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HomeMy WebLinkAbout20060_Townsend_Siler_City_GW Assessment Rpt_20170426 DUNCKLEE & DUNHAM 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 LICENSING OF GEOLOGISTS LICENSE C-261 NC DEQ REGISTERED ENVIRONMENTAL CONSULTANT NUMBER 00061 DD ENVIRONMENTAL GEOLOGISTS & ENGINEERS 511 KEISLER DRIVE – SUITE 102 CARY, NORTH CAROLINA 27518 OFFICE: (919) 858–9898 WWW.DUNCKLEEDUNHAM.COM VIA EMAIL TO: bsise@mountaire.com April 26, 2017 Ms. Beth B. Sise Mountaire Farms of Delaware, Inc. 29292 John J. Williams Hwy. Millsboro, Delaware 19966 Reference: Letter Report of Groundwater Assessment Brownfields Project No: 20060-16-019 Relax Inn and Rey de Gloria Pentecostal Church Siler City, North Carolina Dear Ms. Sise: As authorized by John Wren’s acceptance of our proposal in an email dated March 8, 2017, Duncklee & Dunham, P.C. (Duncklee & Dunham) is pleased to submit this letter report to Mountaire Farms Inc. (Mountaire) that summarizes the results of the groundwater assessment we conducted at the above- referenced site. This scope of work and report was requested by Ms. Sharon Eckard of the North Carolina Brownfields Program (NCBP) to evaluate the potential for volatile organic compound vapor intrusion as part of the ongoing brownfields agreement application process. As authorized by Mountaire, a copy of this report has been sent to Ms. Eckard. Background Information Duncklee & Dunham conducted a Phase I Environmental Site Assessment (Phase I) at the Rey de Gloria Pentecostal Church at 1314 East Eleventh Street (church) and the Relax Inn at 1240 East Eleventh Street (motel) in Siler City, Chatham County, North Carolina (Figure 1). We prepared a Phase I report dated January 23, 2017, and did not identify evidence of recognized environmental conditions in connection with the subject site except for the possible presence of contaminants in groundwater beneath the subject site. Due to the presence of petroleum constituents and chlorinated solvents in groundwater on surrounding properties, the North Carolina Brownfields Program requested a vapor intrusion risk assessment of the motel and church sites. Duncklee & Dunham conducted a groundwater assessment of these sites and compared our findings to the Ground Water Screening Level established by the North Carolina Department of Environmental Quality (NCDEQ) in the Non-Residential Vapor Intrusion Screening Concentrations dated October 2016. Letter Report of Groundwater Assessment Relax Inn and Rey de Gloria Pentecostal Church Siler City, North Carolina April 26, 2017 Page 2 of 4 DUNCKLEE & DUNHAM, P.C. DD Based on topographic observations, the church and motel sites are hydraulically downgradient of the Quick Way Mart, a gasoline station/convenience store on the list of leaking underground storage tanks (LUST list). The North Carolina Department of Environmental Quality (NCDEQ) closed the regulatory file for this LUST after a Notice of Residual Petroleum had been filed to document that petroleum contaminants in soil and groundwater remained at the site. Thus, the Quick Way Mart is a potential source of contaminants to the subject site. Field Activities Duncklee & Dunham completed applications for permits to construct two temporary monitoring wells on each of the church and motel properties. We submitted the applications for signatures to Mountaire, which signed and forwarded them to the landowners. Upon receipt of the signed applications, we submitted them to the Division of Water Resources (DWR) of NCDEQ, which issued a permit dated March 21, 2017. A copy of this permit is attached. We called North Carolina 811 to clear utilities at the site 72 hours prior to mobilization. Duncklee & Dunham mobilized to the site on March 22, 2017, with our drilling contractor, Troxler Geologic Services (Troxler). We marked the four locations for temporary monitoring wells planned for the church and motel sites, and Troxler used geophysical techniques to locate underground utilities in the vicinity of the wells. Troxler did not identify underground utilities near the well locations. Troxler used a Geoprobe™ to construct four temporary monitoring wells (TMWs) at the locations shown on Figure 2. Troxler encountered refusal at each location between 6 to 10 feet below land surface (bls) and switched to augers to advance the borings through the water table. Troxler constructed the wells using PVC with a diameter of one inch. The following table summarizes details of well construction: Well No. Location Depth of Probe/Boring (feet bls) Intervals of Riser/Well Screen (feet bls) TMW-10 Northeastern Corner (Church) 19 0-9/9-19 TMW-11 Southeastern Corner (Church) 20 0-10/10-20 TMW-12 Center of Parking Lot (Motel) 22 0-12/12-22 TMW-13 Southwestern Corner (Motel) 25 0-13/13-23 Letter Report of Groundwater Assessment Relax Inn and Rey de Gloria Pentecostal Church Siler City, North Carolina April 26, 2017 Page 3 of 4 DUNCKLEE & DUNHAM, P.C. DD In each probe hole, little to no groundwater recharged the well at the time of construction. We allowed the wells to recharge overnight and gauged the depth to water in each well the following day. Duncklee & Dunham measured 2 to 7 feet of water in wells TMW-11, -12, and -13 and observed TMW-10 to be dry on March 23, 2017. We developed the water-producing wells and allowed them to recharge overnight again before collecting the samples for testing. TMW-10 was still dry on March 24 and we sampled the three remaining wells with a peristaltic pump and tubing, discharged the groundwater sample from the tubing into laboratory-provided containers, labeled the containers, and placed the containers in a cooler with ice. We submitted the coolers under chain-of-custody to a courier for ESC Lab Sciences (ESC). The courier sent the coolers via overnight delivery to ESC’s laboratory in Mt. Juliet, Tennessee. Troxler returned to the site on March 24 and abandoned the temporary monitoring wells after we collected all groundwater samples. Troxler abandoned the wells with bentonite chips and grouted the surface of any probe holes constructed in asphalt. The well abandonment record is attached. Troxler sent a copy of this record to the DWR. Laboratory Test Results ESC tested the groundwater samples for volatile organic compounds (VOCs) according to EPA Method 8260B. ESC’s report is attached, and the laboratory test results are summarized on Table 1. ESC detected methyl tert-butyl ether and di-isopropyl ether, both used as an