=microseimens per centimeter ORP = Oxidation Reduction Potennol measured in millivolts \\boss\files\Projects\Kayser-Roth\Asheboro - 02600A Comphance\4.7 Permits (Well and Other)\2010 UIC PetmR\UIC Summary Repons\2009-2013 Summary Report\Tables\Table I -Field Parametem.xlsx Table 1 Summary of Field Parameters Kayser -Roth Facility Asheboro, North Carolina N"V-23 Sample Date Temperature (DegXelsius) pH (Standard Units) Conductivity (PS/CM) ORP (m�� Dissolved Oxygen (mtiUi Water Injection .luh 2011 9/14/2011 18.19 5.08 80 468 4.50 9/302011 17.70 6.54 90 _34 5.1 11/302012 16.13 6-12 70 164.6 4.81 mW-24 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/CM) ORP (MV) Dissolved Oxygen (mg.I ) Water Injection July 2011 1129,2012 16 o0 (o l 59 05 1 5.41 NIAV-25 Sample Date remperature (Deg. Celsius) pH (Standard Units} Conductivity (pS/cm) ORP (m�') Dissolved Oxygen (�/L) Water Injection July 2011 I 1 -18 'O13 14.72 6.24 487 241 1 26 AI«'-26 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (pS/cm) ORP (mb') Dissohed Oxygen (mg/U) Water Injection July 2011 1 1/27/2012 18.71 5 6, ill NI«'-27 Sample Date Temperature (Deg. Celsius) plI (Standard l'mts) Conductivity (PS/cm) ORP (m�`) Dissolved Oxygen (mg/L) Water Injection .July 2011 11/29/2012 17.33 6.28 565 99.5 5 NIW-28 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivit}' (pS/cm) ORP (m�') Dissolved Oxygen (mg/U) Water Injection July 2011 11'17''OP 1631 614 231 301.9 _ 31 DV1'-1 Sample Date Temperature (Deg. Celsius) PH (Standard Units) Conductivity (PS/CM) ORP (MY) Dissolved Oxygen (mg/I,) 411,2010 87 66" h33 IIS 4.02 Water Injection July 2011 7:13/2011 18 77 6 8'J 130 384 034 9/15/2011 17 79 5 il5 270 399 0 77 Doi`-2 Sample Date remperature (Deg. Celsius) p1l (Standard Units) Conductivity (PS/CM) ORP (MY) Dissolved Oxygen (mglU) 1'14/2010 1959 645 999 340 1-1 Water Injection July 2011 7/132011 18.45 G.39 150 416 0.10 9/15/2011 18.59 5.82 430 418 5.00 mg L - milligrams per liter Scm-microseimem per centimeter ORP - Oxidation Reduction Potential mea>vred in milli olts \\boss\files\Projects\Kayser-Roth\Asheboro - 0260M Comphance\4.7 Permits (Well and Orher)\2010 UIC Permil\UIC Summary R.cports\2009-2013 Summary Report\Tables\Table 1 - Field Pammeters.xlsx Table 1 Summary of Field Parameters Kayser -Roth Facility Asheboro, North Carolina DW-3 Sample Date Temperature (Deg. Celsius) PH (Standard Units) Conductivity (Ns/cm) ORP (mV) Dissolved Oxygen 4%1 , 2010 21 00 6.1 ; 999 150 �2 Water Injection July 2011 9%15 2011 20 80 5 92 400 376 3 41 DNN'-4 Sambre Date Temperature (Deg. Celsius) pH (Standard (nits) Conductivity (pS/cm) ORP (mV) Dissohed Oxygen {mg L) 414 "2010 M04 648 565 2'0 9 21 Water Injection July 2011 9i14?011 1968 556 210 410 2.11 DNV- S Sample Date Temperature (Deg. Celsius) pH (Standard Unite) Conductivity (PS/cm) ORP (mV) Dissohed Oxygen (mg/1.) 4,13i2010 1964. 5.93 900 201 0.89 Water ln'ection July 2011 9/14/2011 17.28 5.39 240 295 0.43 1127/2012 16.67 5.85 183 297.2 3.41 D�1"-G Sample Date Temperature (Deg. Celsius) I (Standard Units) Conductivity (NS/cm) ORP (mV) Dissolved Oxy Oxygen g Water Injection Jul), 2011 9/16/2011 NM 5.39 240 2282012 NNI NM NM NM N.M DW-7 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (NS/cm) ORP (mV) Dissolved Oxygen {mg [ ) Water Injection July 2011 9/15/2011 17.94 9.28 Ali -17.2 M8 9/302011 18.00 9.43 0 172 1.5 2292012 NM NM NM NM NM DW-8 Sample Date Temperature (Deg. Celsius) pIl (Standard Units) Conductivity (NS/cm) ORP (mV) Dissolved Oxygen (mg/L) Water Injection July 2011 9%15201 1 21 31 5 58 150 40? 2.46 2-282012 NM NM NM NNI NM DW--9 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (NS)cm) ORI, (mV) Dissohed Oxygen (mg/L) Water Injection July 2011 9/15/2011 22.16 5.19 290 319 0 9S 9/302011 20.30 6S5 277 2N8 19 2/292012 NM NM NM NM NM mg L = milligrams per liter S/em=mieroseimens per mntimeter ORP = Oxidation Reduction Potential measured in mill —Its \\boss\tiles\Projects\Ka\we Roth\Ashebom - 02600\4 Complimw\4.7 Permits (Well and Odrer)\2010 UIC Permit\UIC Summary Reports\2009-2013 Summary Report\TablesUable 1 -Field Parametem.xlsx 7"able 1 Summary of Field Parameters Kayser -Roth Facility Asheboro, North Carolina DNV-10 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conducthity I (PS/cm) ORP Dissolved Oxygen (mg/L) Rater Injection July 2011 2/29/2012 NM NM NM NM NM 11/27/2012 1(1 6- 183 297.2 3.41 DV-11 Sample Date Temperature (Deg. Celsius} pi (Standard Units) Conductiv itp OIZP (NS/cm) (mV) UissolvivJ Oxygen (mg/L) Water Injection July 2011 2/29/2012 NM NM NM NM N%I 11/28/2012 654 6.54 157 96 3 4 1 3 DNV-12 Sample Date Temperature (Deg. Celsius) pit (Standard Units) Conductivity (pS1em) ORP Dissolved Oxygen Water Injection July 2011 2/28/2012 NM NM NM NM NM 1129/2012 1654 8,11 167 17.0 5 DW-13 Sample Date Temperature (Deg. Celsius) pll - (Standard Units) Conductivity (PS/cm) ORP (mV) Dissohed Oxygen (mg/L) Water Injection July 2011 2i28�201' NM NM NM NM NM 11/2812012 1651 698 107 2003 �_6I DW-14 Sample Date Temperature pH Conductivity ORP Dissolved Oxygen (Deg. Celsius) (Standard Units) (PS/cm) (mV) (mg/I,) Water Injection July 2011 -s 9/1421011 1968. 5.56 230 4I0 2.11 11/28/2012 15,91 7,01 487 249 6 1 71 D�1'-1$ Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/cm) ORP (mV) Dissolved Oxygen (mg/L) Water Injection July 2011 11')'oi �_,� 1702 1475 306 DW-16 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (NS/cm) ORP Dissolved Oxygen (mg/L) Water Injection July 2011 11/30/2012 18,73 6 (IS 103, 193? D�1'-17 Sample Date Temperature (Deg. Celsius) pH Conductivity (Standard Units) (VS/cm) ORP Dissolved Oxygen Water Injection July 2011 11 27r N , 15,51 6 21 70 290.1 2.33 DW-18 Sample Date Temperature (Deg- Celsius) pH (Standard Units) Conductivity (NSJan) ORP (mti') Dissolved Oxygen (mg/1,) Water Injection July 2011 11/29/2012 17 87 7.91 367 2, 4 144 mg L = milligrams per firer S"cm=microseimens per centimeter ORP = Oxidation Reduction potential measured in mill -Its \\bossTiiles\Projects\Kayser-Roth\Asheboro - 02600\4 Complianee\4.7 Permits (Well and Odwr)\2010 UIC PermMUIC Summary Reports\2009-2013 Summary Report\Tables\Table 1 - Field Paameters.xlsx Table 1 SummaryotField Parameters Kayser -Roth Facility Asheboro, North Carolina Cw_1 Sample Date Temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/cm) ORP (mV) Dissolved Oxygen Water In'ectiou July 201 I 2/28/2012 NM NM NM NM NM 11/282012 16.25 11.98 1,077 -1.8 0.51 12/32012 21.82 11.91 1289 104.1 0.01 CNN -2 Sample Date temperamre (Deg. Celsius) pH (Standard Units) Conductivity (NS/cm) ORP (m%) Dissolved Oxygen (medL) Water Injection July 2011 2/28/2012 NM NM NM NM NM 11292012 16.18 6.96 221 -154.9 0.35 CN -3 Sample llate Temperature (Deg. Cetvus) pH (Standard Units) Conductivity (NS/cm) ORP (mV) Dissolved Oxygen (mg/L) Water Injection July 2011 11/30/2012 19'_7 ? 