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HomeMy WebLinkAbout17060_Perfecting_Confirmatory IAS Report 2019.08.23SITEATANDO AVEROBINSON CIRN. TRYON STDATE :SCALE :DRAWN BY : FIGURE :SHIELDENGINEERING, INC.704-394-6913704-394-6968 faxwww.shieldengineering.com4301 TAGGART CREEK ROADCHARLOTTE, NC 28208SITE LOCATION MAP07/19/191" = 500'DWAUTOMOTIVE GROUP, LLCCHARLOTTE, NORTH CAROLINA332 ATANDO AVENUESHIELD #1150187-011H:\Projects\2015\1150187-01 Automotive Group, LLC Brownfields Assistance\Figures\SITE LOCATION MAP.dwg MW-1MW-3MW-2SS-02SS-01SS-03SS-05SS-04SS-06SS-07SS-08AG-2IA-2IA-2DAG-1IA-1AG-3IA-3AG-11IA-11AG-10IA-10IA-10/AAG-5IA-5AG-6IA-6AG-7IA-7AG-8IA-8AG-12IA-12AG-4IA-4BG-1BG-3BG-5BG-4BG-2HA-1HA-2IA-13S-1BG-6RECENTLY ENCOUNTEREDPOTENTIAL AREA OF CONCERNAG-9IA-9A/BIA-9C/D704-394-6913 704-394-6968 fax www.shieldengineering.com SHIELD ENGINEERING, INC. H:\Projects\2015\1150187-01 Automotive Group, LLC Brownfields Assistance\Figures\AREA MAP REV 7-19-19.dwg , 8/22/2019 3:34 PM , David Weikle The drawings, specifications and other documents prepared by Shield engineering for this project are instruments of Shield Engineering for use solely with respect to this prroject and, unless otherwise provided, Shield shall be deemed the author of these documents and shall retain all common law, statutory and other reserved rights, including copyright. DRAWN BY: HMH CHECKED BY: DAS PROJECT NUMBER: 1150187-01 SCALE: 1" = 100' DATE: 08/22/2019SEAL:AUTOMOTIVE GROUP, LLC 332 ATANDO AVE CHARLOTTE, NORTH CAROLINA SAMPLING LOCATION MAP 2SHEET:(IN FEET)GRAPHIC SCALE01"=100'50100200S E W N NOT FORCONSTRUCTIONLEGENDAPPROXIMATE MONITORING WELL LOCATIONMW-#SS-#APPROXIMATE SOIL SAMPLE LOCATIONAPPROXIMATE SOIL BORING LOCATIONAPPROXIMATE SUB-SLAB VAPOR MONITORING LOCATIONS(BY SHIELD ENGINEERING, INC. [SHIELD] AUGUST, 2016)(BY ENVIRO/PROBE, INC. OCTOBER, 2013 , PROVIDED BY NORTH CAROLINADEPARTMENT OF ENVIRONMENTAL QUALITY)(BY SHIELD AUGUST, 2016)(BY SHIELD FEBRUARY, 2018)S-#AG-#IA-#APPROXIMATE INDOOR AIR SAMPLING LOCATIONS.BG-#APPROXIMATE OUTDOOR BACKGROUND AIR SAMPLINGLOCATIONS FOR QA/QC.HA-#APPROXIMATE INDOOR SOIL SAMPLING LOCATIONSBLUE #RECENT APPROXIMATE SAMPLE LOCATIONS DATE :SCALE :DRAWN BY : FIGURE :SHIELDENGINEERING, INC.704-394-6913704-394-6968 faxwww.shieldengineering.com4301 TAGGART CREEK ROADCHARLOTTE, NC 28208GROUNDWATER ELEVATION CONTOUR MAP02/15/17AS SHOWNRBSAUTOMOTIVE GROUP, LLCCHARLOTTE, NORTH CAROLINA332 ATANDO AVENUESHIELD #1150187-023H:\Projects\2015\1150187-01 Automotive Group, LLC Brownfields Assistance\Figures\AREA MAP REV 8-31-16.dwgLEGENDMONITORING WELL LOCATIONMW-1100GRAPHIC SCALESCALE: 1 in. = 100 ft.2505075Reference: Mecklenburg County POLARIS GISMW-2MW-3MW-1AUTO CARESOIL BORING LOCATIONS-1(84.49)(83.81)(92.80)FEET(ft)GROUNDWATER ELEVATION (ft)(92.80)GROUNDWATER ELEVATION (ft)GENERALIZED GROUNDWATER FLOWCONTOUR LINEDIRECTIONNOTES:1. DEPTH TO GROUNDWATER MEASURED ON 08/22/162. CONTOUR INTERVAL AS SHOWN.3. ALL LOCATIONS ARE APPROXIMATE.92'91' 90 ' 89 ' 88 ' 87 ' 86 ' 85' 84 ' 1,1-Dichloroethenecis-1,2-DichloroetheneTetrachloroethene (PCE)Trichloroethene (TCE)Vinyl ChlorideIA-9C Building 4 Storage +07/31/19 ND ND 21.0 0.94 ND IA-9D Building 4 Storage +07/31/19 ND ND 19.7 0.91 ND IA-10A Building 5 Offices 07/31/19 ND ND 4.8 ND ND BG-6 Outside Between Bldgs. 