oxygenate additive for gasoline, in the samples collected from TMW-13 on the motel site and in the sample from TMW-11 on the church site. ESC detected 1,1-dichloroethene (1,1-DCE) in the sample from TMW-12 located on the motel site. Estimated concentrations of 1,3-dichlorobenzene in the sample from TMW-12 and acetone in samples from TMW-11 and TMW-13 were detected below the laboratory’s lowest calibration point. Discussion The concentrations of MTBE detected in samples from TMW-11 and -13 exceeded the North Carolina groundwater quality standard in Title 15A, Subchapter 2L, Section .0202 of the North Carolina Administrative Code (15A NCAC 2L .0202, the “2L standards”). The concentrations of di-isopropyl ether detected from these wells did not exceed the 2L standards. This result suggests a source for the MTBE and di-isopropyl ether may be the Quick Way Stop site. The Quick Way Stop site appears to have been properly assessed by the responsible party and the file subsequently closed by NC DEQ. The groundwater sample collected from TMW-12 exhibited 1,1-DCE at a concentration that did not exceed the 2L standard. The presence of trace levels of chlorinated solvents has been documented in other wells on adjacent properties. The exact source of the chlorinated compounds has not been established. Letter Report of Groundwater Assessment Relax Inn and Rey de Gloria Pentecostal Church Siler City, North Carolina April 26, 2017 Page 4 of 4 DUNCKLEE & DUNHAM, P.C. DD Conclusions and Recommendations The concentrations detected in groundwater samples from the wells on the church and motel sites did not exceed the Groundwater Screening Level for Non-residential Vapor Intrusion Concentrations. Based on this result, Duncklee & Dunham considers the risk of vapor intrusion to be within acceptable ranges for industrial uses. We appreciate the opportunity to provide our services to Mountaire. Please contact Joshua Hanks at (919) 858-9898 or by email at josh@dunckleedunham.com if you have any questions or require further assistance. Sincerely, Duncklee & Dunham, P.C. Joshua M. Hanks, G.I.T. David L. Duncklee, P.G. Project Geologist Senior Hydrogeologist Senior Peer Review: Richard A. Kolb, L.G. Senior Geologist ec: Sharon Eckard, NCBP Attachments: Well Construction Permit Figures 1-2 Table 1 Well Abandonment Record Laboratory Analytical Report P:\Mountaire\Siler City\BF-201691\201691a - Data Gap Assessments\Report\Church and Motel\GW Report-17189.doc Divider Page Figures S i t e 0 2 0 0 0 ' 4 0 0 0 ' N S c a l e : 1 " = 2 0 0 0 ' D a t e : J a n u a r y 2 0 1 7 P r o j e c t N u m b e r : 2 0 1 6 5 9 H R e l a x I n n a n d R e y D e C r i s t o P e n t e c o s t a l C h u r c h S i l e r C i t y , N o r t h C a r o l i n a S i t e T o p o g r a p h i c M a p D r a w n B y : m r w C h e c k e d B y : R e f e r e n c e s : P : \ M o u n t a i r e \ S i l e r C i t y - 2 0 1 6 5 9 \ 2 0 1 6 5 9 H R e l a x I n n a n d R e y d e G l o r i a P h a s e I \ C A D \ S i t e T o p o . d w g F i l e n a m e : 1 F i g u r e L a y e r s : S i z e : M a p C a r d ; S i l e r C i t y 1 9 8 0 8 . 5 " x 1 1 " 0 , 1 5 1 1 K e i s l e r D r i v e S u i t e 1 0 2 ( 9 1 9 ) 8 5 8 - 9 8 9 8 D C a r y , N o r t h C a r o l i n a 2 7 5 1 8 w w w . d u n c k l e e d u n h a m . c o m N C E n g . L i c e n s e N o . C - 3 5 5 9 N C G e o . L i c e n s e N o . C - 2 6 1 D U N C K L E E & D U N H A M E N V I R O N M E N T A L G E O L O G I S T S & E N G I N E E R S C o n t o u r I n t e r v a l = 1 0 f t E a s t E l e v e n t h S t r e e t E a s t T h i r d S t r e e t R e l a x I n n R e y D e G l o r i a P . C . 1 2 4 0 1 3 1 4 1 3 1 4 1 1 0 1 E x p r e s s C a r e Q u i c k W a y M a r t 1 3 2 2 FormerTownsend Plant F o r m e r W a r e h o u s e / M i l l 1 2 0 0 T T T T T M W - 1 3 T M W - 1 2 T M W - 1 1 T M W - 1 0 0 7 5 ' 1 5 0 ' Scale:1" = 75' D a t e : P r o j e c t N u m b e r : R e l a x I n n a n d R e y D e G l o r i a P e n t e c o s t a l C h u r c h S i l e r C i t y , N o r t h C a r o l i n a S i t e M a p Drawn By:mrw Checke d B y : R e f e r e n c e s : P : \ M o u n t a i r e \ S i l e r C i t y \ B F - 2 0 1 6 9 1 \ C A D \ P a r c e l s a n d R e s u l t s M a p . d w g 5 1 1 K e i s l e r D r i v e S u i t e 1 0 2 ( 9 1 9 ) 8 5 8 - 9 8 9 8 D F i l e n a m e : Figure L a y e r s : Size: C h a t h a m C o u n t y G I S , N C O n e M a p , F i e l d N o t e s C a r y , N o r t h C a r o l i n a 2 7 5 1 8 w w w . d u n c k l e e d u n h a m . c o m 2 N8.5" x 1 1 " N C E n g . L i c e n s e N o . C - 3 5 5 9 N C G e o . L i c e n s e N o . C - 2 6 1 0 , 1 , 3 , 4 , 5 , 9 D U N C K L E E & D U N H A M E N V I R O N M E N T A L G E O L O G I S T S & E N G I N E E R S 2 0 1 6 9 1 A p r i l 2 0 1 7 LegendBoundary of Subject SiteBoundary of Tax ParcelStreet Number Location of Temporary Well1240T Tables Groundwater Quality Standard Non-residential Groundwater Screening Level Value Q Value Q Value Q 6,000 19,000,000 15.5 J <10.0 10.6 J 200 NE <0.220 0.422 J <0.220 350 164 <0.398 22.5 <0.398 70 5,860 17.3 <0.320 3.95 20 19,700 878 <0.367 192 Notes: All results in µg/L Bold value exceeds Reported Detection Limit (RL) Bold and shaded value exceeds the North Carolina Groundwater Quality Standard as defined in 15A NCAC 2L .0202 Non-residential Groundwater Screening Levels as shown in Division of Waste Management Vapor Intrusion Screening Concentrations Table (Oct. 2016) NE - Screening Level not established Qualifiers: Q = Laboratory qualifier J = The identification of the analyte is acceptable; the reported value is an estimate TMW-12TMW-11 TMW-13 03/24/2017 Di-isopropyl ether Methyl Tert-Butyl Ether Table 1 Summary of Laboratory Test Results - Groundwater Relax Inn and Rey de Gloria Pentecostal Church Siler City, North Carolina Volatile Organic Compounds - EPA 8260B Parameter Sample Collection Date Sample ID Acetone 1,3-Dichlorobenzene 1,1-Dichloroethene P:\Mountaire\Siler City\BF-201691\201691a - Data Gap Assessments\Tables\Church and Motel VI Wells.xls Divider Page WELL ABANDONMENT RECORD This form can be used for single or multiple wells Form GW-30 North Carolina Department of Environment and Natural Resources – Division of Water Resources Revised August 2013 1. Well Contractor Information: Well Contractor Name (or well owner personally abandoning well on his/her property) NC Well Contractor Certification Number Company Name 2. Well Construction Permit #: List all applicable well permits (i.e. County, State, Variance, Injection, etc.) if