comprehensive site investigation and remediation objectives report

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maximum of two hours. The containerized sample were carefully poured and transferred from the original jar into clean laboratory grade plastic jars containing appropriate preservatives. Care was taken to not introduce settled sediment when transferring collected samples. Bailers, ropes, plastic tubing, and all other field measurement and sampling equipment were decontaminated prior to inserting them into each well, as described in Section 3.3. Groundwater grab samples were collected from the wells by either using a dedicated, bottomfilling disposable polyethylene bailer or polyethylene tubing and a peristaltic pump. For both sampling methods, special care was taken to avoid physically altering or chemically contaminating the samples. Groundwater samples were collected in appropriate laboratory supplied containers, preservative added depending on the analysis, then placed on ice to cool to 4°C, packed and hand delivered or picked up by State of Illinois Laboratory, Springfield, Illinois or First Environmental Laboratories (First) in Naperville, Illinois for analysis. All containers were furnished by the analytical laboratory and pre-cleaned according to US EPA protocols. Field quality assurance/quality control (QA/QC) samples (trip blanks and field duplicates) were collected at the frequency specified in V3’s Sampling and Analysis Plan or as otherwise specified. Required chain-of-custody procedures were maintained from the time of sample collection until delivery to the analytical laboratory. 3.8 LABORATORY METHODOLOGIES Laboratory services were performed by State of Illinois Laboratory, Springfield, Illinois and First Environmental of Naperville, Illinois (First). All of the laboratories are accredited by the Illinois Environmental Laboratory Accreditation Program (IL ELAP), a copy of the accreditation status and certification that all analyses were performed in accordance with the requirements of 35 Ill. Adm. Code 186 is provided in Appendix E.1. Soil and groundwater samples were analyzed for one or more of the following: VOCs, SVOCs, pesticides, PCBs, pH, total analyte list (TAL) metals, RCRA metals, fractional organic carbon (FOC) and total cyanide. Analytical methods used are listed below: Parameter Method Number Total Solids 2540B VOCs, BTEX 5035A/8260B SVOCs/PNAs 8270C Pesticides/PCBs 8081A/8082 pH 4500H+B/9045C Total Metals 6010B Total Mercury 7470A FOC D2974-87C Standard chain-of-custody procedures were followed to ensure adequate documentation accompanied all samples submitted to the laboratory. Upon arrival at the laboratory, the sample cooler was accepted by the Laboratory Sample Custodian who signed and dated the chain-ofcustody record. Complete analytical data reports and copies of the chain-of-custody forms are provided in Appendix E.2. Comprehensive Site Investigation Report V3 Companies, 17 Spartans’ Square Shopping Center May 2010
Summary results of analyses are presented in Table 1.1. Data comparison to appropriate remediation objectives are detailed in Tables 2.1 to 2.5 and Tables 3.1 to 3.2. Comprehensive Site Investigation Report V3 Companies, 18 Spartans’ Square Shopping Center May 2010
Page 1 and 2: ILLINOIS SITE REMEDIATION PROGRAM C
Page 3 and 4: TABLE OF CONTENTS EXECUTIVE SUMMARY
Page 5 and 6: APPENDICES Appendix A Historical Do
Page 7 and 8: The far northeast Former Clark Stat
Page 9 and 10: ‣ Tier 2 soil component of the Cl
Page 11 and 12: Section 4 - Documentation of Field
Page 13 and 14: Physical Setting Sources: • Berg,
Page 15 and 16: The Will Silty Clay Loam is a poorl
Page 17 and 18: Groundwater Classification: The sat
Page 19 and 20: y Dalhart Avenue to the west, Norma
Page 21 and 22: The soil gas samples were submitted
Page 23 and 24: 3.3 INVESTIGATION MONITORING AND EQ
Page 25: casing volumes and allowed to recha
Page 29 and 30: 4.3 REC 1 - FORMER DRY CLEANING OPE
Page 31 and 32: 5.0 ENDANGERMENT ASSESSMENT The Sit
Page 33 and 34: 5.3 SITE RECOGNIZED ENVIRONMENTAL C
Page 35 and 36: • There is no evidence of hazardo
Page 37 and 38: As summarized in (Tables 1.1, 2.1 t
Page 39 and 40: ‣ The Village of Romeoville maint
Page 41 and 42: A Tier 1 RO evaluation of Site data
Page 43 and 44: FIIGURES
Page 45 and 46: ± Various Retail & Commercial Busi
Page 47 and 48: FIGgwcontour07292.dgn 5/14/2010 12:
Page 49 and 50: FIGRECs07292.dgn 5/16/2010 1:07:17
Page 51 and 52: FIGbor_exceed07292.dgn 5/19/2010 4:
Page 53 and 54: TABLES
Page 55 and 56: Table 1.1 Summary of Soil and Groun
Page 57 and 58: TABLE 2.1 - SOIL ANALYTICAL RESULTS
Page 63 and 64: Volatile Organic Compounds (Method
Page 65 and 66: TABLE 3.2 - GROUNDWATER ANALYTICAL
Page 67 and 68: Chemical Name and Soil Remediation
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February 13, 2008 Ms. Dawn Caldwell
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SIGNATURES OF ENVIRONMENTAL PROFESS
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LIST OF APPENDICES Appendix I Quali
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material risk of harm to public hea
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terms with Village of Romeoville. T
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The following published documents w
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An ALTA/ACSM Land Title Survey was
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Hydrogeology: Based on regional top
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The EDR database report identified
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One site was identified as part of
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Multiple historical sources were re
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Independence Boulevard followed by
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All tenants Mexican Restaurant Laun
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Parking lot, northeast of building
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8.0 FINDINGS, OPINIONS & CONCLUSION
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± Approximate Site Boundary V3 Com
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± Spartans' Square Shopping Center
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Ms. Dawn Caldwell Village of Romeov
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Ms. Dawn Caldwell Village of Romeov
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FIIGURES
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± Approximate Site Boundary Variou
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TABLES
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TABLE 2 - GROUNDWATER ANALYTICAL RE
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10173 V3 Boring Log Report Boring N
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CHAIN-OF-CUSTODY PROTOCOL Laborator
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DECONTAMINATION ACTIVITIES PROTOCOL
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• Depth at which saturated condit
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BEACON Report No. 2096 PASSIVE SOIL
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BEACON Report Number: 2096 Passive
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BEACON ENVIRONMENTAL SERVICES, INC.
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Table 1 Beacon Environmental Servic
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MW-9 Asphalt Parking Lot Sanitary S
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MW-9 Asphalt Parking Lot Sanitary S
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Attachments
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BEACON PSG SAMPLER DEPLOYMENT THROU
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Attachment 3 LABORATORY PROCEDURES
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APPENDIIX B WELL SURVEY DOCUMENTATI
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Well ID Well Description Status Dep
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minimum protection zones are regula
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Well Survey Correspondence Spatans'
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10233 V3 Boring Log Report Spartans
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APPENDIIX D PHOTOGRAPHIC DOCUMENTAT
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PHOTO 4 Date:11/18/2008 Installatio
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Prairie Analytical Systems, Inc. CL
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Prairie Analytical Systems, Inc. Da
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Prairie Analytical Systems, Inc. Qu
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CLIENT: Illinois Environmental Prot
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Illinois Environmental Protection A
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CHAIN-OF-CUSTODY PROTOCOL Laborator
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DECONTAMINATION ACTIVITIES PROTOCOL
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• Drilling method • Depth at wh
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to collect the soil sample from the
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TEMPORARY MONITORING WELL INSTALLAT
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Page 2 of 2 Purging will be perform
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comprehensive site investigation and remediation objectives report

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