4&5 07/31/19 ND ND ND ND ND 180 NS 35 1.8 2.8 Notes: ug/m3 = micrograms per cubic meter J = Estimated concentration above adjusted method detection limit and below adjusted reporting limit. ND = Not detected above laboratory detection limit. IHSB = Inactive Hazardous Sites Branch (IHSB) NS = No IHSB Non-Residential Vapor Intrusion Screening Level. Values bolded exceed the IHSB Non-Residential Vapor Intrusion Screening Level (February 2018) IHSB Non-Residential Vapor Intrusion Screening Levels Sample IDSample LocationSampling DateResults in ug/m3 Analytical Method TO-15 Table 1 Recent Indoor Air Analytical Data 332 Atando Avenue Charlotte, North Carolina Shield Engineering Job No. 1150187 1,1-Dichloroethenecis-1,2-DichloroetheneTetrachloroethene (PCE)Trichloroethene (TCE)Vinyl ChlorideIA-1 Building 1 Auto Service 08/06/18 IA-2 Building 1 Auto Service 08/06/18 1.3 IA-2(D)Building 1 Auto Service 08/06/18 2.7 IA-3 Building 1 Auto Service 08/06/18 0.59J IA-4 Building 2 Engine & Parts Storage 08/06/18 4.2 IA-5A Building 3 Storage & Transport 08/07/18 14.7 IA-6 Building 2 Engine & Parts Storage 08/06/18 6.3 IA-7 Building 3 Storage & Transport 08/06/18 4.0 IA-8 Building 4 Storage +08/06/18 9.0 IA-9 Building 4 Storage +08/06/18 74.4 2.7 IA-9A Building 4 Storage +09/14/18 85.2 2.7 IA-9B Building 4 Storage +02/20/19 5.8 IA-9C Building 4 Storage +07/31/19 21.0 0.94 IA-9D Building 4 Storage +07/31/19 19.7 0.91 IA-10 Building 5 Offices 08/06/18 8.3 IA-10A Building 5 Offices 07/31/19 4.8 IA-11 Building 5 Offices 08/06/18 6.3 IA-12 Building 6 Storage 08/06/18 8.7 IA-13 Building 4 Storage +02/20/19 6.6 BG-1 Outside Between Bldgs. 4&5 08/06/18 BG-3 Outside Between Bldgs. 4&5 08/07/18 BG-4 Outside Between Bldgs. 4&5 09/14/18 BG-5 Outside Between Bldgs. 4&5 02/20/19 BG-6 Outside Between Bldgs. 4&5 07/31/19 180 NS 35 1.8 2.8 Notes: ug/m3 = micrograms per cubic meter J = Estimated concentration above adjusted method detection limit and below adjusted reporting limit. IHSB = Inactive Hazardous Sites Branch (IHSB) NS = No IHSB Non-Residential Vapor Intrusion Screening Level. Blank boxes = No detections above laboratory report limit Values bolded exceed the IHSB Non-Residential Vapor Intrusion Screening Level (February 2018) IHSB Non-Residential Vapor Intrusion Screening Levels Sample IDSample LocationSampling DateResults in ug/m3 Analytical Method TO-15 Table 2 Summary of Historical Indoor Air Analytical Data 332 Atando Avenue Charlotte, North Carolina Shield Engineering Job No. 1150187 AcetoneBenzene2-Butanone (MEK)Carbon disulfideChloroformCyclohexaneDichlorodifluoromethane1,4-Dichlorobenzene1,1-Dichloroethane1,1-Dichloroethene1,2-Dichloroethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene (trans-1,2-DCE)Ethyl acetateEthylbenzene4-Ethyltoluenen-Heptanen-Hexane2-HexanoneMethylene Chloride4-Methyl-2-pentanoneNaphthalenePropyleneStyreneTetrachloroethene (PCE)TetrahydrofuranToluene1,1,1-Trichloroethane 1,1,2-Trichloroethane Trichloroethene (TCE)1,1,2-Trichlorofluoroethane1,2,4-Trimethylbenzene1,3,5-TrimethylbenzeneVinyl ChlorideXylene, m- & p-Xylene, o-AG-1 Building 1 Auto Service 02/12/18 518 51.2 