known 3. Well use (check well use): Water Supply Well: □Agricultural □Municipal/Public □Geothermal (Heating/Cooling Supply) □Residential Water Supply (single) □Industrial/Commercial □Residential Water Supply (shared) □Irrigation Non-Water Supply Well: □Monitoring □Recovery Injection Well: □Aquifer Recharge □Groundwater Remediation □Aquifer Storage and Recovery □Salinity Barrier □Aquifer Test □Stormwater Drainage □Experimental Technology □Subsidence Control □Geothermal (Closed Loop) □Tracer □Geothermal (Heating/Cooling Return) □Other (explain under 7g) 4. Date well(s) abandoned: 5a. Well location: Facility/Owner Name Facility ID# (if applicable) Physical Address, City, and Zip County Parcel Identification No. (PIN) 5b. Latitude and longitude in degrees/minutes/seconds or decimal degrees: (if well field, one lat/long is sufficient) N W CONSTRUCTION DETAILS OF WELL(S) BEING ABANDONED Attach well construction record(s) if available. For multiple injection or non-water supply wells ONLY with the same construction/abandonment, you can submit one form. 6a. Well ID#: 6b. Total well depth: (ft.) 6c. Borehole diameter: (in.) 6d. Water level below ground surface: (ft.) 6e. Outer casing length (if known): (ft.) 6f. Inner casing/tubing length (if known): (ft.) 6g. Screen length (if known): (ft.) WELL ABANDONMENT DETAILS 7a. Number of wells being abandoned: For multiple injection or non-water supply wells ONLY with the same construction/abandonment, you can submit one form. 7b. Approximate volume of water remaining in well(s): (gal.) FOR WATER SUPPLY WELLS ONLY: 7c. Type of disinfectant used: 7d. Amount of disinfectant used: 7e. Sealing materials used (check all that apply): □ Neat Cement Grout □ Bentonite Chips or Pellets □ Sand Cement Grout □ Dry Clay □ Concrete Grout □ Drill Cuttings □ Specialty Grout □ Gravel □ Bentonite Slurry □ Other (explain under 7g) 7f. For each material selected above, provide amount of materials used: 7g. Provide a brief description of the abandonment procedure: 8. Certification: Signature of Certified Well Contractor or Well Owner Date By signing this form, I hereby certify that the well(s) was (were) abandoned in accordance with 15A NCAC 02C .0100 or 2C .0200 Well Construction Standards and that a copy of this record has been provided to the well owner. 9. Site diagram or additional well details: You may use the back of this page to provide additional well site details or well abandonment details. You may also attach additional pages if necessary. SUBMITTAL INSTRUCTIONS 10a. For All Wells: Submit this form within 30 days of completion of well abandonment to the following: Division of Water Resources, Information Processing Unit, 1617 Mail Service Center, Raleigh, NC 27699-1617 10b. For Injection Wells: In addition to sending the form to the address in 10a above, also submit one copy of this form within 30 days of completion of well abandonment to the following: Division of Water Resources, Underground Injection Control Program, 1636 Mail Service Center, Raleigh, NC 27699-1636 10c. For Water Supply & Injection Wells: In addition to sending the form to the address(es) above, also submit one copy of this form within 30 days of completion of well abandonment to the county health department of the county where abandoned. For Internal Use ONLY: Ben J. Troxler 2511 Troxler Geologic Services, Inc. 3-24-17 Mountaire Former Relax Inn 1240 E 11th St, Siler City, NC 27344 Chatham ! MW-(10-13) 19-23ft 4.25 16-19 9-13 NA 10ft 4 0.0 NA NA 4 temporary wells abandoned; all the same property.  MW10-MW13 4-4-2017 35.7311981 -79.448460 Divider Page ANALYTICAL REPORT March 30, 2017 Duncklee and Dunham Sample Delivery Group:L898610 Samples Received:03/28/2017 Project Number:201691 Description:Mountaire Siler City BF Site:SILER CITY, NC Report To:Josh Hanks PO Box 639 Cary, NC 27512 Entire Report Reviewed By: March 30, 2017 [Preliminary Report] Jimmy Hunt Technical Service Representative Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by ESC is performed per guidance provided in laboratory standard operating procedures: 060302, 060303, and 060304. 12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 www.esclabsciences.com March 30, 2017 Jimmy Hunt Technical Service Representative ONE LAB. NATIONWIDE.TABLE OF CONTENTS ¹Cp: Cover Page 1 ²Tc: Table of Contents 2 ³Ss: Sample Summary 3 ⁴Cn: Case Narrative 4 ⁵Sr: Sample Results 5 TMW-11 L898610-01 5 TMW-12 L898610-02 7 TMW-13 L898610-03 9 TRIP BLANK L898610-04 11 ⁶Qc: Quality Control Summary 13 Volatile Organic Compounds (GC/MS) by Method 8260B 13 ⁷Gl: Glossary of Terms 17 ⁸Al: Accreditations & Locations 18 ⁹Sc: Chain of Custody 19 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 2 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 2 of 20 ONE LAB. NATIONWIDE.SAMPLE SUMMARY Collected by Collected date/time Received date/time TMW-11 L898610-01 GW Brandon Wise 03/24/17 08:45 03/28/17 08:45 Method Batch Dilution Preparation Analysis Analyst date/time date/time Volatile Organic Compounds (GC/MS) by Method 8260B WG964135 1 03/30/17 15:15 03/30/17 15:15 ACG Volatile Organic Compounds (GC/MS) by Method 8260B WG964135 50 03/30/17 17:10 03/30/17 17:10 ACG Collected by Collected date/time Received date/time TMW-12 L898610-02 GW Brandon Wise 03/24/17 09:05 03/28/17 08:45 Method Batch Dilution Preparation Analysis Analyst date/time date/time Volatile Organic Compounds (GC/MS) by Method 8260B WG964135 1 03/30/17 15:38 03/30/17 15:38 ACG Collected by Collected date/time Received date/time TMW-13 L898610-03 GW Brandon Wise 03/24/17 09:30 03/28/17 08:45 Method Batch Dilution Preparation Analysis Analyst date/time date/time Volatile Organic Compounds (GC/MS) by Method 8260B WG964135 1 03/30/17 16:01 03/30/17 16:01 ACG Volatile Organic Compounds (GC/MS) by Method 8260B WG964135 10 03/30/17 17:33 03/30/17 17:33 ACG Collected by Collected date/time Received date/time TRIP BLANK L898610-04 GW Brandon Wise 03/24/17 00:00 03/28/17 08:45 Method Batch Dilution Preparation Analysis Analyst date/time date/time Volatile Organic Compounds (GC/MS) by Method 8260B WG964135 1 03/30/17 14:29 03/30/17 14:29 ACG 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 3 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 3 of 20 ONE LAB. NATIONWIDE.CASE NARRATIVE All MDL (LOD) and RDL (LOQ) values reported for environmental samples have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control are within established criteria except where addressed in this case narrative, a