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2900 - Site Mitigation Program
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PR0506460
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/14/2020 1:07:30 PM
Creation date
5/14/2020 12:32:12 PM
Metadata
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0506460
PE
2950
FACILITY_ID
FA0007440
FACILITY_NAME
ATHERTON KIRK/SPRECKELS
STREET_NUMBER
18800
STREET_NAME
SPRECKELS
STREET_TYPE
RD
City
MANTECA
Zip
95336
CURRENT_STATUS
01
SITE_LOCATION
18800 SPRECKELS RD
P_LOCATION
04
QC Status
Approved
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KLEINFELDER <br /> File No. 20-3978-01.W10 <br /> July 26, 1997 <br /> 3. Additionally, Kleinfelder recommends that all State of California Department of <br /> Conservation Division of Oil and Gas guidance documents and regulations for development <br /> in former well/pit locations be carefully followed. <br /> 4.9 Potential Landfill Locations (File No. 20-3978-O1.WR9) <br /> Based on the results of the subsurface assessment conducted in this area, Kleinfelder had the <br /> following conclusions detailed in our report "Investigation of Suspected Landfill Locations, <br /> (Phase I ESA Recommendation No. 11), Former Spreckels Sugar Plant, Manteca, California" <br /> dated February 24, 1997: <br /> 1. Investigation of seven suspected landfill locations revealed two disposal areas, one <br /> containing a lime waste (Site B disposal area), and the second containing construction debris <br /> (Site C disposal area). Site B disposal area is approximately 11,000 square feet in area and <br /> contains an estimated 2,800 cubic yards of debris mixed with soil and lime. Site C disposal <br /> area has a surface area of approximately 26,000 square feet and contain as estimated 8,600 <br /> cubic yard of debris. <br /> 2. Soil samples collected beneath the Site C disposal area did not show evidence of <br /> contamination. Groundwater samples revealed possible elevation of inorganic constituents <br /> downgradient of both disposal areas although the degree of elevation was not exceptionally <br /> high. Several volatile organic constituents were detected in MW-CDOI downgradient of Site <br /> C disposal area although these results are not definitive as there are other possible sources. <br /> Methane gas was detected at both disposal areas in low concentrations. The highest <br /> concentration was found in the Site C disposal area but that concentration was still below the <br /> lower explosive limit for methane. Varying amounts of near surface debris was found in <br /> other areas (Site A, Site D, Site E) but this debris does not appear to be extensive enough to <br /> be classified as a disposal area. <br /> 3. Of the two closure methods considered (in-place closure and clean closure), in-place closure <br /> had the lowest cost. Note that very conservative assumptions were made in the in-place <br /> closure costing and the actual cost is likely to be lower than that estimated here. Although <br /> clean closure was more expensive initially, it has the advantage of removing the waste from <br /> the property thereby decrease uncertainty and liability associated with owning a waste <br /> disposal site in the future. <br /> 10-3978-01.W1011017L155 Page 25 of 50 Copyright 1997,Kleinfelder,Inc. <br />
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