9.9 1430 8230 888 8.9 7 42.3 1560 4.5J 6.7 441 108 106 19800 11.7 3.1 47.8 17.2 AG-2 Building 1 Auto Service 02/12/18 2440J 5020 625000 2950 2580 3380000 709000 1840 AG-3 Building 1 Auto Service 02/12/18 20.6 56.3 61.3 21.9 29.8 26.3 1820 2.1J 2.0 101 248 92.6 49.8 14.2 81.5 36.8 AG-4 Building 2 Engine & Parts Storage 02/12/18 474 2.1 37.7 109 16.6 1.9 53.2 0.79J 3.3 5.7J 2270000 31.0 5730 0.72J 1.5J AG-5 Building 3 Storage & Transport 02/12/18 62.1 18.4 5.0 3.2 8.1 22.0 51.4 24300 37.3 5.9 212000 3.2 5980 0.94J 1.9J 2.0 AG-5D Building 3 Storage & Transport 02/13/18 24.8 16.7 5.5 7.1 20.1 45.3 30700 14.9 0.80J 1.7 4.7 390000 4.0 7670 3.2 1.0J 4.1 2.2 AG-6 Building 2 Engine & Parts Storage 02/13/18 289 0.92 26.9 2.5 36.4 0.93J 4.1 3.6J 3.4J 2260 1.0J 22.2 15.1 2.3 5.1 1.8 AG-7 Building 3 Storage & Transport 02/13/18 43.9 1.8 4.7 5.1 537 3.0 23300 2.3 525 1.9J AG-8 Building 4 Storage +02/13/18 31.8 4.5 21.9 558 2.3 5.0 1.1J 105 41.6 AG-9 Building 4 Storage +02/12/18 206 703 9.6 1140 1.1J 25000 11200 83.3 22.6 3.6J 1510000 82.7 42.9 126000 0.84J AG-10 Building 5 Offices 02/12/18 56.0 1.5 2.9J 0.75 12.1 15.4 8.6 0.88J 1.8 7250 3.0 104 1.9 2.6J AG-11 Building 5 Offices 02/12/18 18.4 4.1J 2.4 1.7 1.5 4.6J 2000 2.5 2.2 39.1 7.4 2.6 AG-12 Building 6 Storage 02/12/18 44.5 7.4 2.5 0.79J 86300 73.3 17.7 0.82J 3.6 2700000 1600 440000 61000 530 530000 8800 1100 7700 18000 470 --6100 4900 -35000 61000 2600 53000 260000 260 260000 88000 3500 -440000 440000 18 180 440000 5300 5300 2800 8800 ea.8800 Notes: ug/m3 = micrograms per cubic meter J = Estimated concentration above adjusted method detection limit and below adjusted reporting limit. Blank boxes = No detections above laboratory report limit Shaded boxes indicates concentration exceeds Inactive Hazardous Sites Branch (IHSB) Non-Residential Sub-Slab and Exterior Soil-Gas Vapor Intrusion Screening Level (February 2018) IHSB Sub-Slab & Exterior Soil Gas Screening Level Sample IDSample LocationSampling DateUnits = ug/m3 Analytical Method TO-15 Table 3 Summary of Sub-Slab Vapor Analytical Data 332 Atando Avenue Charlotte, North Carolina Shield Engineering Job No. 1150187 BariumChromium**Hexavalent ChromiumLeadMercury (elemental)SeleniumMADEP EPH Aliphatics C9-C18***MADEP EPH Aliphatics C19-C36MADEP EPH Aromatics C11-C22****MADEP VPH Aliphatics C5-C12***MADEP VPH Aromatics C9-C10****AcetoneBenzene1,1-Dichloroethane1,2-Dichloroethane1,1-Dichloroethenecis-1,2-DichloroetheneMethyl acetateMethylene ChlorideTetrachloroethene (PCE)1,1,2-Trichloroethane Trichloroethene (TCE)bis(2-ethylhexyl)phthalatePCB Aroclor 1254alpha-Chlordanegamma-Chlordanebeta-BHC4,4'-DDTDieldrinEndrin aldehydegamma-ChlordaneSample ID Date Collected Sample Depth Interval mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 3,100 24,000*0.3 400 2.3 78 1,500 31,000 469 1,500 469 12,200 1.2 3.8 0.49 48 32 15,600 58 16.2 0.32 0.87 39 NS NS NS 0.3 1.9 0.034 NS NS 47,000 100,000*6.3 800 9.7 1,200 40,000 810,000 12,264 40,000 12,264 100,000 5.4 17 2.2 210 460 29,000 650 78 1.3 4 160 NS NS NS 1.3 8.5 0.14 NS NS 580 360,000*3.8 270 1 2.1 540 NS 31 540 31 24 0.01 0.034 0.0023 2.5 0.36 NS 0.025 0.005 0.0039 0.021 7.2 NS NS NS 0.001 0.34 0.00081 NS NS S-1 8/22/2016 1'-2'182 ND S-1 