non-conformance form or properly qualified within the sample results. By my digital signature below, I affirm to the best of my knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the quality of the data have been identified by the laboratory, and no information or data have been knowingly withheld that would affect the quality of the data. [Preliminary Report] Jimmy Hunt Technical Service Representative Sample Handling and Receiving The analysis for 2-Chloroethyl Vinyl Ether was conducted from a chemically preserved container. ESC Sample ID Project Sample ID Method L898610-01 TMW-11 8260B L898610-02 TMW-12 8260B L898610-03 TMW-13 8260B L898610-04 TRIP BLANK 8260B 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 4 of 20 Jimmy Hunt Technical Service Representative ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 4 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 01 L898610 TMW-11 Collected date/time: 03/24/17 08:45 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time Acetone 15.5 J 10.0 50.0 1 03/30/2017 15:15 WG964135 Acrolein U J4 8.87 50.0 1 03/30/2017 15:15 WG964135 Acrylonitrile U 1.87 10.0 1 03/30/2017 15:15 WG964135 Benzene U 0.331 1.00 1 03/30/2017 15:15 WG964135 Bromobenzene U 0.352 1.00 1 03/30/2017 15:15 WG964135 Bromodichloromethane U 0.380 1.00 1 03/30/2017 15:15 WG964135 Bromoform U 0.469 1.00 1 03/30/2017 15:15 WG964135 Bromomethane U 0.866 5.00 1 03/30/2017 15:15 WG964135 n-Butylbenzene U 0.361 1.00 1 03/30/2017 15:15 WG964135 sec-Butylbenzene U 0.365 1.00 1 03/30/2017 15:15 WG964135 tert-Butylbenzene U 0.399 1.00 1 03/30/2017 15:15 WG964135 Carbon tetrachloride U 0.379 1.00 1 03/30/2017 15:15 WG964135 Chlorobenzene U 0.348 1.00 1 03/30/2017 15:15 WG964135 Chlorodibromomethane U 0.327 1.00 1 03/30/2017 15:15 WG964135 Chloroethane U 0.453 5.00 1 03/30/2017 15:15 WG964135 2-Chloroethyl vinyl ether U 3.01 50.0 1 03/30/2017 15:15 WG964135 Chloroform U 0.324 5.00 1 03/30/2017 15:15 WG964135 Chloromethane U 0.276 2.50 1 03/30/2017 15:15 WG964135 2-Chlorotoluene U 0.375 1.00 1 03/30/2017 15:15 WG964135 4-Chlorotoluene U 0.351 1.00 1 03/30/2017 15:15 WG964135 1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2017 15:15 WG964135 1,2-Dibromoethane U 0.381 1.00 1 03/30/2017 15:15 WG964135 Dibromomethane U 0.346 1.00 1 03/30/2017 15:15 WG964135 1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2017 15:15 WG964135 1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2017 15:15 WG964135 1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2017 15:15 WG964135 Dichlorodifluoromethane U 0.551 5.00 1 03/30/2017 15:15 WG964135 1,1-Dichloroethane U 0.259 1.00 1 03/30/2017 15:15 WG964135 1,2-Dichloroethane U 0.361 1.00 1 03/30/2017 15:15 WG964135 1,1-Dichloroethene U 0.398 1.00 1 03/30/2017 15:15 WG964135 cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2017 15:15 WG964135 trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2017 15:15 WG964135 1,2-Dichloropropane U 0.306 1.00 1 03/30/2017 15:15 WG964135 1,1-Dichloropropene U 0.352 1.00 1 03/30/2017 15:15 WG964135 1,3-Dichloropropane U 0.366 1.00 1 03/30/2017 15:15 WG964135 cis-1,3-Dichloropropene U 0.418 1.00 1 03/30/2017 15:15 WG964135 trans-1,3-Dichloropropene U 0.419 1.00 1 03/30/2017 15:15 WG964135 2,2-Dichloropropane U 0.321 1.00 1 03/30/2017 15:15 WG964135 Di-isopropyl ether 17.3 0.320 1.00 1 03/30/2017 15:15 WG964135 Ethylbenzene U 0.384 1.00 1 03/30/2017 15:15 WG964135 Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2017 15:15 WG964135 Isopropylbenzene U 0.326 1.00 1 03/30/2017 15:15 WG964135 p-Isopropyltoluene U 0.350 1.00 1 03/30/2017 15:15 WG964135 2-Butanone (MEK)U 3.93 10.0 1 03/30/2017 15:15 WG964135 Methylene Chloride U 1.00 5.00 1 03/30/2017 15:15 WG964135 4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2017 15:15 WG964135 Methyl tert-butyl ether 878 18.4 50.0 50 03/30/2017 17:10 WG964135 Naphthalene U 1.00 5.00 1 03/30/2017 15:15 WG964135 n-Propylbenzene U 0.349 1.00 1 03/30/2017 15:15 WG964135 Styrene U 0.307 1.00 1 03/30/2017 15:15 WG964135 1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2017 15:15 WG964135 1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2017 15:15 WG964135 1,1,2-Trichlorotrifluoroethane U 0.303 1.00 1 03/30/2017 15:15 WG964135 Tetrachloroethene U 0.372 1.00 1 03/30/2017 15:15 WG964135 Toluene U 0.412 1.00 1 03/30/2017 15:15 WG964135 1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2017 15:15 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 5 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 5 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 01 L898610 TMW-11 Collected date/time: 03/24/17 08:45 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time 1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2017 15:15 WG964135 1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2017 15:15 WG964135 1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2017 15:15 WG964135 Trichloroethene U 0.398 1.00 1 03/30/2017 15:15 WG964135 Trichlorofluoromethane U 1.20 5.00 1 03/30/2017 15:15 WG964135 1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2017 15:15 WG964135 1,2,4-Trimethylbenzene U 0.373 1.00 1 03/30/2017 15:15 WG964135 1,2,3-Trimethylbenzene U 0.321 1.00 1 03/30/2017 15:15 WG964135 1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2017 15:15 WG964135 Vinyl chloride U 0.259 1.00 1 03/30/2017 15:15 WG964135 Xylenes, Total U 1.06 3.00 1 03/30/2017 15:15 WG964135 (S) Toluene-d8 103 80.0-120 03/30/2017 17:10 WG964135 (S) Toluene-d8 103 80.0-120 03/30/2017 15:15 WG964135 (S) Dibromofluoromethane 105 76.0-123 03/30/2017 17:10 WG964135 (S) Dibromofluoromethane 105 76.0-123 03/30/2017 15:15 WG964135 (S) 4-Bromofluorobenzene 103 80.0-120 03/30/2017 17:10 WG964135 (S) 4-Bromofluorobenzene 104 80.0-120 03/30/2017 15:15 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 6 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 6 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 02 L898610 TMW-12 Collected date/time: 03/24/17 09:05 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time Acetone U 10.0 50.0 1 03/30/2017 15:38 WG964135 Acrolein U J4 8.87 50.0 1 03/30/2017 15:38 WG964135 Acrylonitrile U 1.87 10.0 1 03/30/2017 15:38 WG964135 Benzene U 0.331 1.00 1 03/30/2017 15:38 WG964135 Bromobenzene U 0.352 1.00 1 03/30/2017 15:38 WG964135 Bromodichloromethane U 0.380 1.00 1 03/30/2017 15:38 WG964135 Bromoform U 0.469 1.00 1 03/30/2017 15:38 WG964135 Bromomethane U 0.866 5.00 1 03/30/2017 15:38 WG964135 n-Butylbenzene U 0.361 1.00 1 03/30/2017 