Laserfiche WebLink
r � <br /> AEMA <br /> City of Stockton Fire Station #b <br /> Soil Remediation Plan <br /> Site Code 1013 <br /> June 24, 1992 <br /> Page 2 <br /> Excavation proceeded until site attributes including public and private thoroughfares prevented <br /> further enlargement of the pit. Subsequent to excavation, RESNA personnel collected 5 soil <br /> samples from the pit walls and one sample from the floor of the pit (Figure 2). <br /> Laboratory analysis of the samples indicated that petroleum hydrocarbon constituents are present <br /> in soils still in place on the south and east walls of the pit as well as the pit floor. Laboratory <br /> results of soil samples are summarized in Table 1. <br /> Due to safety considerations, the pit was subsequently backfilled with clean engineered material <br /> and compacted to grade. <br /> Soils removed during excavation were stockpiled on-site and aerated for a 5-month period under <br /> authorization of the San Joaquin County Air Pollution Control District (APCD). The soils were <br /> kept moist and were tilled several times during aeration to increase natural bacterial decay of <br /> diesel contaminants. The aerated soils were subsequently relocated to the City of Stockton <br /> Corporation yard with the authorization of the San Joaquin County Public Health Services <br /> Environmental Health Division (PHSIEHD) for use as roadbase material at various city paving <br /> projects. Laboratory results of the soil composite sample collected from the soil pile after <br /> aeration (02/14/91) is summarized in Table 1. <br /> Based on the laboratory results of confirmation samples collected during the re-excavation, <br /> further investigation of the extent of soil and possible groundwater contamination was required <br /> by the PHSIEHD in order to evaluate remedial action alternatives. <br /> On April 29, 1991, RESNA personnel advanced two soil borings (SBI and MWI) to respective <br /> depths of 36.5 and 38 feet below grade to determine the full extent of hydrocarbon impacted <br /> soils. Soil Boring MW1 was subsequently converted into a groundwater monitoring well. The <br /> soil boring and monitoring well were located as close as possible to the area of suspected soil <br /> contamination. The location of the two borings are exhibited on Figure 2. <br /> The laboratory analysis of soil samples collected at 10.5 and 25.5 feet below grade in Boring <br /> MW1 and also at 20.5 and 25.5 below grade in Boring SB1 did not detect the presence of diesel <br /> constituents above the method detection limit. The laboratory test results are summarized in <br /> Table 1. <br /> The depth to first groundwater beneath the site was recorded at approximately 28 feet below <br /> grade. Analysis of groundwater collected subsequent to the development of MW 1 indicated <br /> SFSb92.TJL <br />