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ARCHIVED REPORTS XR0006513
EnvironmentalHealth
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6425
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2900 - Site Mitigation Program
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PR0519189
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ARCHIVED REPORTS XR0006513
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Last modified
8/21/2019 3:53:18 PM
Creation date
8/21/2019 3:03:33 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006513
RECORD_ID
PR0519189
PE
2950
FACILITY_ID
FA0014347
FACILITY_NAME
CURRENTLY VACANT
STREET_NUMBER
6425
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
09741031
CURRENT_STATUS
02
SITE_LOCATION
6425 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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compounds under oxygen, nitrate, and manganese limited conditions via iron (III) reduction Iron <br /> (III) is reduced to iron (11) by microbial mediated oxidation of petroleum hydrocarbons <br /> Degradation of benzene via iron (111) reduction occurs as follows <br />' 60 H+ + 30 Fe(OH)3 + C6H6 =, 6 CO2 + 30 Fe 2+ + 78 H2O <br />' From the stoichiometry of anaerobic biodegradation of benzene, 41 1 mg of iron (III) are required <br /> to completely metabolize l mg of benzene and 1 mg of iron (1I1) is capable of facilitating the <br /> destruction of 0 024 mg of benzene Similar calculations can be made using the stoichiometry for <br /> toluene, ethylbenzene, and xylene degradation from iron (111) reduction Because of the difficulty <br /> in measuring the amount of iron (III) that is available for anaerobic biodegradation, the metabolic <br /> byproduct, iron (II), is commonly measured This means that for every 1 mg of iron (11) produced <br />' during biodegradation, 0 047 mg of benzene is destroyed Using the average mass ratio of iron <br /> (11) produced to total BTEX from the individual compound biodegradation stoichiometry, 1 mg <br /> of iron (I1) is produced for every 0 046 mg of total BTEX metabolized during iron (II1) reduction <br /> The EAC of groundwater for iron (III) reduction is determined as follows <br /> EACFe = 0 046 (Fem-FeB) <br /> Where EACF,_=Expressed Assimilative <br /> p Capacity, Iran (III) reduction <br /> 0 046 = mg/1 BTFX degraded per mg/I iron (1I) produced ratio <br /> Fetii = iron (II) concentration measured in plume (mg/L) <br /> FeB =background iron (11) concentration (mg/L) <br /> An increase in iron (II) and decrease in BTEX concentrations within an existing BTEX plume is a <br /> strong indication that indigenous anaerobic microbes are established and actively biodegrading <br />' petroleum hydrocarbons via iron (III) reduction <br /> 7 2,3) Sulfate Reduction <br /> Sulfate can be used as an electron acceptor by facultative anaerobic microbes to degrade BTEX <br /> compounds tinder oxygen, nitrate, manganese and iron (III) limited conditions vid sulfate <br /> reduction Anaerobic biodegradation of benzene by sulfate reduction occurs as follows <br /> 7 5 H++ 3 75 50. 2- + C6H6 ==,� 6 CO2 + 3 75 H2S + 3 H2O <br /> From ttie stoichiometryu <br /> of anaerobic degradation of benzene by sulfate reduction, 4 6 mg of <br /> sulfate are required to completely metabolize 1 mg of benzene and 1 mg of sulfate is capable of <br /> facilitating the destruction of 0 22 m; of benzene Similar calculations can be made using the <br /> stoichiometry for toluene, ethylbenzene, and xylene degradation by sulfate reduction Using the <br /> average mass ratio of sulfate to total BTEX from the individual compound biodegradation <br /> stoichiometry, 1 mg of sulfate is required to metabolize 0 21 mg of total BTEX The EAC of <br /> 17 <br />
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