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ARCHIVED REPORTS_XR0003214
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0541693
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ARCHIVED REPORTS_XR0003214
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Entry Properties
Last modified
2/6/2020 12:01:03 PM
Creation date
2/6/2020 11:07:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003214
RECORD_ID
PR0541693
PE
2960
FACILITY_ID
FA0023897
FACILITY_NAME
TOYOTA TOWN INC
STREET_NUMBER
610
Direction
N
STREET_NAME
HUNTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13906033
CURRENT_STATUS
01
SITE_LOCATION
610 N HUNTER ST
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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� v <br /> 0 <br /> 1 <br /> A S S O C I A T E S I N C <br /> The vapor extraction wells were constructed with 2-inch PVC casing to depths of approximately <br /> 25 feet bgs The screen interval in the vapor extraction wells was placed from 15 to 25 feet bgs <br /> ' The air sparge wells were constructed with 2-inch PVC casing to depths of approximately 40 feet <br /> bgs The screen interval in the vapor extraction wells was placed from 35 to 40 feet bgs <br /> Construction details are depicted on the well logs contained in Appendix A <br /> 1 4.4 <br /> Air Sparge Well Development <br /> Air sparge wells AS 1 and AS2 were developed on January 18, 2002 Each well was purged until <br /> the extracted water was relatively sediment free Development logs are included in Appendix C <br />' Purgewater was temporarily stored on site in DOT approved 55-gallon drums <br /> 4.5 Air Sparge Well Sampling and Analysis <br /> On January 18, 2002, oundwater samples were <br /> �' p collected from air sparge wells AS 1 and AS2 <br /> Prior to collecting groundwater samples, fluid levels were taken utilizing an electronic water probe <br /> 1 capable of measuring with an accuracy of 11100 of a foot Groundwater elevation data are <br /> presented in Table 2 The samples were collected after purging a mimmum of three well volumes <br /> and stabilization of electric conductivity, pH, and temperature Field purge logs are presented in <br /> Appendix C Subsequent to purging, groundwater was sampled and transferred to appropriate <br /> sample containers, using clean, disposable bailers with bottom emptying devices to reduce <br />' volatilization <br /> Groundwater samples were placed on ice and delivered under chain-of-custody documentation to <br /> Argon for chemical analysis Selected groundwater samples were analyzed for TPHg by EPA <br /> method 8015, BTEX by EPA method 8020, and MTBE, TAME, ETBE, DIPE, TBA, 1,2-DCA, <br /> and EDB by EPA method 8260 The analytical results for groundwater samples are summarized <br /> 1 in Table 2 Laboratory data sheets and chain-of-custody documentation are included in <br /> Appendix D <br /> 5.0 REMEDIATION SYSTEM INSTALLATION <br /> 5.1 Trenching and Piping Activities <br />' During the week of April 15 2002 ATC supervised the trenching P � p and plumbing activities to install <br /> the subsurface piping that directs extracted vapor from the wells to a nearby remediation compound <br />' and directs air generated by the blower to the air sparge wells <br />' Cal-West Concrete Cutting sawcut the asphalt/concrete surface of the site in the locations where the <br /> subsurface piping was going to be installed Land Technology Inc (LTI) removed the <br /> asphalt/concrete debris and excavated the trenches to the specifications contained in ATC's Interim <br /> Remediation Plan for the Farmer Property, 610 North Hunter Street, Stockton, California, dated <br /> October 24, 2001 The asphalt/concrete debris and excavated soil was transported under non- <br /> w lwordpro1625961reportsl1rp doc 4 <br />
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