8/22/2016 5'-6'201 ND S-1 8/22/2016 20'-21'287 ND SS-01 10/21/2013 ≈ 12'230 22 ND 180 28 ND ND ND ND ND ND ND ND ND ND 0.011 ND ND 1.7 0.1 ND ND ND 0.04 ND ND ND SS-02 10/21/2013 ≈ 12'190 43 ND 230 36 ND ND ND ND ND ND ND ND ND ND 0.021 ND ND 1.7 0.18 ND ND ND 0.06 0.026 ND ND SS-03 10/21/2013 ≈ 12'150 230 ND 89 18 ND ND ND ND ND ND ND ND ND ND 0.014 ND ND 8.4 0.28 ND ND ND 0.086 0.026 ND ND SS-04 10/21/2013 ≈ 12'150 170 ND 75 14 ND ND 0.025 ND ND ND ND ND ND ND 0.038 ND ND 7.8 0.18 ND ND ND 0.05 ND ND ND SS-05 10/21/2013 ≈ 12'250 340 96 3,100 390 ND ND 0.022 ND ND ND ND ND ND ND 0.24 ND ND ND 0.26 ND 0.041P ND 0.41 0.19 0.036 0.041P SS-06 10/21/2013 ≈ 12'510 270 ND 420 65 ND ND ND ND ND ND ND ND ND ND 0.037 ND ND 0.71 0.76 ND ND ND 0.27 0.087 ND ND SS-07 10/21/2013 ≈ 12'230 29 ND 150 26 ND ND 0.026 ND ND ND ND ND ND ND ND ND ND 9.7 0.094 ND ND ND 0.028 ND ND ND SS-08 10/21/2013 1'-3'130 47 ND 130 17 ND ND ND ND ND ND ND ND ND ND ND ND ND 6.7 0.15 ND ND ND 0.044 ND ND ND Stockpile SP-01*10/21/2013 86 22 1,600 7,000 1,100 110 31 ND ND ND ND ND 0.83 1.9 ND 15 ND ND ND ND ND ND 0.035P ND ND ND ND Stockpile SP-02*10/21/2013 69 9.2 1,700 7,500 1,000 66 19 ND ND ND ND ND ND 1.3 ND 8.6 ND ND ND 0.16 0.023P ND 0.038P ND ND ND ND Stockpile SP-03*10/21/2013 130 35 ND 230 34 ND ND 0.027 ND ND ND ND ND 0.007 ND 0.021 ND ND 5.2 0.23P ND ND ND 0.073 0.033 ND ND Stockpile SP-04*10/21/2013 160 60 17 400 40 ND ND ND ND ND ND ND ND ND ND 0.012 ND ND 8.5 0.28 ND ND ND 0.064 0.029 ND ND BG 10/21/2013 50 610 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND MW-1 8/22/2016 1'-2'67.9 ND MW-1 8/22/2016 5'-6'20.9 ND MW-1 8/22/2016 20'-21'3.5 ND HA-1 8/7/2018 1'-1.5'10 9.0 ND 3.3 0.070 ND 1.36 0.0019J 0.0101 ND 0.0171 0.0190 0.0112J 0.851 0.0029J 0.0717 ND HA-1 8/7/2018 4'-5'51.2 11.1 ND 4.8 0.073 4.6 ND 0.0025J 0.0084 ND 0.0062J 0.0175 0.0241J 4.990 0.0075 0.106 ND HA-2 8/7/2018 3'-4'59.4 9.9 ND 4.2 0.0091 7.2 ND ND ND ND ND ND ND ND ND ND ND 1. * The Stockpiles were removed offsite and disposed. 2. ** The PSRG used for chromium is the PSRG for the insoluble salt, trivalent chromium. 3. PSRGs are the North Carolina Inactive Hazardous Sites Branch Preliminary Soil Remediation Goals or if none exist, then the Underground Storage Tank Maximum Soil Contaminant Concentrations (MSCCs) 4. The 2016 investigation only tested soil for chromium and hexavalent chromium. 5. The 2016 data was collected by Shield Engineering, Inc. 6. The 2013 data was collected by ENVRO\PROBE, INC., and obtained as public information. 7. NS indicates that no North Carolina Standard (PSRG or MSCC) exists. 8. ND indicates not detected at or above the method detection limit specified in the laboratory report. 9. Blank/empty box indicates not analyzed for this parameter 10. Values bolded exceed the parameter's Industrial/Commercial Health Based PSRG. 11. MADEP EPH and VPH = Massachusetts Department of Environmental Protection Extractable and Volatile Petroleum Hydrocarbons 12. *** EPH and VPH Aliphatics in range of C5-C18 get added together; still none exceeded the Industrial Commercial MSSCs 13. **** EPH and VPH Aromatics in range of C9-C22 get added together; still none exceeded the Industrial Commercial MSSCs 14. Values