15:38 WG964135 sec-Butylbenzene U 0.365 1.00 1 03/30/2017 15:38 WG964135 tert-Butylbenzene U 0.399 1.00 1 03/30/2017 15:38 WG964135 Carbon tetrachloride U 0.379 1.00 1 03/30/2017 15:38 WG964135 Chlorobenzene U 0.348 1.00 1 03/30/2017 15:38 WG964135 Chlorodibromomethane U 0.327 1.00 1 03/30/2017 15:38 WG964135 Chloroethane U 0.453 5.00 1 03/30/2017 15:38 WG964135 2-Chloroethyl vinyl ether U 3.01 50.0 1 03/30/2017 15:38 WG964135 Chloroform U 0.324 5.00 1 03/30/2017 15:38 WG964135 Chloromethane U 0.276 2.50 1 03/30/2017 15:38 WG964135 2-Chlorotoluene U 0.375 1.00 1 03/30/2017 15:38 WG964135 4-Chlorotoluene U 0.351 1.00 1 03/30/2017 15:38 WG964135 1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2017 15:38 WG964135 1,2-Dibromoethane U 0.381 1.00 1 03/30/2017 15:38 WG964135 Dibromomethane U 0.346 1.00 1 03/30/2017 15:38 WG964135 1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2017 15:38 WG964135 1,3-Dichlorobenzene 0.422 J 0.220 1.00 1 03/30/2017 15:38 WG964135 1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2017 15:38 WG964135 Dichlorodifluoromethane U 0.551 5.00 1 03/30/2017 15:38 WG964135 1,1-Dichloroethane U 0.259 1.00 1 03/30/2017 15:38 WG964135 1,2-Dichloroethane U 0.361 1.00 1 03/30/2017 15:38 WG964135 1,1-Dichloroethene 22.5 0.398 1.00 1 03/30/2017 15:38 WG964135 cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2017 15:38 WG964135 trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2017 15:38 WG964135 1,2-Dichloropropane U 0.306 1.00 1 03/30/2017 15:38 WG964135 1,1-Dichloropropene U 0.352 1.00 1 03/30/2017 15:38 WG964135 1,3-Dichloropropane U 0.366 1.00 1 03/30/2017 15:38 WG964135 cis-1,3-Dichloropropene U 0.418 1.00 1 03/30/2017 15:38 WG964135 trans-1,3-Dichloropropene U 0.419 1.00 1 03/30/2017 15:38 WG964135 2,2-Dichloropropane U 0.321 1.00 1 03/30/2017 15:38 WG964135 Di-isopropyl ether U 0.320 1.00 1 03/30/2017 15:38 WG964135 Ethylbenzene U 0.384 1.00 1 03/30/2017 15:38 WG964135 Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2017 15:38 WG964135 Isopropylbenzene U 0.326 1.00 1 03/30/2017 15:38 WG964135 p-Isopropyltoluene U 0.350 1.00 1 03/30/2017 15:38 WG964135 2-Butanone (MEK)U 3.93 10.0 1 03/30/2017 15:38 WG964135 Methylene Chloride U 1.00 5.00 1 03/30/2017 15:38 WG964135 4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2017 15:38 WG964135 Methyl tert-butyl ether U 0.367 1.00 1 03/30/2017 15:38 WG964135 Naphthalene U 1.00 5.00 1 03/30/2017 15:38 WG964135 n-Propylbenzene U 0.349 1.00 1 03/30/2017 15:38 WG964135 Styrene U 0.307 1.00 1 03/30/2017 15:38 WG964135 1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2017 15:38 WG964135 1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2017 15:38 WG964135 1,1,2-Trichlorotrifluoroethane U 0.303 1.00 1 03/30/2017 15:38 WG964135 Tetrachloroethene U 0.372 1.00 1 03/30/2017 15:38 WG964135 Toluene U 0.412 1.00 1 03/30/2017 15:38 WG964135 1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2017 15:38 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 7 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 7 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 02 L898610 TMW-12 Collected date/time: 03/24/17 09:05 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time 1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2017 15:38 WG964135 1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2017 15:38 WG964135 1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2017 15:38 WG964135 Trichloroethene U 0.398 1.00 1 03/30/2017 15:38 WG964135 Trichlorofluoromethane U 1.20 5.00 1 03/30/2017 15:38 WG964135 1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2017 15:38 WG964135 1,2,4-Trimethylbenzene U 0.373 1.00 1 03/30/2017 15:38 WG964135 1,2,3-Trimethylbenzene U 0.321 1.00 1 03/30/2017 15:38 WG964135 1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2017 15:38 WG964135 Vinyl chloride U 0.259 1.00 1 03/30/2017 15:38 WG964135 Xylenes, Total U 1.06 3.00 1 03/30/2017 15:38 WG964135 (S) Toluene-d8 103 80.0-120 03/30/2017 15:38 WG964135 (S) Dibromofluoromethane 107 76.0-123 03/30/2017 15:38 WG964135 (S) 4-Bromofluorobenzene 103 80.0-120 03/30/2017 15:38 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 8 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 8 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 03 L898610 TMW-13 Collected date/time: 03/24/17 09:30 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time Acetone 10.6 J 10.0 50.0 1 03/30/2017 16:01 WG964135 Acrolein U J4 8.87 50.0 1 03/30/2017 16:01 WG964135 Acrylonitrile U 1.87 10.0 1 03/30/2017 16:01 WG964135 Benzene U 0.331 1.00 1 03/30/2017 16:01 WG964135 Bromobenzene U 0.352 1.00 1 03/30/2017 16:01 WG964135 Bromodichloromethane U 0.380 1.00 1 03/30/2017 16:01 WG964135 Bromoform U 0.469 1.00 1 03/30/2017 16:01 WG964135 Bromomethane U 0.866 5.00 1 03/30/2017 16:01 WG964135 n-Butylbenzene U 0.361 1.00 1 03/30/2017 16:01 WG964135 sec-Butylbenzene U 0.365 1.00 1 03/30/2017 16:01 WG964135 tert-Butylbenzene U 0.399 1.00 1 03/30/2017 16:01 WG964135 Carbon tetrachloride U 0.379 1.00 1 03/30/2017 16:01 WG964135 Chlorobenzene U 0.348 1.00 1 03/30/2017 16:01 WG964135 Chlorodibromomethane U 0.327 1.00 1 03/30/2017 16:01 WG964135 Chloroethane U 0.453 5.00 1 03/30/2017 16:01 WG964135 2-Chloroethyl vinyl ether U 3.01 50.0 1 03/30/2017 16:01 WG964135 Chloroform U 0.324 5.00 1 03/30/2017 16:01 WG964135 Chloromethane U 0.276 2.50 1 03/30/2017 16:01 WG964135 2-Chlorotoluene U 0.375 1.00 1 03/30/2017 16:01 WG964135 4-Chlorotoluene U 0.351 1.00 1 03/30/2017 16:01 WG964135 1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2017 16:01 WG964135 1,2-Dibromoethane U 0.381 1.00 1 03/30/2017 16:01 WG964135 Dibromomethane U 0.346 1.00 1 03/30/2017 16:01 WG964135 1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2017 16:01 WG964135 1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2017 16:01 WG964135 1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2017 16:01 WG964135 Dichlorodifluoromethane U 0.551 5.00 1 03/30/2017 16:01 WG964135 1,1-Dichloroethane U 0.259 1.00 1 03/30/2017 16:01 WG964135 1,2-Dichloroethane U 0.361 1.00 1 03/30/2017 16:01 WG964135 1,1-Dichloroethene U 0.398 1.00 1 03/30/2017 16:01 WG964135 cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2017 16:01 WG964135 trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2017 16:01 WG964135 1,2-Dichloropropane U 0.306 1.00 1 03/30/2017 16:01 WG964135 1,1-Dichloropropene U 0.352 1.00 1 03/30/2017 16:01 WG964135 1,3-Dichloropropane U 0.366 1.00 1 03/30/2017 16:01 WG964135 cis-1,3-Dichloropropene