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ARCHIVED REPORTS_XR0002475
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0540859
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ARCHIVED REPORTS_XR0002475
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Last modified
1/15/2020 3:48:27 PM
Creation date
1/15/2020 2:59:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002475
RECORD_ID
PR0540859
PE
2960
FACILITY_ID
FA0023361
FACILITY_NAME
PLAY N PARK (FORMER BARNES TRUCKING)
STREET_NUMBER
1817
Direction
S
STREET_NAME
FRESNO
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
1817 S FRESNO AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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CLEARWATER <br /> • R d P <br /> En rn <br /> vironrnfa( Se Srrurces <br /> which takes into account the observed mass loss (contaminant decay rate), however, <br /> volatilization has been demonstrated to account of only 5% of benzene mass loss at a site with <br /> relatively favorable conditions for this process3 <br /> Advection is responsible for the off-site migration of contaminants in concentrations below the <br /> detection limit To evaluate the extent of a plume attenuated through advection, the dissolved <br /> constituents are assumed to move at the same velocity as the groundwater (i a no retardation) <br /> Using the hydraulic conductivity of the water bearing zone, average hydraulic gradient, and <br /> average effective porosity, an approximate volume of hydrocarbons moving off site at <br /> concentrations at or below the detection limit can be estimated using Darcy's Law However, <br /> this process typically accounts for a relatively small percentage of apparent contaminant mass <br /> loss at most sites <br /> Biodegradation Processes and Indicators <br /> • During biodegradation, microbes utilize electron acceptors to convert hydrocarbons to carbon <br /> dioxide, water, and biomass In aerobic degradation, the electron acceptor is dissolved oxygen <br /> (DO) In anaerobic degradation, compounds other than DO are used as electron acceptors The <br /> reactions that yield the most energy take precedence over those reactions that yield less energy <br /> (except for denitrification which yields the most free energy but will not occur if DO <br /> concentrations are >0 5 milligrams per liter (mg/L)) This results in electron acceptors being <br /> used up in the following preferential order DO, nitrate, ferric-iron oxides, sulfate, and carbon <br /> dioxide (methanogenesis) Since DO and nitrate are toxic to sulfate-reducing organisms, sulfate <br /> cannot be used as an electron acceptor until DO and nitrate have been sufficiently depleted4 <br /> Metabolism through iron reduction uses ferric-iron oxides and produces ferrous iron (dissolved) <br /> as a byproduct <br /> 3Chiang,C Y et al (1989) Aerobic Biodegradation of Benzene,Toluene,and Xylene in a Sandy Aquifer-Data <br /> Analysis and Computer Modeling Groundwater Vol 27,No 6, p 823-834 <br /> • 4Wiedemeier,T H,Wilson,J T , Kampbell,D H,Miller,R N and Hansen, J H (1995) Technical Protocol for <br /> implementing Intrinsic Remediation with Long-Term Monitoring for Natural Attenuation of Fuel Contamination <br /> ZB178C/4Q03 Monitoring Rpt 9 January 29,2004 <br />
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