with a "P" after them had the qualifier "Relative Percent Difference between 2 Gas Chromatography columns exceeds 40%." Contaminant of Concern Unrestricted Use Health Based PSRG Industrial/Commercial Health Based PSRG Protection of Groundwater PSRG Table 4 Shield Engineering Job No. 1150187 Summary of Soil Analytical Data -2013, 2016, and 2018 332 Atando Avenue Charlotte, North Carolina Page 1 of 1 Contaminant of Concern ChromiumCopperManganeseNickelZinc1,1-Dichloroethane1,1-Dichloroethenecis-1,2-DichlroetheneTetrachloethene (PCE)TrichloroetheneSample ID Date Collected (m/dd/yy)mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L 15A NCAC 2L Groundwater Stds. 0.01 1 0.05 0.1 1 0.006 0.35 0.07 0.0007 0.003 IHSB Non-Res. Vapor Intrusion SLs NS NS NS NS NS 0.334 0.164 NS 0.0484 0.00435 MW-1 08/24/16 ND 0.0097 1.130 0.0056 0.0186 ND ND ND ND ND MW-2 08/24/16 0.0056 0.0052 0.482 0.0191 0.0133 0.0052 ND 0.561 0.999 0.0661 MW-3 08/24/16 0.0059 ND 0.612 ND 0.0111 ND 0.0327 0.0431 0.623 0.108 Notes: 1. mg/L = Milligrams per liter 2. ND = Not detected at or above the method detection limit specified in the laboratory report. 3. Bold numbers exceed the 15ANCAC 2L Groundwater Standards. 4. Bold shaded values exceed the North Carolina IHSB Non-Residential Vapor Intrusion Groundwater Screening Levels. Table 5 Summary of Groundwater Analytical Data H:\Projects\2015\1150187-01 Automotive Group, LLC Brownfields Assistance\Confirmatory Indoor Air Sampling July, 2019\Table 5 - Summary of Groundwater Analytical Data.xls Page 1 of 1 #=CL# August 13, 2019 LIMS USE: FR - DAVID STONER LIMS OBJECT ID: 92439578 92439578 Project: Pace Project No.: RE: Mr. David Stoner Shield Engineering 4301 Taggart Creek Road Charlotte, NC 28208 Automotive Group Dear Mr. Stoner: Enclosed are the analytical results for sample(s) received by the laboratory on August 01, 2019. The results relate only to the samples included in this report. Results reported herein conform to the most current, applicable TNI/NELAC standards and the laboratory's Quality Assurance Manual, where applicable, unless otherwise noted in the body of the report. If you have any questions concerning this report, please feel free to contact me. Sincerely, Amanda Payne amanda.payne@pacelabs.com Project Manager (704)875-9092 Enclosures REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 1 of 12 #=CP# CERTIFICATIONS Pace Project No.: Project: 92439578 Automotive Group Minnesota Certification IDs 1700 Elm Street SE, Minneapolis, MN 55414-2485 A2LA Certification #: 2926.01 Alabama Certification #: 40770 Alaska Contaminated Sites Certification #: 17-009 Alaska DW Certification #: MN00064 Arizona Certification #: AZ0014 Arkansas DW Certification #: MN00064 Arkansas WW Certification #: 88-0680 California Certification #: 2929 CNMI Saipan Certification #: MP0003 Colorado Certification #: MN00064 Connecticut Certification #: PH-0256 EPA Region 8+Wyoming DW Certification #: via MN 027- 053-137 Florida Certification #: E87605 Georgia Certification #: 959 Guam EPA Certification #: MN00064 Hawaii Certification #: MN00064 Idaho Certification #: MN00064 Illinois Certification #: 200011 Indiana Certification #: C-MN-01 Iowa Certification #: 368 Kansas