89 246 107.0 0.32 C11'-4 Sample Date Temtreratnre (Deg. Celsias} p1I (Standard Units) Conductivity (NS/cm) ORP Dissoh ed Oxygen Water Injection July 2011 l_0�01' 5i8._4 165 442 036 (AV-5 Sample Date Temperature (Deg. Celsius) pit (Standard Units) Conductivity (PS/cm ) ORP (MV) Dissolved Oxygen Water Injection July 2011 I -'o '01 19ol 858 101 1-1-6 0.18 C1V-6 Sample Date temperature (Deg. Celsius) pH (Standard Units) Conductivity (PS/cm) ORP (mV) Dissolved Oxygen (mgiL) Water Injection July 2011 17.73 7.92 195 158.7 0.15 g/L = milligrams per liter Sicm=mieroseimens per centimeter RP = Oxidation Reduction Potential measured in millivolts \\bmsTdes\Projects\Kayser-Rah\Ashebom - 02600\4 Comphwce\4.7 Permits (Well and 01ber)\2010 UIC Permit\UIC Summary Repons\2009-2013 Summary Report\Tables\Table 1 - Field P—iieters.xls< \\boss\filcs\Pmjmtsways RothWshebmo-02600\4 Compliance\4.7 Permits(Well and Other)\2010 UIC PertnitlUIC Summary ReportsU009-2013 Summary Report\Table\Table 2- Water Table Elevations-2011-2012 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-1* Sample Date PCG in µg/L TCE in µg/L Chloroform in , L cis-1,2-DCE in /L trans-1,2-DCE in /L Manganese in m 1, Chromium in m /l: Chloride in In/l. April 9, 1999 <5 <5 5 <5 <5 NA NA NA July 9, 1999 <5 <5 <5 <5 <5 NA NA NA September 2, 1999 <5 <5 <5 <5 <5 NA NA NA September 14, 2000 <1 <1 2.7 <1 <1 NA NA NA February 15, 2001 <0.5 <0.5 2.4 <0.5 <0.5 NA NA NA May 8, 2001 <1 <1 2.1 <0.5 <0.5 NA NA NA November 27, 2001 <1 <1 3.3 <1 <1 0.12 NA 9.7 July 9, 2003 <1 <1 <1 <1 <1 0.14 <0.002 96 Phase I Pilot Test July 30, 2003 <I -1 I <1 <I 0.14 0.0042 94 August 13, 2003 I <-1 <I <I <1 0.13 <0.002 110 Phase 11 Pilot Test September 29,2003 <1 <1 <1 <1 <1 0.13 <0.002 90 October 27, 2003 <1 <1 1.2 <1 <1 0.13 <0.002 100 November 24, 2003 <1 <1 <1 <1 <1 0.14 <0.002 120 February 16, 2004 <l <1 <1 <1 <1 0.15 <0.002 69 May 27, 2004 <1 <1 <1 <1 <1 0.14 <0.002 130 March 3, 2005 <1 I <1 1 <5 1 <l <1 0.12 <0.002 59 Slurry Injection May 23, 2005 <1 <1 <5 <1 <1 NA NA NA August 9, 2005 <1 <1 <5 <1 <1 0,084 <0.010 35 December 5, 2005 <1 <l <5 <1 <1 NA NA NA April 10, 2006 <1 <1 <1 <1 <1 NA NA NA October 11. 2006 <1 <1 <1 <1 <1 NA NA NA April 1712007 NA NA Water Injection October 23, 200- l S1 - I I I N,A N-1 A A1,111 1-1_ 01O -0 6 <0,47 \A I - o 19 - 0.41) 1 N:A \A Water Injection July 2011 September 15, 2011 21.2 0,47 1.1 <0.19 <0,49 0.20 <o.0004 16.3 L_I2L Standard 0.7 3 70 70 100 0.050 0.010 250 pgT = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. 'Samples Collected through 2007 in passive Diffusion Bag Samplers NA = Not analyzed J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BDL = Below detection limit (laboratory reporting limit unknown) mgT = milligrams per liter \\boss\51es\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Penmts (Well and Other)\2010 UIC Pennit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx I of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-2b Sample Date PCE in µg/L TCE in µg/L Chloroform in �tg/L cis-1,2-DCE in L trans-1,2-DCE in IL Manganese in m /L Chromium in m /l, Chloride in m =/l, September 8, 1999 3 <1 41 <1 <1 NA NA NA September 15, 2000 9.1 <1 24 <1 <1 NA NA NA November 6, 2000 6 <1 24 <1 <1 NA NA NA February 15, 2001 T8 1 75 1 23 1 <0.5 1 <0.5 NA NA NA Well Not Accessible After February 2001 May 20, 2010 14 <1 <5 <1 <1 0.17 <0.01 40 Water Injection July 2011 September 15, 2011 11.1 <0.47 4.4 <0.19 <0.49 0.02 0.00056 J 32.1 2L Standard 0.7 3 70 70 100 0.050 0.010 250 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. *Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BW — Be/ow detection limit (laboratory reporting limit unknown) mg L milligrams per liter \\boss\files\Projects\Kayser-RotMAsheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Pemrit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 2 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-3 Sample Date PCE in µg/L TCE in µg/L Chloroform in WI/L cis-1,2-DCE in /L trans-1,2-DCE in µg/I, Manganese in mg/L Chromium in mg/L Chloride in mg/L April 91999 180 5 5 <5 <� NA N;\ NA July 9, 1999 250 6 <5 <5 <5 NA NA NA September 2, 1999 160 10 10 <10 <10 NA NA NA September 15, 2000 440 6.3 4.6 <1 <1 NA NA NA November 8, 2000 270 5.4 3.9 <I <1 NA NA NA February 15, 2001 1,100 <5 11 <5 <5 NA NA NA May 8 2001 800 <10 <10 <10 <10 NA NA NA November 28, 2001 160 72 4.3 <1 <1 NA NA NA Phase I Pilot Test Phase ❑ Pilot Test August 13, 2003 600 <1 <1 <1 <1 0.022 <0.002 7.1 Sem tember 29, 2003 420 <1 <1 <1 <1 0.035 <0.002 8.4 October 27, 2003 670 <1 <1 <1 <1 0.043 <0.002 11 November 24, 2003 540 <I <1 <1 <I 0.028 <0.002 19 February 16, 2004 1100 <10 <10 <10 <10 0.034 <0.002 14 May 28, 2004 460 <5 <5 <5 1 <5 1 0.021 <0.002 29 March 3, 2005 760 1.8 <5 1 <1 <1 0.053 <0.002 12 Slurry Injection May 23, 2005 690 4.1 <5 <1 -� l o o47 <0 010 13 August 9, 2005 410 6.4 <5 <I <1 0.019 <0.010 13 December 5, 2005 320 7.1 <5 <1 <l NA <0.010 14 April 11.2006 660 5.2 2 <1 <1 0.0086 <0.002 14 October 11 ,2006 230 6.9 2.6 <I <1 0.0088 0.011 19.9 April 17, 2007 390 <2 <2 <2 <2 0.078 <0.005 1 13.8 Water Injection October 10, 2007 456 9.0 S I <� 5 <0.005 <0.005 2 1) April 14, 2010 637 <0.47 NA <o. I ) <0.49 0.199 0.0013 J 17 Water Injection July 2011 July 13, 2011 260 4. 