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constituent concentrations. Therefore, a follow-up sampling for indoor air will be tentatively scheduled for <br /> approximately six months after the initial indoor sampling is implemented. However, the frequency and <br /> timing of follow-up sampling may also be guided by the initial concentrations of VOCs detected in <br /> accordance with January 2016 DTSC Human Health and Ecological Risk Office, Human Health Risk <br /> Assessment Note Number 3 and August 23, 2014 DTSC Human Health and Ecological Risk Office, Human <br /> Health Risk Assessment Note Number 5 (discussed in Section 1.3). <br /> The air samples will be transported under a sample chain of custody to Eurofins/Air Toxics, in Folsom, <br /> California, a laboratory certified by the State of California for analysis of air samples. To protect sample <br /> integrity, soil gas samples to be analyzed will not be chilled. The samples will be analyzed by Modified <br /> Method TO-15 Selective Ion Mode (TO-15 SIM). <br /> 5.2.2 Proposed Sub-Slab Soil Gas Probe Installation Methods <br /> The proposed sub-slab soil gas assessment will be conducted in general accordance with the July 2015 <br /> DTSC document titled Advisory-Active Soil Gas Sampling (Advisory). The three proposed sub-slab soil gas <br /> sample locations within the interior of the Quality Cleaners as shown on Figure 6. One sample will be <br /> proximate to the floor drain in the boiler room and the location of the December 2014 sub-slab soil gas <br /> sample SG1, a second sample will be proximate to the dry cleaning machine and December 2014 sub-slab <br /> soil gas sample SG2, and a third sample will be within the southwestern portion of the dry cleaners suite <br /> and proximate to the inferred location of the sewer lateral. <br /> The soil gas probes will be completed with a four-inch diameter well vault. The permanent soil gas <br /> probes will allow for resampling as necessary. Eight-inch diameter cores will be removed from the <br /> concrete slab at the sample probe locations. The well vaults will be installed flush with the floor and <br /> secured with a redi-mix concrete. Eight inch diameter holes will allow for observation of the sub-slab <br /> material. <br /> Sub-slab soil gas probes consisting of sample tubing and a porous tip will be inserted to approximately <br /> four to six inches below the concrete floor. Flexible sampling tubing will be 1/4 -inch in diameter made of <br /> Teflon that will not react or interact with VOCs. Clean, dry, dedicated tubing will be used for sampling. No <br /> moisture, water, or any unknown material will be present in the probes prior to insertion. <br /> During installation of the probes, clean sand will be used to support the sample tip and a transition seal of <br /> dry granular bentonite will be placed between the sand pack and neat cement grout. To allow for the <br /> subsurface to equilibrate o representative conditions, each probe was not purged or sampled for at least <br /> two hours following probe installation. The sample probe will covered with a shroud (plastic tote or <br /> overturned 5-gallon plastic bucket) during the sampling process. <br /> The permanent soil gas probes will be secured and completed to prevent infiltration of water or ambient <br /> air into the subsurface and to prevent accidental damage or vandalism. The tubing will be marked at the <br /> surface to identify the probe location and depth. A gas-tight valve or fitting for capping will be affixed to <br /> the sampling tube. <br /> The sub-slab soil gas samples will be collected and analyzed by on-site mobile laboratory using gas-tight <br /> glass syringes which will allow the analytical results to be available within approximately 30 minutes after <br /> Sampling and Analysis Plan <br /> Tracy Corners Shopping Center <br /> 3225 North Tracy Boulevard <br /> Tracy,California 95376 <br /> Partner Project Number SM14-129814 <br /> Docket Number HAS-VCA 14/15-108 <br /> August 15,2016 <br /> Page 14 <br />