Certification #: E-10167 Kentucky DW Certification #: 90062 Kentucky WW Certification #: 90062 Louisiana DEQ Certification #: 03086 Louisiana DW Certification #: MN00064 Maine Certification #: MN00064 Maryland Certification #: 322 Massachusetts Certification #: M-MN064 Michigan Certification #: 9909 Minnesota Certification #: 027-053-137 Minnesota Dept of Ag Certifcation #: via MN 027-053-137 Minnesota Petrofund Certification #: 1240 Mississippi Certification #: MN00064 Missouri Certification #: 10100 Montana Certification #: CERT0092 Nebraska Certification #: NE-OS-18-06 Nevada Certification #: MN00064 New Hampshire Certification #: 2081 New Jersey Certification #: MN002 New York Certification #: 11647 North Carolina DW Certification #: 27700 North Carolina WW Certification #: 530 North Dakota Certification #: R-036 Ohio DW Certification #: 41244 Ohio VAP Certification #: CL101 Oklahoma Certification #: 9507 Oregon Primary Certification #: MN300001 Oregon Secondary Certification #: MN200001 Pennsylvania Certification #: 68-00563 Puerto Rico Certification #: MN00064 South Carolina Certification #:74003001 Tennessee Certification #: TN02818 Texas Certification #: T104704192 Utah Certification #: MN00064 Vermont Certification #: VT-027053137 Virginia Certification #: 460163 Washington Certification #: C486 West Virginia DEP Certification #: 382 West Virginia DW Certification #: 9952 C Wisconsin Certification #: 999407970 Wyoming UST Certification #: via A2LA 2926.01 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 2 of 12 #=SA# SAMPLE ANALYTE COUNT Pace Project No.: Project: 92439578 Automotive Group Lab ID Sample ID Method Analytes Reported LaboratoryAnalysts 92439578001 IA-9C TO-15 5 PASI-MNCK 92439578002 IA-9D TO-15 5 PASI-MNCK 92439578003 IA-10A TO-15 5 PASI-MNCK 92439578004 BG-6 TO-15 5 PASI-MNCK REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 3 of 12 #=NA# PROJECT NARRATIVE Pace Project No.: Project: 92439578 Automotive Group Method: Client:Shield TO-15 Date:August 13, 2019 Description:TO15 MSV AIR General Information: 4 samples were analyzed for TO-15. All samples were received in acceptable condition with any exceptions noted below or on the chain-of custody and/or the sample condition upon receipt form (SCUR) attached at the end of this report. Hold Time: The samples were analyzed within the method required hold times with any exceptions noted below. Initial Calibrations (including MS Tune as applicable): All criteria were within method requirements with any exceptions noted below. Continuing Calibration: All criteria were within method requirements with any exceptions noted below. Internal Standards: All internal standards were within QC limits with any exceptions noted below. Method Blank: All analytes were below the report limit in the method blank, where applicable, with any exceptions noted below. Laboratory Control Spike: All laboratory control spike compounds were within QC limits with any exceptions noted below. Duplicate Sample: All duplicate sample results were within method acceptance criteria with any exceptions noted below. Additional Comments: This data package has been reviewed for quality and completeness and is approved for release. