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ARCHIVED REPORTS_XR0011359
Environmental Health - Public
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ARCHIVED REPORTS_XR0011359
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Last modified
12/10/2019 7:33:46 PM
Creation date
12/10/2019 11:47:57 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011359
RECORD_ID
PR0545039
PE
3528
FACILITY_ID
FA0010186
FACILITY_NAME
DEL MONTE FOODS PLNT #33 - DISCO WH
STREET_NUMBER
110
Direction
N
STREET_NAME
FILBERT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15702009
CURRENT_STATUS
02
SITE_LOCATION
110 N FILBERT ST
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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i <br /> conditions present at the Disco location, target levels of BTEX and TPH-Gas are <br /> { nondetectable and 10 mg/kg, respectively. <br /> Remedial Technologies <br /> Potentially applicable technology types and process options expected to be effective in <br /> achieving the remedial objectives in soil and groundwater were identified and evaluated <br /> (Figure 4-1). Also included are screening comments with respect to the effectiveness, <br /> implementability, and relative cost of each of the process options for the chemical <br /> compounds and conditions at the property. <br /> Effectiveness is an estimate of how well each process option will perform in handling <br /> the estimated volume of waste material and in reducing contamination or controlling <br /> mobility. Implementability includes both construction considerations and the feasibility <br /> of implementing each process option in order to eliminate those that would be <br /> unworkable or too difficult to permit at the .property. The initial cost screening was <br /> based on engineering judgement as to whether costs were high, low, or moderate <br /> relative to other process options of the same technology type. <br /> + As a result of the technology screening for soils and groundwater shown on Figure 4-1, <br /> technology options expected to be the most cost-effective were selected for developing <br /> remedial alternatives. <br /> Technology Descriptions <br /> Process Options for Unsaturated Soils <br /> As discussed in Section 3 of this report, petroleum hydrocarbons occur in the <br /> unsaturated soil within the vertical boundaries. of the former tank pit. Affected soils in <br /> this area occupy a zone about 20 feet thick,above the groundwater table, between 55 <br /> and 75 feet bgs. The depth at which these petroleum hydrocarbons occur in the soil <br /> make excavation impractical. Therefore, the remediation options chosen for <br /> unsaturated soil are the in situ techniques of sparging and bioremediation. <br /> Sparging. Sparging is a method of introducing air, and thus oxygen, into the <br /> subsurface. Blowers installed in wells inject air below the water table. Sparging allows <br /> for oxygen to penetrate a specific and localized area above and below the water table. <br /> This introduction of oxygen will stimulate aerobic biodegradation of petroleum <br /> compounds.. <br /> In Situ Bioremediation. In situ bioremediation is commonly used for treating <br /> petroleum products in soil and groundwater. Biological degradation occurs naturally in <br /> the environment, but with the addition of nutrients in an aerobic environment, <br /> biodegradation can be greatly enhanced. The technology involves adding nutrients such <br /> as nitrogen and phosphorus, and oxygen to saturated soil and groundwater through <br /> sF03160 \RP1007.51 4-3 <br />
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