1 NA <5.0 <5.0 0.0765 <0.005 2-10 September 14, 2011 331 4,5 74 <0.38 <0.98 0.0095 0.0012 J s0 I 2I, Standard 0.7 3 70 170 100 0.050 1 0.010 1 µg/L = Micrograms per hicr All samples through May 2001 collected by Gala Tech, Inc. ".Samples Collected through 2007 in Passive Dion Bag Samplers NA = Not analyzed J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BDL = Below detection limit (laboratory reporting limit unknown) mg1L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 3 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina pg/L = Micrograms per liter All samples through May 2001 collected by Gana Tech, Inc. BDL = Below detection limit (laboratory reporting limit unknown) *Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed mg/L = milligrams per liter I - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Stunmary Report\Tables\Tables 3-5 - Summaryof Laboratory Test Results.xlsx 4 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-6b Sample Date PCE in µg/L TCE in µg/L Chloroform in L. cis-1,2-DCE in µg/1, trans-1,2-DCE in µg/l., Manganese in nig/L Chromium in m /L Chloride in m /l, September 8, 1999 <1 <1 <1 <1 <1 NA NA NA September 15, 2000 <1 <1 <1 <1 <1 NA NA NA February 13, 2001 <0.5 <0.5 <0.5 <0.5 <0.5 NA NA NA May 8, 2001 <0.5 <0.5 <0.5 <0.5 <0.5 NA NA NA November 27, 2001 <1 <1 <1 <1 <1 0.98 <0.002 48 July 9, 2003 1.2 <1 <1 <i <I 0.52 <0.002 220 ]phase I Pilot Test July 30, 2003 1.3 <1 <1 <1 <I 0.45 <0.002 200 Au gust 13. 2003 <1 <I <1 <1 <1 0.44 <0.002 210 A . Phase 11Piltti <1 <1 <1 0.41 <0.002 180 September 12, 2003 2 <1 October 27, 2003 <1 <1 <1 <1 - 1 0.51 <0.002 220 November 24, 2003 2.8 <1 <1 <1 <1 0.48 <0.002 220 February 16, 2004 2.2 <1 <1 <1 <1 0.58 <0.002 220 May 27, 2004 2 9 <1 <1 <1 <1 0.47 <0.002 390 .Sin ry Injection May 23,2005 14 <1 <I <1 <1 0.370 <0.010 170 December 5, 2005 3.8 <1 <1 <1 <1 NA <0.010 82 April 11, 2006 10 <1 <1 <1 <1 0.130 <0.002 121 October 11, 2006 5A <1 <1 <1 <1 0.210 0.0061 138 April 17, 2007 2.3 <1 <1 <1 <1 0.170 <0.005 128 U'ater Injection As October 10. 2007 <1 <1 <I <1 <1 0.173 <0.005 92.6 April 14, 2010 4.3 <1 NA <1 <1 033,0 0.0064 152.0 y, Water Injection Juiv 2011 Se tember 15, 2011 13.5 <0.47 <0.14 <0.19 <0.49 0.194 0.0014 J 110.0 tan ar 70 /0 100 U.())U µg/L = Micrograms per liter All samples through May 200! collected by Gaia Tech, Inc. '.Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed J- Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BDL = Below detection limit (laboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results,xlsx 5 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina *Samples Collected through 1007 in Passive Diffusion Bag Samplers NA = Not analyzed mg1L = milligrams per liter J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Pemrits (Well and Other)\2010 UIC Permit\2009-2013 Summaty Report\Tables\Tables 3-5 - Summary of Laboratoty Test Results.xlsx 6 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina September 15, 1999 650 <1 <1 <1 <1 NA NA NA September 15, 2000 510 <1 <1 <1 <1 NA NA NA November 8, 2000 390 <10 <10 <10 <10 NA NA NA February 12, 2001 270 <1 <1 <1 <1 NA NA NA May 8, 2001 310 <10 <10 <10 <10 NA NA NA November 28, 2001 650 <I <1 <1 <1 0.35 NA 240 July 9, 2003 410 <1 <1 <1 <1 0.9 <0.002 620 1�fiase I �ii�t Tee . July 30, 2003 8.6 <1 <1 <1 <1 0.56 0.002 660 August 13, 2003 210 <1 <1 <1 <1 0.61 <0.002 710 September 29, 2003 170 <1 <1 <1 <1 0.53 <0.002 660 October 27, 2003 190 <1 <1 <1 <1 1 <0.002 680 November 25, 2003 200 <1 <1 <1 <1 0.91 <0.002 850 Febmary 16, 2004 280 <5 <5 <5 <5 1.3 <0.002 660 May 28, 2004 170 <1 <1 <1 <1 1.3 <0.002 1,300 March 3, 2005 200 <1 <5 <1 <1 1.4 1 <0.002 1 560 Slur .i eetiva May 23, 2005 120 <1 <5 <1 <1 1.4 <0.010 580 Au ust 9,2005 190 <1 <5 <1 <1 1.4 <0.010 480 December 5, 2005 180 <1 <5 <1 <1 NA <0.010 530 April 11, 2006 160 <1 <1 <1 <1 1.5 <0.002 548 October 11, 2006 260 6.4 2.9 <2 <2 0.16 <0.005 18.2 April 17, 2007 240 <2 <2 <2 1 <2 1 0.98 <0.005 20,100 Water In ection " October 10, 2007 128.0 <1 <1 <1 <1 0.905 0.0073 465 April 14, 2010 <230 <235 NA <95.0 <245 124 <4.0 NA Water ''In edl w July,'• O t !September 16, 2011 <46.6 47.0 <14.0 <19.0 <49.0 42.5 0.0058 235 2L Standard 0.7 3 70 70 100 0.050 0.010 250 pg,'L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. BDL = Below detection limit (lahoratory reporting limit unknown) "Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed mg/L = milligrams per liter J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. \\boss\fifes\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Perm is (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 7 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-10b Sample Date PCE in µg/L TCE in µg/L Chloroform in ILg/l, cis-1,2-D(, E in /L trans-1,2-DCE in /l, Manganese in nt L Chromium in m /l, Chloride In m /L September 28, 1999 4,300 <50 <50 <50 <50 NA NA NA October 6, 1999 4,000 1 <1 <1 <1 NA NA NA September 15, 2000 8,900 25 <1 <1 <1 NA NA NA November 8, 2000 6,300 <100 <100 <100 <100 NA NA NA February 12 2001 9,000 14 <1 <1 <1 NA NA NA May 8, 2001 7,000 <10 <10 <10 <10 NA NA NA July 9, 2003 9.700 1.2 <l <1 <1 0.084 0.0059 3 Pltasa lot Test Jul y 30, 2003 6900 <I 1 <1 <1 0.053 0.0043 2.4 August 13, 2003 9,300 <1 <I <l <1 0.046 0.0028 1 2.9 Phase 11 Pilot Test September 29, 2003 5,800 <I <I <1 <1 1.1 0.01 7.2 October 27, 2003 4,400 <I <1 <1 <1 0.24 0.0042 4.9 November 26, 2003 6,400 <I <1 <1 <1 0.22 0.0054 4.6 February 16, 2004 8,200 <200 <200 <200 <200 0.41 0.0043 3.8 May 28, 2004 10,000 <100 <100 <100 <100 0.26 0.0033 0 March 3, 2005 6,100 IA <5 <I <1 0.33 <0.010 1.5 Slu ry Injection May 23,2005 <100 <100 <500 <100 <100 730 <0.010 <50 August 9, 2005 <1 <1 <5 <1 <1 23 0.012 <10 December 5, 2005 2.6 <1 <5 <1 <1 NA <0.010 <10 April 12, 2006 <1 <1 <1 <1 <1 12 0.045 7.78 October 12, 2006 <1 <1 <1 <1 <1 NS NS 12.9 April 17, 2007 <1 <1 <1 <1 <I 270 0.011 42,900 Water Injection. October 10, 2007 DrN' Dry Dr) Dry WN Dry Dr Dry April 14, 2010 <920 <940 NA <380 <980 339 <4.0 NA Water Injection .lulu 2011 September 16, 2011 463 <2.4 6.5 1 70.95 <2.4 11.6 6.685 14.2 2L Standard 0.7 3 70 1 70 100 0.050 1 0.010 250 µg L Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. 'Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BDL = Below detection limit (laboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.Asx 8 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina N1W-11 Sample Date I C"E in µg/L LCE in µg/L Chloroform in µg/L cis-1,2-DCE in µg/L, trans-1,2-DCE in g/l,. Manganese in mg/L Chromium in mg/I.. Chloride in ing/I, October 5, 1999 NSA NA N:1 September 14, 2000 -1 I l <I I NA NA N A February 13. 