U 0.418 1.00 1 03/30/2017 16:01 WG964135 trans-1,3-Dichloropropene U 0.419 1.00 1 03/30/2017 16:01 WG964135 2,2-Dichloropropane U 0.321 1.00 1 03/30/2017 16:01 WG964135 Di-isopropyl ether 3.95 0.320 1.00 1 03/30/2017 16:01 WG964135 Ethylbenzene U 0.384 1.00 1 03/30/2017 16:01 WG964135 Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2017 16:01 WG964135 Isopropylbenzene U 0.326 1.00 1 03/30/2017 16:01 WG964135 p-Isopropyltoluene U 0.350 1.00 1 03/30/2017 16:01 WG964135 2-Butanone (MEK)U 3.93 10.0 1 03/30/2017 16:01 WG964135 Methylene Chloride U 1.00 5.00 1 03/30/2017 16:01 WG964135 4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2017 16:01 WG964135 Methyl tert-butyl ether 192 3.67 10.0 10 03/30/2017 17:33 WG964135 Naphthalene U 1.00 5.00 1 03/30/2017 16:01 WG964135 n-Propylbenzene U 0.349 1.00 1 03/30/2017 16:01 WG964135 Styrene U 0.307 1.00 1 03/30/2017 16:01 WG964135 1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2017 16:01 WG964135 1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2017 16:01 WG964135 1,1,2-Trichlorotrifluoroethane U 0.303 1.00 1 03/30/2017 16:01 WG964135 Tetrachloroethene U 0.372 1.00 1 03/30/2017 16:01 WG964135 Toluene U 0.412 1.00 1 03/30/2017 16:01 WG964135 1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2017 16:01 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 9 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 9 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 03 L898610 TMW-13 Collected date/time: 03/24/17 09:30 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time 1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2017 16:01 WG964135 1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2017 16:01 WG964135 1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2017 16:01 WG964135 Trichloroethene U 0.398 1.00 1 03/30/2017 16:01 WG964135 Trichlorofluoromethane U 1.20 5.00 1 03/30/2017 16:01 WG964135 1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2017 16:01 WG964135 1,2,4-Trimethylbenzene U 0.373 1.00 1 03/30/2017 16:01 WG964135 1,2,3-Trimethylbenzene U 0.321 1.00 1 03/30/2017 16:01 WG964135 1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2017 16:01 WG964135 Vinyl chloride U 0.259 1.00 1 03/30/2017 16:01 WG964135 Xylenes, Total U 1.06 3.00 1 03/30/2017 16:01 WG964135 (S) Toluene-d8 103 80.0-120 03/30/2017 16:01 WG964135 (S) Toluene-d8 103 80.0-120 03/30/2017 17:33 WG964135 (S) Dibromofluoromethane 104 76.0-123 03/30/2017 16:01 WG964135 (S) Dibromofluoromethane 105 76.0-123 03/30/2017 17:33 WG964135 (S) 4-Bromofluorobenzene 104 80.0-120 03/30/2017 17:33 WG964135 (S) 4-Bromofluorobenzene 104 80.0-120 03/30/2017 16:01 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 10 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 10 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 04 L898610 TRIP BLANK Collected date/time: 03/24/17 00:00 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time Acetone U 10.0 50.0 1 03/30/2017 14:29 WG964135 Acrolein U J4 8.87 50.0 1 03/30/2017 14:29 WG964135 Acrylonitrile U 1.87 10.0 1 03/30/2017 14:29 WG964135 Benzene U 0.331 1.00 1 03/30/2017 14:29 WG964135 Bromobenzene U 0.352 1.00 1 03/30/2017 14:29 WG964135 Bromodichloromethane U 0.380 1.00 1 03/30/2017 14:29 WG964135 Bromoform U 0.469 1.00 1 03/30/2017 14:29 WG964135 Bromomethane U 0.866 5.00 1 03/30/2017 14:29 WG964135 n-Butylbenzene U 0.361 1.00 1 03/30/2017 14:29 WG964135 sec-Butylbenzene U 0.365 1.00 1 03/30/2017 14:29 WG964135 tert-Butylbenzene U 0.399 1.00 1 03/30/2017 14:29 WG964135 Carbon tetrachloride U 0.379 1.00 1 03/30/2017 14:29 WG964135 Chlorobenzene U 0.348 1.00 1 03/30/2017 14:29 WG964135 Chlorodibromomethane U 0.327 1.00 1 03/30/2017 14:29 WG964135 Chloroethane U 0.453 5.00 1 03/30/2017 14:29 WG964135 2-Chloroethyl vinyl ether U 3.01 50.0 1 03/30/2017 14:29 WG964135 Chloroform U 0.324 5.00 1 03/30/2017 14:29 WG964135 Chloromethane U 0.276 2.50 1 03/30/2017 14:29 WG964135 2-Chlorotoluene U 0.375 1.00 1 03/30/2017 14:29 WG964135 4-Chlorotoluene U 0.351 1.00 1 03/30/2017 14:29 WG964135 1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2017 14:29 WG964135 1,2-Dibromoethane U 0.381 1.00 1 03/30/2017 14:29 WG964135 Dibromomethane U 0.346 1.00 1 03/30/2017 14:29 WG964135 1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2017 14:29 WG964135 1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2017 14:29 WG964135 1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2017 14:29 WG964135 Dichlorodifluoromethane U 0.551 5.00 1 03/30/2017 14:29 WG964135 1,1-Dichloroethane U 0.259 1.00 1 03/30/2017 14:29 WG964135 1,2-Dichloroethane U 0.361 1.00 1 03/30/2017 14:29 WG964135 1,1-Dichloroethene U 0.398 1.00 1 03/30/2017 14:29 WG964135 cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2017 14:29 WG964135 trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2017 14:29 WG964135 1,2-Dichloropropane U 0.306 1.00 1 03/30/2017 14:29 WG964135 1,1-Dichloropropene U 0.352 1.00 1 03/30/2017 14:29 WG964135 1,3-Dichloropropane U 0.366 1.00 1 03/30/2017 14:29 WG964135 cis-1,3-Dichloropropene U 0.418 1.00 1 03/30/2017 14:29 WG964135 trans-1,3-Dichloropropene U 0.419 1.00 1 03/30/2017 14:29 WG964135 2,2-Dichloropropane U 0.321 1.00 1 03/30/2017 14:29 WG964135 Di-isopropyl ether U 0.320 1.00 1 03/30/2017 14:29 WG964135 Ethylbenzene U 0.384 1.00 1 03/30/2017 14:29 WG964135 Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2017 14:29 WG964135 Isopropylbenzene U 0.326 1.00 1 03/30/2017 14:29 WG964135 p-Isopropyltoluene U 0.350 1.00 1 03/30/2017 14:29 WG964135 2-Butanone (MEK)U 3.93 10.0 1 03/30/2017 14:29 WG964135 Methylene Chloride U 1.00 5.00 1 03/30/2017 14:29 WG964135 4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2017 14:29 WG964135 Methyl tert-butyl ether U 0.367 1.00 1 03/30/2017 14:29 WG964135 Naphthalene U 1.00 5.00 1 03/30/2017 14:29 WG964135 n-Propylbenzene U 0.349 1.00 1 03/30/2017 14:29 WG964135 Styrene U 0.307 1.00 1 03/30/2017 14:29 WG964135 1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2017 14:29 WG964135 1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2017 14:29 WG964135 1,1,2-Trichlorotrifluoroethane U 0.303 1.00 1 03/30/2017 14:29 WG964135 Tetrachloroethene U 0.372 1.00 1 03/30/2017 14:29 WG964135 Toluene U 0.412 1.00 1 03/30/2017 14:29 WG964135 1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2017 14:29 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 11 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 11 of 20 ONE LAB. NATIONWIDE.SAMPLE RESULTS - 04 L898610 TRIP