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Last modified
3/4/2020 12:00:52 PM
Creation date
3/4/2020 11:19:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0516329
PE
2965
FACILITY_ID
FA0012560
FACILITY_NAME
KELLOGG GARDEN PRODUCTS
STREET_NUMBER
12686
STREET_NAME
LOCKE
STREET_TYPE
RD
City
LOCKEFORD
Zip
95237
APN
05132011
CURRENT_STATUS
01
SITE_LOCATION
12686 LOCKE RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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OV %Tt <br /> JUL 2 1 2000 <br /> ENVIRONMENT HEALTH <br /> PERMIT/SERVICES <br /> California, dated July 11, 2000. This workplan was approved by San Joaquin County Public <br /> Health Services Environmental Health Division (PHS/EHD) with minor modifications on July <br /> 14, 2000. <br /> Drvwell Destruction <br /> The drywell locations are shown on Figure 2 in the bottom of a pond area. The depth of the pond <br /> area is approximately four feet below ground surface (bgs). The drywells were approximately 30 <br /> inches in diameter and 38 feet deep. In each drywell was a 4-inch PVC center pipe. <br /> A small ramp was constructed in the southwest corner of the pond area to provide access for the <br /> equipment necessary to complete the drywell destruction. The well monuments were removed <br /> from the top of each well. A vacuum rig was used to remove gravel from around the center pipe <br /> of each drywell. Water was injected into each drywell to loosen up the gravel pack. The gravel <br /> and water were then removed from the drywells using the vacuum rig. Gravel encountered in <br /> each well was approximately 2.5 inches in diameter, which is larger than the 1.5-inch diameter <br /> gravel usually encountered in most drywells. <br /> Near each drywell, a shallow pit was excavated and lined with visquene plastic. The gravel, <br /> injection water, and soil cuttings from each drywell was placed in these pits and one composite <br /> soil sample was collected from each spoils pile. <br /> After removing as much gravel as possible with the vacuum rig from each drywell, the bucket <br /> auger rig was then used to overdrill each drywell to the bottom of the original boring, <br /> approximately 38 feet bgs. Once the bottom of each drywell had been verified, another two feet <br /> of soil was removed from each drywell and a soil sample was collected from the bottom of each <br /> drywell. Soil cuttings were placed in the dedicated pits described above. <br /> Soil Sample Anal <br /> In accordance with the PHS/EHD Guidelines for Closure of Shallow Dry Wells, all eight <br /> samples (four bottom samples and four cuttings samples) were analyzed for volatile organic <br /> chemicals (VOCs) by EPA method 8260, semi-volatile organic compounds (SVOCs) by EPA <br /> Method 8270, total petroleum hydrocarbons as gasoline (TPHg) and as diesel (TPHd) by EPA <br /> method 8015, total oil and grease (TOG) by method 5520, and for toxicity characteristics of <br /> metals CAM 17 by TCLP analysis. State-Certified Excelchem Environmental Labs analyzed all <br /> eight soil samples on a 24-hour turn-around time. <br /> Soil samples collected from the bottom of the drywells NW, SW, SE, and NE contained no <br /> detectable concentrations of VOCs, SVOCs, TPHg, TPHd, or TOG. The soil samples collected <br /> from the bottom of the drywells NW, SW, SE, and NE contained low concentrations of various <br /> metals. The concentrations of metals detected in these soil samples were consistent with <br />
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