2001 u 5 <0 5 ..0 <0 NA XA \;A Mxv `3 2001 0 62 <0 5 - O 5 ..OS U5 NA N,A \A Phase I Pilot Test Phase 11 Pilot Test November 21, 2003 <1 <1 I <I I NA NSA NA May 26, 2004 <1 <1I=1 - I NA NA NA March 3, 2005 <1 <1 5 <l < I 0,02 0_0l0 � 6 Slurry Injection May 23, 2005 <1 <1 <5 <1 <1 0.019 <0.010 2.8 August 9, 2005 <1 <1 <5 <1 <1 0.022 <0.010 2.7 December 5, 2005 <1 <1 <5 <1 <1 NA <0.010 2.5 April 12, 2006 NS NS NS NS NS NS NS NS October 12, 2006 <1 <1 <1 <1 <1 0.046 <0.005 4.15 April 17, 2007 NS NS NS NS NS NS NS NS Water Injection Octobcr 23, 2007 <I <I <1 <1 <].. NSA NA NA April 14, 2010 0.89.1 <0 47 NA <0.19 <0.49 N:A NA NA Water Injection July 2011 September 15, 2011 746 <0.47 <0.14 <0.19 <0.49 0 0572 0.0029 J 6 1 2L Standard 0.7 3 70 70 100 0.050 0.010 250 pg'1, - Micrograms per liter All samples through May 2001 collected b,v Gaia Tech, Inc. *Samples Collected through 1007 in Passive Dr(fusion Bag Samplers NA = Not analyzed I - Estimated concentration above the adjusted method detection limit and Belo" the adjusted reporting limit. BUL == Below detection limit (laboratory reporting limit unknown) mg1L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 9 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-12 Sample Date PCEin µg/I TCE in µg/L' Chloroform iu cis-1,2-DCE in. tram-1,2-1) M hganese in Chromium,in . Chloride in 114,11A'id Ciit m /t ttt October 6, 1999 1 <1 <1 <1 <1 September 14, 2000 <1 <1 <1 <1 <1 February 13, 2001 <0.5 <0.5 <0.5 <0.5 <0.5 May 8, 2001 <0.5 <0.5 <0.5 <0.5 <0.5 NA NA NA JLIIY 9, 2003 <1 <1 <1 <1 <1 0.066 0.0048 3.7 Phase I Pilot Test JUly 30, 2003 <1 <1 <1 <1 <1 0.02 0.0027 2.9 August 13,2003 <1 <1 <1 <1 <1 0.01 0.0021 3.1 Pase.Iiltit Test'; September 29, 2003 <1 <1 <1 <1 <1 0.012 <0.002 15 October 27, 2003 <1 <1 <1 <1 <1 0.0054 <0.002 2.5 November 21, 2003 <1 <1 <1 <1 <1 0.012 0.0026 2.9 February 16, 2004 <1 <1 <1 <1 <1 0.016 0.0021 2.6 May 26, 2004 <1 <1 <1 <1 <1 0.03 0.03 0 November 28, 2012 <1.0 <1.0 <1.0 <1.0 I <1.0 NA NA 2.0 2L Standard 1 0.7 3 70 70 1 100 0.050 0.010 250 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. BDL = Below detection limit (laboratory reporting limit unknown) *Samples Collected through 2007 in passive Diffusion Bag Samplers NA = Not analyzed mg/L = milligrams per liter J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Pennits (Well and Other)\2010 UIC Pemv62009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 10 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-13 Sample Date PCE in µg/L WE in µg/l, Chloroform in L cis-1 2-DCE in g/I, trans-1,2-DCE in g/I, Manganese in nt L Chromium in mg/L Chloride in mg/l, February 15, 2001 24 <0.5 <0.5 <0 ; <0.5 NA NA A March 1, 2001 17 <0.5 <0.5 <0.5 - 0_5 NA NA N 1 May 9, 2001 1 8 <0.5 <0.5 <0.5 NA \A y A NoN ember 28, 2001 9.2 <I <I <I -1 I NA NA N-1 Phase I Pilot Pest Phase 11 Pilot Test November 25 2003 3.8 <- I 11 < I 1 I NA N A NA May 28, 2004 1.3 <I <II <I <1 NA NA NA Slu ry Injection May 23, 2005 <1 <1 <5 <1 < I 0 > 7 - 0 010 2 7 December 5 2005 14 <1 <5 <1 <1 NA 0.011 2.4 April 10, 2006 4 <I 4.1 <1 <1 0.15 0.0026 3.56 October 12, 2006 �.2 <1 5.4 <1 <1 1.2 0.026 4.69 April 13, 2007 62 <1 6.4 <1 <1 0.19 <0.005 3.49 Water Injection October 10, 2007 14.7 <I <I1 <I <I 0_ I61 --woos 0 April 13, 2010 7 --OA7 NA I 41.19 =0.49 0.160 0.0022 1 4.0 Water Injection Julv 2011 September 16, 2011 0.99 J <0.47 13.0 <0.19 -0.49 0268 0.00.11 1 � 0 November 30, 2012 78.8 <1.0 9.6 <1.0 <1.0 NA NA i I 2L Standard 0.7 3 70 70 100 0.050 0.010 250 µg/L = Micrograms per liter All samples through May 2001 collected by Gata Tech, Inc. 'Samples Collected through 1007 in Passive Diffusion Bag Samplers NA = Not analyzed J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. HDL = Below detection limit (laboratory reporting limit unknown) mg1L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Pemvt\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx l l of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-17 Sample Date PIwE in µg/L TCE in µIL', Chloroform in cis-1»1C%✓„itl.: tram»1,2»)D) Manganese in,lrnrnium;in , + hlorid+e in L jWL An WL m lip February 15, 2001 2,500 4.6 1.2 <0.5 <0.5 NA NA NA March 1, 2001 2,200 6.2 1.4 <0.5 <0.5 NA NA NA May 9, 2001 9,600 <100 <100 <1,000 <1,000 NA NA NA November 28, 2001 1,200 6.9 1.9 <1 1.5 NA NA NA Phaw, I Pilot Test August 13, 2003 13,000 <1 <1 <1 <1 0.026 <0.002 10 Phasel Pilot Test°` :• :: N September 29, 2003 <I <1 <1 <1 <1 12 0.020 14 October 27, 2003 900 <1 2.1 <1 <1 9.6 0.016 16 November 25, 2003 5,200 <1 1.9 <1 <1 2.4 0.019 17 February 16, 2004 1,200 <50 <50 <50 <50 11 0.021 11 May 28, 2004 760 <10 <10 <10 <10 35 0.024 20 March 3, 2005 6,500 8.8 <5 1 <1 <1 0.14 1 0.020 1 5.4 Spar •:Insechon,:= ram;,,,•,, May 23, 2005 6,300 <20 <100 <20 <20 0.53 0.023 5.2 August 9, 2005 5,800 <20 <100 <20 <20 0.43 0.015 4.9 December 5, 2005 720 <20 <100 <20 <20 NA <0.010 5.7 April 12, 2006 6,800 <50 <50 <50 <50 0.35 0.019 7.49 October 12, 2006 1,800 <20 <20 <20 <20 1.5 0.019 8.36 April 17, 2007 7,200 <10 I <10 <10 I <10 1 0.044 1 0.015 1 5.81 Water Inj ection .:,�•• , r October 10, 2007 2,350 <50 <10 <10 <10 0.818 0.0162 7.8 April 14, 2010 5,740 11.5 J NA <3.8 <9.8 0.176 0.0109 7.7 _'Water' eetian.Iu1 20I1 �. ,..