BLANK Collected date/time: 03/24/17 00:00 Volatile Organic Compounds (GC/MS) by Method 8260B Result Qualifier MDL RDL Dilution Analysis Batch Analyte ug/l ug/l ug/l date / time 1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2017 14:29 WG964135 1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2017 14:29 WG964135 1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2017 14:29 WG964135 Trichloroethene U 0.398 1.00 1 03/30/2017 14:29 WG964135 Trichlorofluoromethane U 1.20 5.00 1 03/30/2017 14:29 WG964135 1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2017 14:29 WG964135 1,2,4-Trimethylbenzene U 0.373 1.00 1 03/30/2017 14:29 WG964135 1,2,3-Trimethylbenzene U 0.321 1.00 1 03/30/2017 14:29 WG964135 1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2017 14:29 WG964135 Vinyl chloride U 0.259 1.00 1 03/30/2017 14:29 WG964135 Xylenes, Total U 1.06 3.00 1 03/30/2017 14:29 WG964135 (S) Toluene-d8 103 80.0-120 03/30/2017 14:29 WG964135 (S) Dibromofluoromethane 105 76.0-123 03/30/2017 14:29 WG964135 (S) 4-Bromofluorobenzene 103 80.0-120 03/30/2017 14:29 WG964135 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 12 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 12 of 20 ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG964135 Volatile Organic Compounds (GC/MS) by Method 8260B L898610-01,02,03,04 Method Blank (MB) (MB) R3207140-3 03/30/17 14:00 MB Result MB Qualifier MB MDL MB RDL Analyte ug/l ug/l ug/l Acetone U 10.0 50.0 Acrolein U 8.87 50.0 Acrylonitrile U 1.87 10.0 Benzene U 0.331 1.00 Bromobenzene U 0.352 1.00 Bromodichloromethane U 0.380 1.00 Bromoform U 0.469 1.00 Bromomethane U 0.866 5.00 n-Butylbenzene U 0.361 1.00 sec-Butylbenzene U 0.365 1.00 tert-Butylbenzene U 0.399 1.00 Carbon tetrachloride U 0.379 1.00 Chlorobenzene U 0.348 1.00 Chlorodibromomethane U 0.327 1.00 Chloroethane U 0.453 5.00 2-Chloroethyl vinyl ether U 3.01 50.0 Chloroform U 0.324 5.00 Chloromethane U 0.276 2.50 2-Chlorotoluene U 0.375 1.00 4-Chlorotoluene U 0.351 1.00 1,2-Dibromo-3-Chloropropane U 1.33 5.00 1,2-Dibromoethane U 0.381 1.00 Dibromomethane U 0.346 1.00 1,2-Dichlorobenzene U 0.349 1.00 1,3-Dichlorobenzene U 0.220 1.00 1,4-Dichlorobenzene U 0.274 1.00 Dichlorodifluoromethane U 0.551 5.00 1,1-Dichloroethane U 0.259 1.00 1,2-Dichloroethane U 0.361 1.00 1,1-Dichloroethene U 0.398 1.00 cis-1,2-Dichloroethene U 0.260 1.00 trans-1,2-Dichloroethene U 0.396 1.00 1,2-Dichloropropane U 0.306 1.00 1,1-Dichloropropene U 0.352 1.00 1,3-Dichloropropane U 0.366 1.00 cis-1,3-Dichloropropene U 0.418 1.00 trans-1,3-Dichloropropene U 0.419 1.00 2,2-Dichloropropane U 0.321 1.00 Di-isopropyl ether U 0.320 1.00 Ethylbenzene U 0.384 1.00 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 13 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 13 of 20 ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG964135 Volatile Organic Compounds (GC/MS) by Method 8260B L898610-01,02,03,04 Method Blank (MB) (MB) R3207140-3 03/30/17 14:00 MB Result MB Qualifier MB MDL MB RDL Analyte ug/l ug/l ug/l Hexachloro-1,3-butadiene U 0.256 1.00 Isopropylbenzene U 0.326 1.00 p-Isopropyltoluene U 0.350 1.00 2-Butanone (MEK)U 3.93 10.0 Methylene Chloride U 1.00 5.00 4-Methyl-2-pentanone (MIBK)U 2.14 10.0 Methyl tert-butyl ether U 0.367 1.00 Naphthalene U 1.00 5.00 n-Propylbenzene U 0.349 1.00 Styrene U 0.307 1.00 1,1,1,2-Tetrachloroethane U 0.385 1.00 1,1,2,2-Tetrachloroethane U 0.130 1.00 Tetrachloroethene U 0.372 1.00 Toluene U 0.412 1.00 1,1,2-Trichlorotrifluoroethane U 0.303 1.00 1,2,3-Trichlorobenzene U 0.230 1.00 1,2,4-Trichlorobenzene U 0.355 1.00 1,1,1-Trichloroethane U 0.319 1.00 1,1,2-Trichloroethane U 0.383 1.00 Trichloroethene U 0.398 1.00 Trichlorofluoromethane U 1.20 5.00 1,2,3-Trichloropropane U 0.807 2.50 1,2,3-Trimethylbenzene U 0.321 1.00 1,2,4-Trimethylbenzene U 0.373 1.00 1,3,5-Trimethylbenzene U 0.387 1.00 Vinyl chloride U 0.259 1.00 Xylenes, Total U 1.06 3.00 (S) Toluene-d8 103 80.0-120 (S) Dibromofluoromethane 105 76.0-123 (S) 4-Bromofluorobenzene 104 80.0-120 Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD) (LCS) R3207140-1 03/30/17 12:28 • (LCSD) R3207140-2 03/30/17 12:51 Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits Analyte ug/l ug/l ug/l %%%%% Acetone 125 118 117 94.6 93.2 10.0-160 1.41 23 Acrolein 125 551 538 440 430 10.0-160 E J4 E J4 2.31 20 Acrylonitrile 125 140 137 112 110 60.0-142 2.16 20 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 14 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 14 of 20 ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG964135 Volatile Organic Compounds (GC/MS) by Method 8260B L898610-01,02,03,04 Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD) (LCS) R3207140-1 03/30/17 12:28 • (LCSD) R3207140-2 03/30/17 12:51 Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits Analyte ug/l ug/l ug/l %%%%% Benzene 25.0 24.8 24.9 99.2 99.5 69.0-123 0.390 20 Bromobenzene 25.0 26.8 27.6 107 111 79.0-120 3.19 20 Bromodichloromethane 25.0 26.9 27.1 108 109 76.0-120 0.910 20 Bromoform 25.0 24.9 24.9 99.8 99.8 67.0-132 0.0300 20 Bromomethane 25.0 28.9 25.7 116 103 18.0-160 11.5 20 n-Butylbenzene 25.0 23.8 23.8 95.0 95.3 72.0-126 0.280 20 sec-Butylbenzene 25.0 23.5 24.1 94.0 96.4 74.0-121 2.58 20 tert-Butylbenzene 25.0 22.1 22.7 88.4 90.7 75.0-122 2.58 20 Carbon tetrachloride 25.0 24.6 24.4 98.3 97.7 63.0-122 0.610 20 Chlorobenzene 25.0 28.0 28.4 112 113 79.0-121 1.24 20 Chlorodibromomethane 25.0 27.7 28.2 111 113 75.0-125 1.98 20 Chloroethane 25.0 24.8 25.5 99.2 102 47.0-152 2.87 20 2-Chloroethyl vinyl ether 125 120 122 95.8 97.7 10.0-160 2.00 22 Chloroform 25.0 27.7 27.7 111 111 72.0-121 0.0900 20 Chloromethane 25.0 19.3 20.7 77.3 82.9 48.0-139 7.02 20 2-Chlorotoluene 25.0 27.1 28.0 109 112 74.0-122 2.95 20 4-Chlorotoluene 25.0 27.1 27.5 108 110 79.0-120 1.38 20 1,2-Dibromo-3-Chloropropane 25.0 26.2 25.8 105 103 64.0-127 1.60 20 1,2-Dibromoethane 25.0 28.1 28.6 112 115 77.0-123 1.94 20 Dibromomethane 25.0 24.0 24.4 96.0 97.8 78.0-120 1.82 20 1,2-Dichlorobenzene 25.0 28.1 28.8 112 115 80.0-120 2.22 20 1,3-Dichlorobenzene 25.0 27.3 27.6 109 110 72.0-123 1.03 20 1,4-Dichlorobenzene 25.0 27.7 27.7 111 111 77.0-120 0.120 20 Dichlorodifluoromethane 25.0 31.2 31.2 125 125 49.0-155 0.130 20 1,1-Dichloroethane 25.0 27.0 27.2 108 109 70.0-126 0.690 20 1,2-Dichloroethane 25.0 26.6 26.5 106 106 67.0-126 0.410 20 1,1-Dichloroethene 25.0 28.1 28.2 112 113 64.0-129 0.360 20 cis-1,2-Dichloroethene 25.0 27.8 28.2 111 113 73.0-120 1.68 20 trans-1,2-Dichloroethene 25.0 