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 4 of 12 #=AR# ANALYTICAL RESULTS Pace Project No.: Project: 92439578 Automotive Group Sample:IA-9C Lab ID:92439578001 Collected:07/31/19 14:46 Received:08/01/19 11:46 Matrix:Air Parameters Results Units DF Prepared Analyzed CAS No.QualReport Limit Analytical Method: TO-15TO15 MSV AIR 1,1-Dichloroethene ND ug/m3 08/07/19 23:34 75-35-41.4 1.68 cis-1,2-Dichloroethene ND ug/m3 08/07/19 23:34 156-59-21.4 1.68 Tetrachloroethene 21.0 ug/m3 08/07/19 23:34 127-18-41.2 1.68 Trichloroethene 0.94 ug/m3 08/07/19 23:34 79-01-60.92 1.68 Vinyl chloride ND ug/m3 08/07/19 23:34 75-01-40.44 1.68 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 08/13/2019 04:39 PM Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 5 of 12 #=AR# ANALYTICAL RESULTS Pace Project No.: Project: 92439578 Automotive Group Sample:IA-9D Lab ID:92439578002 Collected:07/31/19 15:20 Received:08/01/19 11:46 Matrix:Air Parameters Results Units DF Prepared Analyzed CAS No.QualReport Limit Analytical Method: TO-15TO15 MSV AIR 1,1-Dichloroethene ND ug/m3 08/08/19 00:04 75-35-41.3 1.61 cis-1,2-Dichloroethene ND ug/m3 08/08/19 00:04 156-59-21.3 1.61 Tetrachloroethene 19.7 ug/m3 08/08/19 00:04 127-18-41.1 1.61 Trichloroethene 0.91 ug/m3 08/08/19 00:04 79-01-60.88 1.61 Vinyl chloride ND ug/m3 08/08/19 00:04 75-01-40.42 1.61 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 08/13/2019 04:39 PM Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 6 of 12 #=AR# ANALYTICAL RESULTS Pace Project No.: Project: 92439578 Automotive Group Sample:IA-10A Lab ID:92439578003 Collected:07/31/19 15:00 Received:08/01/19 11:46 Matrix:Air Parameters Results Units DF Prepared Analyzed CAS No.QualReport Limit Analytical Method: TO-15TO15 MSV AIR 1,1-Dichloroethene ND ug/m3 08/08/19 00:33 75-35-41.2 1.55 cis-1,2-Dichloroethene ND ug/m3 08/08/19 00:33 156-59-21.2 1.55 Tetrachloroethene 4.8 ug/m3 08/08/19 00:33 127-18-41.1 1.55 Trichloroethene ND ug/m3 08/08/19 00:33 79-01-60.85 1.55 Vinyl chloride ND ug/m3 08/08/19 00:33 75-01-40.40 1.55 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 08/13/2019 04:39 PM Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 7 of 12 #=AR# ANALYTICAL RESULTS Pace Project No.: Project: 92439578 Automotive Group Sample:BG-6 Lab ID:92439578004 Collected:07/31/19 14:43 Received:08/01/19 11:46 Matrix:Air Parameters Results Units DF Prepared Analyzed CAS No.QualReport Limit Analytical Method: TO-15TO15 MSV AIR 1,1-Dichloroethene ND ug/m3 08/07/19 23:05 75-35-41.4 1.75 cis-1,2-Dichloroethene ND ug/m3 08/07/19 23:05 156-59-21.4 1.75 Tetrachloroethene ND ug/m3 08/07/19 23:05 127-18-41.2 1.75 Trichloroethene ND ug/m3 08/07/19 23:05 79-01-60.96 1.75 Vinyl chloride ND ug/m3 08/07/19 23:05 75-01-40.46 1.75 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 08/13/2019 04:39 PM Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 8 of 12 #=QC# QUALITY CONTROL DATA Pace Project No.: Project: 92439578 Automotive Group Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. QC Batch: QC Batch Method: Analysis Method: Analysis Description: 624902 TO-15 TO-15 TO15 MSV AIR Low Level Associated Lab Samples:92439578001, 92439578002, 92439578003, 92439578004 Parameter Units Blank Result Reporting Limit Qualifiers METHOD BLANK:3372500 Associated Lab Samples:92439578001, 92439578002, 92439578003, 92439578004 Matrix:Air Analyzed 1,1-Dichloroethene ug/m3 ND 0.81 08/07/19 13:54 cis-1,2-Dichloroethene ug/m3 ND 0.81 08/07/19 13:54 Tetrachloroethene ug/m3 ND 0.69 08/07/19 13:54 Trichloroethene ug/m3 ND 0.55 08/07/19 13:54 Vinyl chloride ug/m3 ND 0.26 08/07/19 13:54 Parameter Units LCS Result % Rec Limits Qualifiers% RecConc. 