•• s M July 13, 2011 3,840 <50 NA <50 <50 0.638 0.0091 7.6 September 16, 2011 2,720 <9.4 3.8 J <3.8 <9.8 0.115 0.0092 8.1 September 16, 2011 DUP 2,540 <9.4 3.4 J <3.8 <9.8 0.170 0.0097 8.1 February 28, 2012 2,190 <20 <20 <20 <20 NA NA NA 2L Standard 0.7 3 70 70 100 0.050 0.010 250 µg L = Micrograms per liter All samples through May 2001 collected by Gant Tech, Inc. BDL = Below detection limit (laboratory reporting limit unknown) *Samples Collected through 2007 in passive Diffusion Bag,Saniplers NA = Not analyzed mg/L = milligrams per liter J - Estimated concentration above the adjusted method detection Ibnit and helow the adjusted reporting limit. \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Restdts.xlsx 12 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-20* ' Sample Date PCE in µg/L TCE' in µg/L Chloroform in cis4,2-DCE in trans-1,2-DCE Manganese In Chromium to , hlori e n /L In tot /L m November 27, 2001 <1 <1 <1 <1 <1 NA NA NA Phase I Pilot Test, Phase 11 Pilot Test November 25, 2003 3.2 <1 <1 <1 <1 NA NA NA May 26, 2004 <1 <1 <1 <1 <1 NA NA NA SlurryInflection May 23, 2005 <1 <1 <5 <1 <1 NA NA NA December 5, 2005 <1 <1 <5 <1 <1 NA NA NA April 12, 2006 <1 <1 <1 <1 <1 NA NA NA October 10, 2006 April 17, 2007 <1 <1 <1 <1 <1 NA NA NA Wafer In'ection October23, 2007 <1 <1 3.9 <1 <1 NA NA NA April 13, 2010 <0.46 <0.47 NA <0.19 <0.49 NA NA NA W aker In"ection July, 2011 September 16, 2011 Dry Dry Dry Dry Dry Dry Dry Dry November 27, 2012 <1.0 <1.0 1.7 <1.0 <1.0 NA NA 2.0 2L Standard 0.7 3 70 70 100 0.050 0.010 250 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. BDL = Below detection limit (laboratory reporting limit unknown) *Samples Collected through 2007 in Passive Diffusion Bag Samplers NA =Not analyzed mg/L =milligrams per liter .l - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Pemrit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 13 of25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-21 Sample Date PCG in µg/L TCC in µg/L Chloroform in 1, cis-1,2-DCE in gll, trans-1,2-DCE - inµ /L Manganese in m /L Chromium in m /L Chloride in mg/L Nov ember 27, 2001 22 <1 2 <I <l 0.068 0.002 17 Iul� 9, 2003 <1 <l <1 <l <1 0.03 <0.002 12 Phase 1 Pilot T88t .. . July 30, 2003 18 <1 <1 <1 <l O.017 <0.002 16 August 13, 2003 5.1 <I <1 <1 <1 0.04 <0.002 8.4 Q,=• '', , ..�� � Phase 11 Pilot Test : Se tcmbcr 29, 2003 21 <1 <1 <1 <1 0.014 <0.002 19 October 27, 2003 30 <1 1.5 <1 <1 0.016 <0.002 19 November 20, 2003 35 <1 1.9 <1 <1 0.0004 <0.002 26 February 16, 2004 30 <1 <1 <1 <1 0.020 <0.002 22 May 25, 2004 26 <1 1.9 <1 <1 0.024 0.024 23 March 3, 2005 23 <1 <5 <1 <1 0.013 <0.010 16 <5 <1 <1 0.023 May 23, 2005 24 <1 <0.010 16 August 9, 2005 24 <1 <5 <1 <1 0.028 <0.010 17 December 5, 2005 35 <1 <5 <1 <1 NA <0.010 19 April 10, 2006 45 <1 2.6 <1 <1 0.0098 <0.002 22.7 October 10, 2006 28 <1 1.5 <1 <1 0.034 <0.005 18.3 April 17, 2007 39 <1 1.8 <1 <1 0.014 <0.005 19.2 Water Injection October 10, 2007 9.7 <] <I <I <1 0.0549 <0.005 11.4 April 13, 2010 16.7 -=0.47 NA <0.19 - 0.49 0.0378 1.6 J 13.3 Water Injection July 2011 9/16/2011 21.1 <0.47 1.0 <0.19 <0.49 0.0147 0.00056 J 11.7 11/30/2012 22.1 <1.0 1.2 <1.0 <1.0 NA NA 13.8 November 30, 2012 DUP 22.3 <1.0 1.1 <1.0 <1.0 NA NA NA 2L Standard 0.7 3 70 70 100 0.050 0.010 250 µg/L -Micrograms per liter All samples through May 2001 collected by Gaut Tech, Inc. 'Samples Collected through 2007 in Passive Diffusion Bag Samplers . NA = Not analyzed J- Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BDL = Below detection limit Qaboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 14 of25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina 7MW-22- Sample Date PCE µg/l, TCE in µg/L Chloroform in µg/L cis-12-DCEin �µg/L trans 1,2-DCE Manganese in in /L % mg/l, Chromium in mg/L Chloride in m /L Sc tcmbcr 20, 2002 <I <I <1 I <1 <1 NA NA NA Phase I Pilot Test Phase 11 Pilot Test ' November 20, 2003 <1 <I <1 <I <1 NA NA NA Mav 28, 2004 <I <I <1 <I <1 NA NA NA Slu ry In'ection Mav 23, 2005 <1 <1 <5 <1 <1 NA NA NA December 5, 2005 <1 <1 <5 <1 <1 NA NA NA April 12, 2006 <1 <1 <5 <1 <1 NA NA NA October 10, 2006 April 17, 2007 <l <1 <1 <1 <1 NA NA NA Water Injection: <1 NA NA NA October 23, 2007 <I <I <I <1 April 13, 2010 <0.46 <0.,17 NA <0.19 <0.49 NA NA NA Water In ection July 2011,....: .' . September 14, 2011 <0.46 <0.47 <0.14 1 <0.19 <0.49 0.0076 0.0015 J <5.0 November 27, 2012 <1.0 <1.0 I <1.0 I <1.0 I <1.0 NA NA 2.1 21, Standard 0.7 3 1 70 1 70 1 100 0.050 0.010 250 MW-23 Sample Date PCE in µg/L TCE in µg/L Chloroform in t/L cis-1',2-DCE'in /L trans-1,2-DCE in /L tilanganese in mg/I, Chromium in m /l, Chloride in m */L Water tn'ection July 2011 September 14, 2011 292 25.3 1.7 <0.19 <0.49 0.0497 0.0012 J 5.4 September 30, 2011 205 22.2 2.4 <1.0 <1.0 NA NA NA November 30, 2012 243 20.9 2.7 2.8 <2.0 NA NA 10 2L Standard 0.7 3 70 70 100 0.050 0.010 250 MW-24 Sample Date PCE in µg/L TCE in,µg/L Chloroform in x/I, cis-1,2-DCE in I ttg/l, trans-1,2-DCL in r/l, Manganese in Chromium in m r/L mg/I, Chloride in m r/L Water In'ection July 2011 November 29, 2012 9.1 5.7 1.8 <1.0 DLO NA NA 9.4 2L Standard 0.7 3 70 70 100 0.050 1 0.010 250 µg/L — Micrograms per liter All samples through May 20UI collected by Gaia Tech, Inc. BDL = Below detection limit (laboratory reporting limit unknown) 'Samples Collected through 2007 in Passive D ffusion Bag Samplers NA = Not analyzed mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 15 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina MW-25 Sample Date .7/L 1'CL in }tg/L TCE in µg/L Chloroform in cis-1,2-DCL in I fig/L trans-1,2-DCG in /L Manganese in mg/I, Chromium in nt /L Chloride in nt r/L, Water Injection .July 2011 November 28, 2012 <1 0 < LO <1.0 <LO <I.0 NA NA 40_6 It 2L Standard 0.7 3 70 70 100 0.050 1 0.010 250 MW-26 -T- Sample Date PCE: in µg/L I'CL in µg/L Chloroform in /L cis-1,2-DCL: in tu11 LI trans-1,2-DCE in /I, Manganese in mg/I, Chromium in m !L Chloride in m */L Water Lt'ection July 2011 November 27, 2012 4.6 4 2 6.7 -1 0 <Lo NA NA 17 ; I E 2L Standard 1 0.7 3 1 70 70 100 0.050 1 010 1 250 MW-27 Sample Date PCL in µg/L I'CE in µg/L Chloroform in /L cis-1,2-DCE in g/L trans-1,2-DCL in /l, Manganese in In/L Chromium in m /L Chloride in nt r/l, Water Injection Jul, 2011 Novemher29,2012 <I (I <I 0 -1 o <1.0 I1J) NA 21, Standard 0.7 3 70 70 100 0.050 0 01O 7_�0 MW-28 Sample Date PCL in µg/L I'CE in µg/I, Chloroform in /I cis-1,2-1)(E; in 1491 trans-1,2-DCE in 1, Manganese in m L Chromium in m /L Chloride in m /L Water Injection July 2011 November 27, 2012 <1.0 <1.0 <I0 <1.0 <1.0 NA NA 14.1 2L Standard 0.7 3 70 70 100 1 0.050 1 0.010 1250 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. '.Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed BDL = Below detection limit (laboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 16 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina Sample Date PCE in µg/l, TCE in µg/L Chloroform in L cis-1,2-DCE in /L trans-1,2-DCE in L Manganese in m L Chromium in m /L Chloride in mg/1, y 12. 1999 120 10 11 <5 6 NA NA [7february September8, 1999 210 12 8 <I <1 NA NA NA September 15, 2000 190 11 9.3 <I <1 NA NA NA vember 8, 2000 240 9.4 8.9 <1 <1 NA NA NA 15 2001 310 14 12 <2.5 <2.5 NA NA NA May 8, 2001 240 12 14 <10 <10 NA NA NA November 28. 2001 II 8.6 4.2 <I <I NA NA NA Phase I Pilot Test Phase 11Pilot Test November 24, 2003 <1 <1 6.0 <I _ I N 1 NA NA May 27, 2004 540 11 3 <I 1 NA NA NA March 3, 2005 270 <25 <25 <25 <25 0 oil- 0 017 1 15 Slurry Injection May 23, 2005 400 16 <5 <10 <10 <0.010 0.014 14 August 9, 2005 400 15 <5 <1 <1 0.19 0.013 14 December 5, 2005 420 16 <5 <1 <1 NA 0.014 15 April 11, 2006 590 16 4.1 <1 <1 3.6 0.012 20.7 October 11, 2006 440 15 3.8 <1 <l 1.2 0.012 22.3 April 17. 2007 480 16 <5 <5 <_5 01 0 0l 23 9 Water Injection October 10, 20U7 729 24 6 6 1 <5.0 <; 0 0.379 0 o094 23, 2 April 14, 2010 576 10 9 NA <0.95 -:2.4 L906 n 0073 44 h Water Injection July 2011 L12L July 13, 2011 478 7.3 NA <5 0 <5.0 0.507 0.006 49.2 September 15, 2011 510 12.2 12.4 <0.95 <2.4 0.0942 0.0037 J 50 Standard 0.7 3 70 70 100 0.050 1 0.010 1 250 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. 'Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed J- Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BUL = Below detection limit (laboratory reporting limit unknown) mg1L = milligrams per liter \\boss\Sles\Rojects\Kayser-RothWsheboro - 02600\4 Compliance\4.7 Pemits (Well and Other)\2010 UIC Pennit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 17 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina DW-2 Sample Date PCC in µg/L T'CF, in µg/f, Chloroform in g/L c s-1,2-DCE in /L trans 1,2 �; in N2Uganes40in , •� .,, rominm in m /L Chlorides in m /l:, July 12, 1999 140 <25 <25 <25 <25 NA NA NA September 8, 1999 190 3 14 <1 <1 NA NA NA September 15, 2000 320 3.3 18 <1 <1 NA NA NA November 8, 2000 410 <10 19 <10 <10 NA NA NA February 15 2001 420 <2.5 14 <2.5 <2.5 NA NA NA May 8, 2001 420 <10 18 <10 <10 NA NA NA November 28, 2001 340 4.5 15 <1 <1 0 NA 85 July' 9, 2003 350 <1 <1 <1 <1 0 <0.002 130 Phase I Pilot Test' Jule 30, 2003 250 <I 15 <I <1 0 <O.OU2 120 August 13, 2003 370 <I 33 <1 <1 0 <0.002 130 Phase 1110otfiest Sc tember 29, 2003 <I <I 11 <1 <1 29 0.044 89 October 27, 2003 290 1.5 15 <1 <1 0.079 0.11 100 November 24, 2003 21 <1 16 <1 <1 9.3 0.12 130 February 16, 2004 81 <1 <1 <1 <1 1 0.18 80 May 27, 2004 550 1.4 10 <1 <1 0.016 0.075 160 March 3, 2005 340 3.7 15 <1 <1 <0.010 0.031 90 $In ry Injection u r �_ --7"'W"T— May 23, 2005 390 3.4 14 <10 <10 <0.010 0.022 98 August 9, 2005 330 3.7 11 <1 <1 <0.010 0.021 88 December 5, 2005 390 4.3 11 <1 <1 <0.010 0.021 83 April 11, 2006 710 5.5 12 <1 <1 0.0083 0.017 80.1 October 11, 2006 430 4.6 15 <1 <1 <0.005 0.013 97.0 April 17, 2007 610 <5 15 <5 1 <5 0.037 1 0.0089 1 98.7 <5 <5 0.0344 0.0063 120 October 10, 2007 883 7 5.6 25.2 A ril 14, 2010 717 4.0 J NA <0.95 <2.4 0.153 0.0038 J 126 Watt eetion July 2011JIMIM <5.0 <5.0 0.0391 <0.005 106 July 13, 2011 633 -5.0 NA September 15, 2011 678 Q 4 13-1 <0.95 <2.4 0.0038 J 0.0038 J 98.7 2L Standard 0.7 3 70 70 100 1 0.050 1 0.010 250 Paired with CW-3 µg1L = Micrograms per liter All samples through May 2001 collected by Gaza Tech, Inc. BDL = Below detection limit (laboratory reporting limit unknown) "Samples Collected through 1007 in Passive Dion Bag Samplers NA = Not analyzed mg1L = milligrams per liter J- Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Pemrit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 18 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina pg 'L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. BDL = Below defection limit (laboratory reporting limit unknown) *Samples Collected through 2007 in Passive Diffusion Bag Samplers NA =Not analyzed mg/L =milligrams per lifer J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Pertnit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 19 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina DW-4 Sample Date PCE in µg/L TCE in µg/L Chloroform in µg/l, cis-12-DCE in Ft /L trans-1,2-DCE in /L Manganese in mg/L Chromium in m /L Chlorides in tnglL September 9 1999 <1 39 <I <I <l NA NA NA September 14, 2000 <1 d4 <1 <1 <I NA NA NA February 15, 2001 <0.5 ,2 1.2 <0.5 <0.5 NA NA NA May 8,2001 <1 40 1S <1 <1 NA NA - NA November 28. 