27.9 28.3 112 113 71.0-121 1.21 20 1,2-Dichloropropane 25.0 26.5 26.6 106 106 75.0-125 0.280 20 1,1-Dichloropropene 25.0 28.5 28.3 114 113 71.0-129 0.380 20 1,3-Dichloropropane 25.0 29.0 29.3 116 117 80.0-121 1.08 20 cis-1,3-Dichloropropene 25.0 27.3 27.8 109 111 79.0-123 1.57 20 trans-1,3-Dichloropropene 25.0 26.4 26.4 105 106 74.0-127 0.300 20 2,2-Dichloropropane 25.0 23.5 23.6 93.8 94.5 60.0-125 0.680 20 Di-isopropyl ether 25.0 24.5 24.4 97.9 97.7 59.0-133 0.250 20 Ethylbenzene 25.0 24.2 25.1 97.0 100 77.0-120 3.31 20 Hexachloro-1,3-butadiene 25.0 24.3 25.1 97.1 100 64.0-131 3.37 20 Isopropylbenzene 25.0 23.2 23.6 92.9 94.4 75.0-120 1.63 20 p-Isopropyltoluene 25.0 24.7 25.3 98.8 101 74.0-126 2.23 20 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 15 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 15 of 20 ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG964135 Volatile Organic Compounds (GC/MS) by Method 8260B L898610-01,02,03,04 Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD) (LCS) R3207140-1 03/30/17 12:28 • (LCSD) R3207140-2 03/30/17 12:51 Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits Analyte ug/l ug/l ug/l %%%%% 2-Butanone (MEK)125 142 139 114 111 37.0-158 2.47 20 Methylene Chloride 25.0 26.2 26.2 105 105 66.0-121 0.100 20 4-Methyl-2-pentanone (MIBK)125 152 149 121 119 59.0-143 1.63 20 Methyl tert-butyl ether 25.0 26.7 26.8 107 107 64.0-123 0.210 20 Naphthalene 25.0 24.1 23.8 96.4 95.1 62.0-128 1.41 20 n-Propylbenzene 25.0 23.9 24.6 95.4 98.5 79.0-120 3.20 20 Styrene 25.0 25.3 25.8 101 103 78.0-124 1.99 20 1,1,1,2-Tetrachloroethane 25.0 27.1 27.7 108 111 75.0-122 2.19 20 1,1,2,2-Tetrachloroethane 25.0 26.1 25.9 104 104 71.0-122 0.760 20 Tetrachloroethene 25.0 27.2 27.4 109 109 70.0-127 0.690 20 Toluene 25.0 25.1 25.2 100 101 77.0-120 0.690 20 1,1,2-Trichlorotrifluoroethane 25.0 27.8 27.8 111 111 61.0-136 0.000 20 1,2,3-Trichlorobenzene 25.0 26.0 26.0 104 104 61.0-133 0.110 20 1,2,4-Trichlorobenzene 25.0 26.5 26.8 106 107 69.0-129 1.34 20 1,1,1-Trichloroethane 25.0 27.7 28.1 111 113 68.0-122 1.53 20 1,1,2-Trichloroethane 25.0 28.7 28.9 115 115 78.0-120 0.620 20 Trichloroethene 25.0 28.2 28.2 113 113 78.0-120 0.0100 20 Trichlorofluoromethane 25.0 30.4 30.8 122 123 56.0-137 1.16 20 1,2,3-Trichloropropane 25.0 27.3 27.2 109 109 72.0-124 0.160 20 1,2,3-Trimethylbenzene 25.0 23.9 24.0 95.7 95.9 75.0-120 0.200 20 1,2,4-Trimethylbenzene 25.0 28.0 28.6 112 114 75.0-120 1.93 20 1,3,5-Trimethylbenzene 25.0 25.9 26.3 104 105 75.0-120 1.37 20 Vinyl chloride 25.0 27.8 28.0 111 112 64.0-133 0.730 20 Xylenes, Total 75.0 73.9 75.0 98.5 100 77.0-120 1.48 20 (S) Toluene-d8 101 103 80.0-120 (S) Dibromofluoromethane 106 107 76.0-123 (S) 4-Bromofluorobenzene 102 102 80.0-120 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 16 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 16 of 20 ONE LAB. NATIONWIDE.GLOSSARY OF TERMS Abbreviations and Definitions SDG Sample Delivery Group. MDL Method Detection Limit. RDL Reported Detection Limit. U Not detected at the Reporting Limit (or MDL where applicable). RPD Relative Percent Difference. (S)Surrogate (Surrogate Standard) - Analytes added to every blank, sample, Laboratory Control Sample/Duplicate and Matrix Spike/Duplicate; used to evaluate analytical efficiency by measuring recovery. Surrogates are not expected to be detected in all environmental media. Rec.Recovery. Qualifier Description E The analyte concentration exceeds the upper limit of the calibration range of the instrument established by the initial calibration (ICAL). J The identification of the analyte is acceptable; the reported value is an estimate. J4 The associated batch QC was outside the established quality control range for accuracy. 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 17 of 20 ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 17 of 20 ONE LAB. NATIONWIDE.ACCREDITATIONS & LOCATIONS 1 Cp 2Tc 3Ss 4Cn 5Sr 6Qc 7Gl 8Al 9Sc ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:07 18 of 20 Our Locations Alabama 40660 Alaska UST-080 Arizona AZ0612 Arkansas 88-0469 California 01157CA Colorado TN00003 Conneticut PH-0197 Florida E87487 Georgia NELAP Georgia 1 923 Idaho TN00003 Illinois 200008 Indiana C-TN-01 Iowa 364 Kansas E-10277 Kentucky 1 90010 Kentucky 2 16 Louisiana AI30792 Maine TN0002 Maryland 324 Massachusetts M-TN003 Michigan 9958 Minnesota 047-999-395 Mississippi TN00003 Missouri 340 Montana CERT0086 Nebraska NE-OS-15-05 Nevada TN-03-2002-34 New Hampshire 2975 New Jersey–NELAP TN002 New Mexico TN00003 New York 11742 North Carolina Env375 North Carolina 1 DW21704 North Carolina 2 41 North Dakota R-140 Ohio–VAP CL0069 Oklahoma 9915 Oregon TN200002 Pennsylvania 68-02979 Rhode Island 221 South Carolina 84004 South Dakota n/a Tennessee 1 4 2006 Texas T 104704245-07-TX Texas 5 LAB0152 A2LA – ISO 17025 1461.01 Canada 1461.01 EPA–Crypto TN00003 State Accreditations Third Party & Federal Accreditations ESC Lab Sciences is the only environmental laboratory accredited/certified to support your work nationwide from one location. One phone call, one point of contact, one laboratory. No other lab is as accessible or prepared to handle your needs throughout the country. Our capacity and capability from our single location laboratory is comparable to the collective totals of the network laboratories in our industry. The most significant benefit to our “one location” design is the design of our laboratory campus. The model is conducive to accelerated productivity, decreasing turn-around time, and preventing cross contamination, thus protecting sample integrity. Our focus on premium quality and prompt service allows us to be YOUR LAB OF CHOICE. ESC Lab Sciences has sixty-four client support centers that provide sample pickup and/or the delivery of sampling supplies. If you would like assistance from one of our support offices, please contact our main office. ESC Lab Sciences performs all testing at our central laboratory. 1. Drinking Water 2. Underground Storage Tanks 3. Aquatic Toxicity 4. Utah 6157585858 Vermont VT2006 Virginia 109 Washington C1915 West Virginia 233 Wisconsin 9980939910 Wyoming A2LA AIHA-LAP,LLC 100789 DOD 1461.01 USDA S-67674 Chemical/Microbiological 5. Mold n/a Accreditation not applicable 1461.02A2LA – ISO 170255 * Not all certifications held by the laboratory are applicable to the results reported in the attached report. ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE: Duncklee and Dunham 201691 L898610 03/30/17 18:15 18 of 20