3372501LABORATORY CONTROL SAMPLE: LCSSpike 1,1-Dichloroethene ug/m3 42.040.3 104 70-130 cis-1,2-Dichloroethene ug/m3 44.440.3 110 70-130 Tetrachloroethene ug/m3 74.168.9 107 70-130 Trichloroethene ug/m3 59.654.6 109 70-130 Vinyl chloride ug/m3 26.726 103 70-130 Parameter Units Dup Result QualifiersRPDResult 10485094001 3373369SAMPLE DUPLICATE: 1,1-Dichloroethene ug/m3 NDND cis-1,2-Dichloroethene ug/m3 NDND Tetrachloroethene ug/m3 NDND Trichloroethene ug/m3 NDND Vinyl chloride ug/m3 NDND REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 08/13/2019 04:39 PM Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 9 of 12 #=QL# QUALIFIERS Pace Project No.: Project: 92439578 Automotive Group DEFINITIONS DF - Dilution Factor, if reported, represents the factor applied to the reported data due to dilution of the sample aliquot. ND - Not Detected at or above adjusted reporting limit. TNTC - Too Numerous To Count J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. MDL - Adjusted Method Detection Limit. PQL - Practical Quantitation Limit. RL - Reporting Limit - The lowest concentration value that meets project requirements for quantitative data with known precision and bias for a specific analyte in a specific matrix. S - Surrogate 1,2-Diphenylhydrazine decomposes to and cannot be separated from Azobenzene using Method 8270. The result for each analyte is a combined concentration. Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values. LCS(D) - Laboratory Control Sample (Duplicate) MS(D) - Matrix Spike (Duplicate) DUP - Sample Duplicate RPD - Relative Percent Difference NC - Not Calculable. SG - Silica Gel - Clean-Up U - Indicates the compound was analyzed for, but not detected. Acid preservation may not be appropriate for 2 Chloroethylvinyl ether. A separate vial preserved to a pH of 4-5 is recommended in SW846 Chapter 4 for the analysis of Acrolein and Acrylonitrile by EPA Method 8260. N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for each analyte is a combined concentration. Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes. TNI - The NELAC Institute. LABORATORIES Pace Analytical Services - MinneapolisPASI-M REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 08/13/2019 04:39 PM Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 10 of 12 #=CR# QUALITY CONTROL DATA CROSS REFERENCE TABLE Pace Project No.: Project: 92439578 Automotive Group Lab ID Sample ID QC Batch Method QC Batch Analytical Method Analytical Batch 92439578001 624902IA-9C TO-15 92439578002 624902IA-9D TO-15 92439578003 624902IA-10A TO-15 92439578004 624902BG-6 TO-15 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 08/13/2019 04:39 PM Pace Analytical Services, LLC 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 11 of 12 Page 12 of 12