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ARCHIVED REPORTS_XR0005814
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545617
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ARCHIVED REPORTS_XR0005814
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Last modified
4/28/2020 1:59:29 PM
Creation date
4/28/2020 1:14:26 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005814
RECORD_ID
PR0545617
PE
3528
FACILITY_ID
FA0005557
FACILITY_NAME
RIPON FARM SERVICE
STREET_NUMBER
935
STREET_NAME
FRONTAGE
STREET_TYPE
RD
City
RIPON
Zip
95366
APN
26102007/2011
CURRENT_STATUS
02
SITE_LOCATION
935 FRONTAGE RD
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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' 01 June 1999 <br /> AGE-NC Project No 95-0137 <br /> Page 23 of 26 <br /> 6 3 5 Cost <br /> Bioremediation of ground water can be a very cost-effective method of treatment With little on-site <br /> ' equipment required beyond the initial inoculation, the cost for in-situ bioremediation at the site <br /> would be between $40,000 and $60,000 However, monitoring will vary depending upon regulatory <br /> requirements, which could significantly increase the total cost of the project <br /> Typical costs for monthly monitoring of an in-situ bioremediation system, in addition to standard <br /> quarterly sampling, would be approximately $1,500 per month Based on a one and one-half year <br /> ' treatment period,the total cost for in-situ bioremediation at the site would be between $70,000 and <br /> $95,000 <br /> ' 6 4 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 or 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 Oxygen depletion in the subsurface is a characteristic of <br /> biodegradation The core of a contaminant plume is typically under anaerobic conditions and only <br /> the margins are aerobic Therefore, even though anaerobic biodegradation is much slower than <br /> ' aerobic biodegradation,anaerobic processes may dominate the degradation of contaminants Ground <br /> water movement will generally assist in the 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 nearby wells Concentrations of hydrocarbon <br /> have varied in monitoring wells MW-1 and MW-2 over time Dissolved hydrocarbon concentrations <br /> ' have increased over the short tern in vapor wells VW-1 and especially VW-2 Continued ground <br /> water monitoring would be required to show a stable plume and decreasing hydrocarbon <br /> ' concentrations <br /> The duration for natural attenuation can be many years Costs for natural attenuation are generally <br /> ' lower than most active remediation options However, costs can be highly variable depending on the <br /> duration and type of monitoring required Fate and Transport modeling may be used to demonstrate <br /> the potential for hydrocarbons to impact nearby ground water receptors Quarterly ground water <br /> ' monitoring may also be used to demonstrate a stable and declining ground water plume <br /> Advanced GeoEn%ironmenlal,Inc <br />
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