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ARCHIVED REPORTS_XR0005088
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PR0545571
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ARCHIVED REPORTS_XR0005088
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Last modified
9/16/2020 1:42:05 AM
Creation date
3/18/2020 4:03:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005088
RECORD_ID
PR0545571
PE
3528
FACILITY_ID
FA0003570
FACILITY_NAME
BOBS MUFFLER & RADIATOR
STREET_NUMBER
466
STREET_NAME
MOFFAT
STREET_TYPE
BLVD
City
MANTECA
Zip
95336
APN
22104019
CURRENT_STATUS
02
SITE_LOCATION
466 MOFFAT BLVD
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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11 February 2003 <br /> • AGE-NC Project No. 98-0520 <br /> Page 19 of 21 <br /> 7.4. MONITORED NATURAL ATTENUATION <br /> Natural attenuation, or passive bioremediation, is a remedial alternative that relies on natural <br /> ' processes to degrade hydrocarbons. Biodegradation is' the most important natural attenuation <br /> mechanism. No additional bacteria or nutrients are added to the soil of ground water. Essential <br /> nutrients required for biodegradation are commonly naturally present in the subsurface. However, <br /> •• where high concentrations of hydrocarbons are present, nutrients may be consumed before <br /> hydrocarbon remediation is complete. <br /> Oxygen depletion in the subsurface is a characteristic of biodegradation.The core of a contaminant <br /> plume is typically under anaerobic conditions and only the margins are aerobic. Therefore, even <br /> though anaerobic biodegradation is much slower than aerobic biodegradation, anaerobic processes <br /> -may dominate the degradation of contaminants.Groundwater movement will generally assist in the' <br /> transport of nutrients in the saturated zone. <br /> Natural attenuation is normally used where low concentrations of hydrocarbons are present, <br /> following completion of another form of remediation,or in an area where no domestic or irrigation <br /> . wells are threatened. Concentrations of petroleum hydrocarbons and BTEX compounds have <br /> ' declined noticeably in monitoring well-MW-5, at the former gasoline UST location (Figures-8 <br /> and 9);all BTEX compounds are below the California's Department of Health Services' Maximum <br /> Contaminant Levels (MCLs) for drinking water. <br /> Costs for natural attenuation are.generally lower than most active remediation options; however, <br /> costs .can be highly variable depending on'the duration and type of monitoring required. The <br />' duration can be many years; for instances based on preliminary TPH-g natural attenuation curves, <br /> the TPH-g concentration in ground water at the UST locations are theoretically projected to decline <br /> to non-detectable levels by.year 2006 to 2008 (Figure 8). <br /> Fate and Transport modeling may be used to demonstrate the potential for hydrocarbons to impact . <br /> nearby ground water receptors.Quarterly ground water monitoring may also be used to demonstrate <br /> a stable and declining groundwater plume. ` <br /> 8.0. RECOMMENDATIONS ' <br />' The following recommendations for remediation are based upon data collected during the <br /> investigation of the property and predicted responses of the site conceptual model' <br /> Advanced Geo$nvironmerital,Inc. <br />
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