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2900 - Site Mitigation Program
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PR0009016
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Last modified
6/17/2020 1:55:20 PM
Creation date
6/17/2020 11:34:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0009016
PE
2959
FACILITY_ID
FA0004032
FACILITY_NAME
AMERICAN MOULDING & MILLWORK (FRMR)
STREET_NUMBER
2801
STREET_NAME
WEST
STREET_TYPE
LN
City
STOCKTON
Zip
95204
APN
11709001
CURRENT_STATUS
01
SITE_LOCATION
2801 WEST LN
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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I <br /> Appendix A <br /> I <br /> loose fine soil particles on the surface. The sediment in the sample tube will th�n be placed into an <br /> appropriate sample container and transported and sealed following the protocols described for soil <br /> samples. Samples for VOC analyses will be collected by inserting an Encore''" sampler into the <br /> sediment. If the sediment is extremely coarse-grained(e.g.,large gravel) such that the clasts are larger <br /> than the diameter of the Encorem samplers,tubes of soil will be submitted in 1 eu of the Encor6l <br /> sampler, and recorded in the daily field logbook and the Chain of Custody. <br /> A1.2.5 Soil Vapor Sampling <br /> Soil vapor data will be collected at 20 locations throughout the site to determine the presence or absence <br /> of VOCs and formaldehyde. Soil vapor samples will be collected using guidelines from the advisory on <br /> active soil gas investigations prepared by the DTSC and Los Angeles RWQC (DTSC and LARWQCB, <br /> January 2003). The collection of soil vapor samples will require the installation of temporary vapor <br /> probes using a direct push drill rig. The following describes procedures fors ling soil vapor using soil <br /> vapor probes. <br /> A1.2.5.1 Temporary Probe Installation <br /> • Prior to use at each sampling location, drive rods and any other non-dedic ted,non-disposable <br /> equipment that may come into contact with the soil vapor sample will be decontaminated. <br /> • Each soil vapor probe will be driven to the target depth and then retracted by 4 to 6 inches to expose <br /> the screened sampling tip. <br /> • An approximate twelve to fifteen-foot length of disposable %4 to 1/8 inch diameter Tygon or Teflon <br /> sampling line will then be inserted into the vapor probe(drive rod)and connected to the screened <br /> sampling tip with a threaded connection containing a rubber gasket(post run tubing set-up). <br /> • Following installation of the sampling line,the annulus surrounding the p robe rod at ground surface <br /> will be sealed with hydrated bentonite. <br /> • To allow subsurface conditions to equilibrate,no further procedures shall be conducted for a <br /> minimum of 20 minutes following placement of the bentonite. <br /> A1.2.5.2 Pre-Sample Purge <br /> • While the subsurface is equilibrating,the"dead space volume"will be estimated by calculating the <br /> volume occupied by the sample tubing and sampling tip. This value will equal one purge volume. <br /> • The low flow pump, flow meter, and"T-valve"are then attached to the end of the sampling line. <br /> The"T-valve"is positioned before the pump and flow meter. <br /> • After 20 minutes and before starting the pre-sample purge, a rag moist d with the selected leak <br /> check compound(butane or isobutene analyzed by ASTM D1945)will a placed on the ground <br /> surface around the annulus of the soil vapor probe. At least once a day,it second moistened rag will <br /> also be placed near the sampling train to check for possible leaks in the t abing connections. <br /> • The"17-valve"will be rotated so that the sampling line is open to the pump. A total of three purge <br /> volumes of vapor will then be pumped from the sampling line at a flow rate of approximately 100 to <br /> KB61125 APPENDIX A MACTEC Engineering and Consulting, Inc. A5 <br /> September 28,2005 <br />
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