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ARCHIVED REPORTS XR0003983
Environmental Health - Public
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0544962
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ARCHIVED REPORTS XR0003983
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Last modified
11/6/2019 10:09:05 AM
Creation date
11/6/2019 9:42:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003983
RECORD_ID
PR0544962
PE
3528
FACILITY_ID
FA0003651
FACILITY_NAME
ARTS & ARTISTS
STREET_NUMBER
204
Direction
E
STREET_NAME
LODI
STREET_TYPE
AVE
City
LODI
Zip
95240
APN
04719102
CURRENT_STATUS
02
SITE_LOCATION
204 E LODI AVE
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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' could be stockpiled on plastic sheeting during the treatment period. However, space at this <br /> lot is sufficient to treat less than 300 cubic yards at a time (50 feet x 50 feet x 3 feet). <br /> Several treatment periods would therefore be required, and the excavation would remain <br /> open for several months. Though treatment with a portable thermal destruction unit could <br /> be performed in a week or less, these units are typically quite large, and require more space <br /> than is available on site. This method also requires space for temporary storage of treated <br /> and untreated soil. <br /> ' The space problem could be avoided by disposing of the excavated soil at a licensed facility. <br /> Off-site disposal would require transport of some of the soil to a Class II landfill, because <br /> ' contamination levels exceed the limits of Class III facilities. Landfills also require <br /> characterization of the contaminants, with one sample per 25 cubic yards and analysis for <br /> metals in addition to TPH and BTE&X. Disposal costs generally range between $20 per <br /> ' yard at Class III facilities to $90 per yard at Class II facilities. <br /> All of these methods require excavation of the contaminated soil, which is generally the <br /> ' fastest and most effective method for soil remediation. However, most of the contaminated <br /> soil underlies the Art & Artists building, and contamination extends to depths inaccessible <br /> to excavation equipment. Therefore, excavation is not practical at this site. In addition, on- <br /> site space limitations, aeration limits set by the San Joaquin Valley Air Quality Management <br /> District, sampling and analysis requirements set by landfills, and the cost of replacing the <br /> disposed soil make ex-situ treatment impractical. <br /> 6.1.2 In-Situ Treatment Alternatives <br /> ' 6.1.2.1 Bioremediation <br /> Acceptance of this treatment technology by the regulatory community has grown somewhat <br /> in recent years, as success has been achieved at several sites in California and elsewhere. <br /> Geological Audit is currently conducting three in-situ bioremediation projects in Southern <br /> California and is preparing to initiate in-situ bioremediation at another site in Lodi. <br /> 6.1.2.1.1 Principles <br />' In this method, hydrocarbon-consuming bacteria are grown in a liquid medium, which is <br /> then poured into inoculation wells that are screened through the zone of contamination. <br /> Once in the contaminant plume, the bacteria degrade the hydrocarbons and spread laterally <br />' and vertically by migrating and reproducing, creating an advancing remediation front. <br />' Hydrocarbon-degrading bacteria are able to metabolize hydrocarbons and assimilate the <br /> resulting organic chemicals into biomass for reproduction and growth. The light-end <br /> hydrocarbons are consumed first, followed by heavier compounds. <br /> GeobD"l Audit S,wic .1 <br /> A <br /> A&A PAM-28.941.47 26 <br />
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