2001 <1 29 1.7 <1 <1 NA NA NA Phase 1 Pilot Test Phase 11 Pilot Test November 21, 2003 <1 24 2 6 <I = I NA NA N� Mav 26, 2004 <1 25 3.4 <I <I NA NA NA Sin ry Injection May 23 2005 1.2 24 5.3 <1 <1 0.14 <0.010 13 December 5, 2005 <1 31 <5 <1 71 NA 0.037 14 April 10 2006 <1 35 7.4 <1 <1 0.67 0.021 NA October 10, 2006 <1 37 6.6 <1 <1 0.21 0.0086 22.3 April 17, 2007 <1 37 9.5 <1 <1 0.85 0.028 29.2 Water Injection October 10, 2007 1.1 39.3 90 <I <1 0.4,6 0.0079 27.6 April 14, 2010 1 2 34.9 NA <0.19 <0 49 1,64 0.0712 40.2 Water Injection July 2011 Se tember 14, 2011 <0.46 31.9 21.4 <0.19 <0.49 0.0753 0.0154 41.3 2L Standard 0.7 3 70 70 100 0.050 0.010 250 µgiL = Micrograms per liter All samples throagh May 2001 collected by Gaia Tech, Inc. *Samples Collected through 2007 in Passive Di fusion Bag Samplers NA = Not analyzed J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BDL = Below detection lindt (lohorannnti reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Pemut\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 20 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina DW-S Sample Date PCE in µg/L TCE in µg1L Chloroform in 1rg/L cis-1,2-DCE`in trans-1,2-DCE µg/I, in r/L Manganese in mg/l, Chromium in mg/L Chlorides in mg/L 'V'o\cm[)ci 27.20)l <I 12 11 <I �' I NA NA Phase CPilot Test Phase 11 Pilot Test November 25, 2003 8.5 8.2 15 I - I NA NA NA May 25, 2004 4.5 6.7 17 <I <1 NA NA NA Sin rv'In'ection May 23, 2005 4 7.8 16 <1 <1 0.029 <0.010 52 December 5, 2005 2.8 4.0 11 <1 <1 NA <0.010 37 April 10, 2006 2.4 2.5 15 <1 <1 0.013 <0.002 42.9 October 10, 2006 2.9 3.6 13 <1 <1 0.014 <0.005 40.4 April 17, 2007 3.0 3.8 13 <1 <1 0.0078 <0.005 47.5 October 10, 2007 2.8 4.0 Waterltr'ection 15.0 <1 <1 <0.005 ... <0.005 42.3 April 13, 2010 6.4 10.8 NA <0.19 <0.49 0.286 0.0211 51.9 Water In'ection July,1011 - <0.49 0.0048 J 0.0016 J 49.3 .September 14, 2011 2.6 3.7 16.6 <0.19 November 27, 2012 2.8 3.5 14.1 <1 <1 NA NA 51.5 21, Standard 0.7 3 70 70 100 0.050 0.010 250 DW-6 Sample Date .'L PCE in µglL Chloroform in cis-DCE in 'I'Cl+: in pg/L / µ{t, trans-1,2-DCE in 1., Manganese in m L Chromium in m /L Chlorides in m r/L Water I jection,luly 2011 September 16, 2011 248 5,8 13.8 <0.19 <0,49 0.288 (1.0524 73.3 February 28, 2012 247 5.8 9. 3 <2.0 <2,0 NA NA NA 2L Standard 0.7 3 70 70 7 0.050 0.01 t) 250 DW-7 Sample Date PCE, in µg/l, TCF in µg/L" Chloroform in �µ /I, cis-1,2-DCE in IL trans-1,2-DCE in : L .. Manganese in m /L Chromium in m /L Chlorides in m r/L Water I jectionJuly 2011 Sc tcmbcr 15, 201 1 15.9 29.3 1.6 0.55 J <0.49 0.0138 4.5 J 15.5 September 30, 2011 23.8 26.5 5.1 <1.0 <1.0 NA NA NA February 29, 2012 37.3 23.2 <1.0 <1.0 <1.0 NA NA NA 2L Standard 0.7 3 70 70 100 1 0.050 0.010 250 Paired with C W-6 µgil, = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. BDL = Below detection limit (laboratory reporting limit unknown) 'Samples Collected through 2007 in Passive Diffusion Bag Samplers NA -Not analyzed mg1L = milligrams per liter J- Gstimated concentration above the adjusted method detection limit and below the adjusted reporting limit. \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 21 of25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina DW-8 Sample Date PCE in µg/l, lCE in µg/L Chloroform in µg/L cis-1,2-DCE in I µg/L trans-1,2-DCE in µg/L Manganese in mg/L Chromium in mg/I, Chlorides in ntg/1. Water In'ection July 2011 September 15, 2011 192 47.9 15.7 0.54 J 0.74 .1 0.0871 0.0024 J 1 1) 8 February 28 2012 110 49.6 10.3 <1 <I NA NA NA 2L Standard 70 70 00 0.050 0.010 250 Paired with CW-5 DW-9 Sample Date7_171"', in µg/1. IVE, in µg/IL Chloroform in µg/L, cis-1,2-DCE in µg/L, trans-1,2-DCE in pg/L Manganese in mg/l, Chromium in mg/L Chlorides in mg/L, Water IjeetionJuly ,2011 September 15, 2011 29.6 32.9 10.7 <0.13 <0.26 0.515 0.183 42.7 September 30, 2011 22.2 28 11.7 <1.0 <1.0 NA NA NA ,February 29, 2012 24.7 29 9.4 <I.0 <1.0 NA NA NA �==12L Standard 0.7 3 70 70 100 0.050 0.010 250 DW-10 Sample Date 7PU E in µg/l' LCE in pg/l, Chloroform in /L cis-1,2-DCE in I Pg/L trans-1,2-DCE in µg/t, I Manganese in mg/L Chromium in ntg/l, Chlorides in m /L Water In'ection,July 2011. November 27, 2011 266 <1.0 13.4 <1.0 <1.0 NA NA NA February 29, 2012 331 11.1 Q.0 <2.0 <2.0 NA NA NA .February 29, 2012 DUP 292 10.1 <2.0 Q.0 <2.0 NA NA NA 2L Standard 0.7 3 70 70 100 0.050 0.010 250 Paired with CW-4 DW-11 Sample Date PCE in µg/L TCE in pg/L Chloroform in µg/I, cis-1,2-DCE in µg/L trans-1,2-1)CE inµ /L Manganese in mg/l, Chromium in mg/l, Chlorides in mg/L Water Injection July 2011 Februaty 29, 2012 <1.0 14.5 <1.0 <1.0 <1.0 NA NA NA November 28, 2012 <1.0 22.6 3.7 <1.0 <1.0 NA NA 15.6 2L Standard 0.7 3 70 70 100 0.050 0.010 250 Paired with CW-1 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. 'Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed BDL = Below detection limit (laboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Pemuts (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 22 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina DW-12 Sample Date PCE in µg/L TCE in µg/L Chloroform in µg/L I cis-1,2-DCE in µg/L trans-1,2-DCE in µg/L Manganese in ntg/L Chromium in m /l1 Chlorides in mg/L Water I jeefion July 2011 February 28, 2012 <10 <1.0 -DLO <LO I.0 NA NA N.N November 29, 2012 <1 M <1 o <I.0 <1.0 I I O NA NA 1 2 9 2L Standard 0.7 3 70 70 100 0 050 0,010 1250 Paired with CW-2 DW-13 Sample Date I CE in µg/L TCI; in µg/L Chloroform in µg/L cis-1,2-DCI: in i fig/L trans-1,2-DCE in µg1L Manganese in m g/L Chromium in m dL Chlorides in m /1. Water Injection July 2011 February 28, 2012 <1.0 <1.0 <1.0 <1.0 <LO November 28, 2012 <1.0 <1.0 <1.0 <1.0 <I o NA N,\ � n 2LStandard 0.7 3 70 70 100 0 050 0.010 2>0 DW-14 Sample Date PCE in µg/L TCE in µg/L Chloroform in µglL cis-1,2-DCE in I µg/I, trans-1,2-DCE in µg/L Manganese in mg/L Chromium in mg/l. Chlorides in ntg/l. Water Injection July2011 November 28, 2012 <LU �I o <1.0 <I 0 <1.0 A NA 22.9 2L Standard i).7 70 7u 100 0 o50 0.010 250 DW-15 Sample Date --T--PCI: in µg/L TCE in µg/L Chloroform in µg/L cis-1,2-DCE in L trans-1,2-DCE in µg/L Manganese in mgll, Chromium in mg/l, Chlorides in m /L Water Injection July 2011 November 29, 2012 <LO ,1.0 I <I.0 N/v 105 2L Standard 0.7 70 70 100 0.050 O Ol0 250 DW-16 Sample Date PCE. in µg/l, fCP: in µg/1, Chloroform in µglL cis-1,2-llCE in "W /I, trans-1,2-DCE in µg/l, Manganese in mg/L Chromium in Mg/ L Chlorides in mg/L Water Injection July 2011 November 30, 2012 )0 25, 2 17.5 <1.0 <1.0 NA NA 11) h 2L Standard 0.7 3 70 70 100 0.050 0.010 250 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. 