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ARCHIVED REPORTS_XR0008413
Environmental Health - Public
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3500 - Local Oversight Program
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ARCHIVED REPORTS_XR0008413
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Last modified
7/21/2020 10:00:58 AM
Creation date
7/21/2020 9:46:52 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008413
RECORD_ID
PR0545864
PE
3528
FACILITY_ID
FA0004530
FACILITY_NAME
MARLOWE PROPERTY
STREET_NUMBER
4648
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95215
CURRENT_STATUS
02
SITE_LOCATION
4648 WATERLOO RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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1 <br />' 18 February 1997 <br /> • AGE-NC Project No 95-0104 <br />' Page 13 of 22 <br />' 6 4 1 PRINCIPLES <br /> Biodegradation is the most important natural attenuation mechanism No additional bacteria or <br />' nutrients are added to the soil Essential nutrients required for biodegradation are usually naturally <br /> present in the subsurface However, where high concentrations of hydrocarbons are present, nutrients <br /> may be consumed before hydrocarbon remediation is complete Oxygen depletion in the subsurface <br />' is another characteristic of passive biodegradation The core of a contaminant plume typically exists <br /> under anaerobic conditions and only the margins are aerobic Therefore even though anaerobic <br /> biodegradation is much slower than aerobic biodegradation, anaerobic processes may dominate the <br />' degradation of contaminants Natural attenuation is normally used where low concentrations of <br /> hydrocarbons are present or after completion of another inethod of remediation <br />' 6 4 2 DURATION <br />' The natural attenuation process is time consuming, it may take many years for the hydrocarbon plume <br /> to reach levels comparable to those of active remediation methods Costs for natural attenuation can <br />'. be significantly lower than the active remediation options Howevei, additional characterization costs <br /> and periodic monitoring costs would accumulate over time and could potentially be significant <br /> depending on the duration and type of monitoring requirements <br /> 6 4 3 FEASIBILITY <br /> IAlthough it is difficult to determine the feasibility of natural attenuation, fate and transport modeling <br /> may be used to determine the probabilities of hydrocarbon-impacted soil affecting ground water <br />' Where ground water has already been impacted, fate and transport modeling may also be used to <br /> evaluate the migration and dilution of hydrocarbons <br /> I6 4 4 ESTIMATED COSTS <br /> It is likely that some additional assessment, including additional laboratory analysis of soil samples <br />' and/or confirmation soil sampling would be verify to monitor and required vera natural attenuation <br /> q <br /> Furthermore, a long-term monitoring program, perhaps 10 years, would be initiated <br /> Overall costs for natural attenuation in soil cannot be estimated at this time Much of the cost <br /> associated with natural attenuation would be for long-term ground water monitoring, discussed in <br /> Section 7 4 4 Other costs for natural attenuation in soil would include periodic soil borings or <br /> probings to monitor the natural attenuation rate <br /> I <br />
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