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2900 - Site Mitigation Program
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PR0542208
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Last modified
7/24/2019 4:35:47 PM
Creation date
7/24/2019 4:30:09 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0542208
PE
2960
FACILITY_ID
FA0024243
FACILITY_NAME
CALIFORNIA TANK LINES
STREET_NUMBER
3105
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
17512028
CURRENT_STATUS
01
SITE_LOCATION
3105 S EL DORADO ST
P_LOCATION
01
QC Status
Approved
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i <br /> I f <br /> Site Investigation Work Plan <br /> Nella Oil Station #21 , 40052 Highway 41 , Oakhurst, California <br /> 11 3.0 PROPOSED SCOPE OF WORK <br /> As directed in their January 12 , 2009 letter, the SJCEHD required that Caltanks conduct a soil <br /> vapor survey to investigate the potential for vapor intrusion into on-site buildings at the subject <br /> site . The following details the soil vapor survey scope of work: <br /> 5. 1 Project Planning <br /> WRM will obtain the required boring permits and work plan approval from the SJCEHD . <br /> Underground Service Alert ( USA) will be notified a minimum of 48 hours prior to the installation <br /> of the soil borings to locate any utilities in the vicinity of the planned boring locations. <br /> Prior to initiating fieldwork, a site-specific health and safety plan ( HASP) will be prepared . The <br /> HASP will include safety procedures for work to be performed , chemical hazard information , site <br /> safety officers , and a medical emergency location . The HASP will be kept on site at all times <br /> during the site investigation work. <br /> 5.2 Soil Vapor Survey <br /> To evaluate potential vapor concentrations throughout the site, WRM will collect eight (8) on- <br /> and off-site soil vapor samples in accordance with the California Regional Water Quality Control <br /> Board Los Angeles Region , Interim Guidance for Active Soil Gas Investigation dated February <br /> 25 , 1997 ; the California Department of Toxic Substances Control Advisory — Active Soil Gas <br /> Investigations dated January 28, 2003 ; and the California Department of Toxic Substances <br /> Control Interim Final Guidance for the Evaluation and Mitigation of Subsurface Vapor Intrusion <br /> to Indoor Air, dated December 14 , 2004 and revised February 7, 2005 . <br /> Soil vapor points will be constructed by advancing a 4-inch diameter Geoprobe® MacroCore® <br /> sampler to approximately 5-feet bgs. Following removal of the MacroCore®, Teflon tubing fitted <br /> with a porous media and inserted into a 1 -inch diameter PVC casing , will be lowered to the total <br /> borehole depth . Approximately 1 -foot of sand will be placed on top of the screen through the <br /> PVC casing and added as the casing is removed allowing the sand evenly distribute in the <br /> borehole . Approximately 1 -foot of dry bentonite pellets will be added on top of the sand through <br /> the PVC casing . The PVC casing will be removed from the borehole and additional bentonite <br /> will be added to approximately 3-inches bgs and slowly hydrated . After sampling the tubing will <br /> be removed and the top of the borehole filled and patched to match the surrounding surface . <br /> WRM will wait at least 30-minutes after well construction to allow for subsurface equilibrium . <br /> i <br /> For each soil vapor sample, the system will be purged of approximately three system volumes <br /> prior to sampling to ensure that a representative soil vapor sample is collected . Immediately <br /> prior to sampling , a tracer gas will be applied to the sampling tubing at ground level and to the <br /> fittings to check seal integrity. The tracer gas will be included in the analytical suite to verify soil <br /> vapor sample reliability. ;Each soil vapor sample will be collected in laboratory provided <br /> containers at a flow rate of 100 to 200 milliliters per minute. <br /> 6 <br />
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