'Samples Collected through 2007 in Passive Dion Bag Samplers NA = Not analyzed BDL = Below detection limit (laboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Petmit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 23 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina DW-17 Sample Date �77µg/l, IVE in µg/L Chloroform in Pg/I cis-1,2-DCE in I µglL trans-1,2-DCE in µg/L Manganese in In Chromium in mg/L Chlorides in mg/l. Water Injection July 2011 November27, 2012 1 124 18.6 7.3 <1.0 <LO NA NA 36.0 2L Standard 0.7 3 70 70 100 0 ono O o l o 250 DW-18 Sample Date PCE in µg/L IVE in µg/l, Chloroform in µg/L, cis-1,2-DCE in /L Gans-1,24DCE inµ 1, Manganese in Chromium in mg/L m /l, Chlorides in mg/L Water Injection.July 2011 November 29, 2012 10.4 8.9 4.6 <1 0 <1 0 NA NA 76 y 2L Standard 0.7 3 70 70 100 0.050 0 010 250 CW-1 Sample Date PCE in µg/l, I CE in µg/C, Chloroform in /L cis-1,2-DCE in µ L trans-1,2-DCE in /L Manganese in m IL Chromium in m /L, Chlorides in mg/L Water Injection .July 2011 I' cbrUary 28, 2012 9.8 1.1 <1.0 <LO NA NA NA November 28, 2012 December 3 2012 <1.0 13.6 1.5 <1.0 <1 0 NA NA 25.4 2L Standard 0.7 3 70 70 100 0.050 0.010 250 Paired with DW-I I CW-2 Sample Date PCE in µg/l,, ICE in µg/L Chloroform in µg/l, cis-1,2-DCE in µglL trans-1,2-DCE in µg/L Manganese in mg/L Chromium in mg/L Chlorides in mg/L Water Injection July 2011 1 chi uar\ 2S. 20l2 <1.0 <LO <LU <1(i <1.0 NA NA NA Febmary 28, 2012 DUP <1.0 <1.0 <1.0 <1.0 <1.0 NA NA NA February 28, 2012 EB <1.0 <1.0 <1.0 <1.0 <1.0 NA NA NA November 29, 2012 <1.0 <1.0 <1.0 <1.0 <1.0 NA NA 3.6 2L Standard 0.7 3 70 1 70 100 0.050 1 0.010 1 250 Paired with DW-12 µg/L = Micrograms per liter All samples through May 2001 collected by Goia Tech, Inc. 'Samples Collected through 2007 in Passive Diffusion Bag Samplers NA = Not analyzed BDL = Below detection limit (laboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Pemuts (Well and Other)\2010 UIC Pennit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 24 of 25 Table 3 Summary of Laboratory Test Results Kayser -Roth Facility Asheboro, North Carolina CW-3 Sample 1), to PCE in µg/L TCE in µg/l, Chloroform in µg/L cis-1,2-DCL in µg/L " trans-1,2-DCE in µg/l, Manganese in mg/L Chromium in mg/1. Chlorides in ntg/1, Water In'ection July 2011 November 30, 2012 4 u 1.3 <l 0 1.0 0.0054 18.0 November 30, 2012 DUP 4 4 1,4 <1,0 <L.0 \ NA NA 2L Standard 70 70 100 0.010 '50 Paired with DW-2 CW-d Sample Date PCL in µg/L TC[; in µg/1, Chloroform in µg/1, cis-1,2-DCE in µg/L trans-1,2-DCE in µg/l, Manganese in mg/L Chromium in mg/L Chlorides in mg/L Water In'ection July 2011 November 30, 2012 <1.0 < I u <1.0 <1.0 < 1.0 NA NA 3.1 November 30, 2012 DUP <1.0 <1.0 <1.0 <1.0 LO NA NA NA 2L Standard 0.7 3 70 70 100 0.050 0.010250 Paved with DW-10 CW-5 Sample Date PCE in µg/L i'CB; in Itg/1, Chloroform in µg/L cis-1,2-DCE 7t—r,—,ns-1,2-DCE L in µ r L Manganese in m g/L Chrontiurn in m 1L Chlorides in mg/1, Water lRiection July 2011 November 30, 2012 <1.0 1.9 <1.0 <1 0 NA NA11 3 2L Standard 0.7 3 70 70 100 0.050 0.010 250 Paired with DW-8 CW-6 Sample Date PCE in pg/L TCE in µg/L Chloroform in µg1L cis-1,2-DCE in I µg/L trans-1,2-1)('L in µg/l,, I Manganese in mg/L I Chromium in mg/L Chlorides in m /l. Water In'eetion July 2011 December 3, 2012 <1.0 8 <1.0 <1.0 <1.0 0.0247 <0.005 7 5 December 3, 2012 DUP <1.0 8.6 <1.0 <1.0 <1.0 NA NA NA 2L Standard 0.7 3 70 70 100 0.050 0.010 250 Paired with D W-7 µg/L = Micrograms per liter All samples through May 2001 collected by Gaia Tech, Inc. "Samples Collected through 1007 in Passive Dion Bag Samplers NA = Not analyzed J- Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. BDL = Below detection limit (laboratory reporting limit unknown) mg/L = milligrams per liter \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Pemtit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx 25 of25 , Table 4 Summary of Laboratory Test Results, HSL Metals Kayser -Roth Facility Asheboro, North Carolina A»alyt><cal Method ID 3 MW 3 2L SiandardSample Antimony <2.6 1 * Arsenic 2.8 J 10 Beryllium <0.10 4* Cadmium <0.50 2 Chromium 1.2 J 10 Copper 1.4 J 1000 EPA 6010 Lead <4.0 15 Manganese 9.5 50 Nickel <1.7 100 Selenium 6.1 J 20 Silver 0.79 J 20 Thallium <3.0 0.2* Zinc 13.2 1000 EPA 7470 Mercury <0.10 1 Notes: r Sample collected September 14, 2011 Concentrations in µg/L 2L Standard -15A NCAC 2L. 0202 * - 2L IMACs standard - Inerim Maximum Allowable Concentrations NE- not established J- Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. Bold Value - Analyte detected at a concentration that exceeds the method detection limit (MDL) \\boss\files\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx Table 5 Sumi'iiwry,,of Laboratory Test Results, Non -Chlorinated VOCs Kayser -Roth Facility `2 AAsheboro, North Carolina Analytical'Method, ..Volatile:Organic:Connpounds-,EPA.1VIethod 8260B' Analyte -� 2 $utanorif '' ' . °ID 1VIEK "' promethane Chi 1,2 D�chloropropane 'T oluene Tr <' orofluorpmethah' Sam le P .Sam le Date P �. MW-2b 5/20/2010 <50.0 <10.0 <2.5-�-, <1.0 <5.0 <5.0 MW-3 9/15/2011 <4.3 . <1.9•'• <01.2 <0.54 0.57 J <0.40 DW-8 9/15/2011 <2.2 -<O.96. --• 0.24 - 0.74 J NM 0.23 J DW-9 9/15/2011 4.7 J ,50.96 0.34-J 0.32 J <0.26 1.7 DW-10 2/29/2012 <50.0 767» J <2.0 <2.0 <2.0 <2.0 DW-IODup 2/29/2012 4.7 J 11.7 :' <2.0. <2.0 1 <2.0 <2.0 DW-13 2/28/2012 223 <5.0 <1.0 <1.0 <1.0 <1.0 2L Standard 6,000 WE p .: 3 0.6 600 2,000 Concentrations in µg/L - NM- not measured NE- not established J - Estimated concentration above the adjusted method detection limit and belowThe adjusted reporting limit. Bold Value - Analyte detected at a concentration that exceeds the method detection limit or method -reporting limit. 2L Standard - North Carolina groundivater quality standards, 15A NCAC 2L. 0202 \\bossTfiles\Projects\Kayser-Roth\Asheboro - 02600\4 Compliance\4.7 Permits (Well and Other)\2010 UIC Permit\UIC Summary Reports\2009-2013 Summary Report\Tables\Tables 3-5 - Summary of Laboratory Test Results.xlsx Appendix A l AJ CoK- fs a�Vai ia.b! " - -el ec, ro n i c, vers oo? �4-5 doc.um en t w 4x,'G- f sot vteL in W q_ c34;tp� c/nrve,