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ARCHIVED REPORTS XR0000109
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ARCHIVED REPORTS XR0000109
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Last modified
10/24/2018 1:12:07 AM
Creation date
10/23/2018 1:16:23 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS XR0000109
FileName_PostFix
XR0000109
RECORD_ID
PR0543371
PE
3528
FACILITY_ID
FA0006174
FACILITY_NAME
Best Express Foods Inc.
STREET_NUMBER
2651
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16912003
CURRENT_STATUS
02
SITE_LOCATION
2651 S AIRPORT WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
WNg
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EHD - Public
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1 <br /> • Page 4 <br /> Ms Margaret Lagono <br />' February 21, 1997 <br />' PetroIeum Hydrocarbon Analytical Data <br />' Certified laboratory reports and chain-of-custody documentation are presented in <br /> Appendix C Current TVH-G and BTEX results are presented in Table 3 Historic <br /> tabulation and graphical presentations for TVH-G and benzene are presented in Table 4 <br /> and Table 5, respectively <br /> 1 PSH were not observed in any of the monitoring wells The highest TVH-G and BTEX <br /> concentrations were detected in samples collected from monitoring wells MW-1, MW-4, <br />' and MW-12 Lower TVH-G and BTEX concentrations were measured in samples <br /> collected from Monitoring Wells MW-5, MW-9, MW-11, and MW-13 Petroleum <br /> concentrations were not detected in samples collected from monitoring wells MW-2 and <br /> MW-3, MW-6 through MW-8, MW-10, and the trip blank TB-01 In general, the <br />' detected petroleum concentrations were lower than those measured in the previous <br /> monitoring event, except for samples collected from monitoring wells MW-4 and MW- <br /> 12 As illustrated in the Table 4 and Table 5 historic graphical presentations, TVH-G and <br />' benzene concentrations are generally trending lower <br /> Biodegradation Assessment Data <br /> 10 Biodegradation analytical results are summarized in Table 6 A graphical presentation of <br /> results for samples collected from monitoring wells passing through the area of <br /> petroleum-impacted groundwater is shown in Table 7 and Table 8 <br /> 1 The reference document for this biodegradation assessment, Protocol for Monitoring <br /> Intrinsic Bioremediation in Groundwater, indicates that natural biodegradation is <br /> 1 occurring when a directly proportional relationship is evident between petroleum <br /> concentrations and ferrous iron and alkalinity concentrations,and an inversely <br /> proportional relationship with dissolved oxygen, redox potential, nitrate, and sulfate <br /> concentrations A decrease of dissolved oxygen concentration, in a sample collected from <br /> 1 a petroleum-impacted well compared to a sample collected from a lower or non-impacted <br /> well, would indicate aerobic biodegradation An increase of ferrous iron or alkalinity, or a <br /> decrease in redox potential, nitrate, or sulfate would be an indication of anaerobic <br />' biodegradation Such evidence demonstrated for any one of these parameters suggests the <br /> occurrence of intrinsic biodegradation <br />' Benzene concentrations for samples collected from monitoring wells MW-6, MW-4, <br /> MW-1, MW-7, MW-12, and MW-8 (along profile A-A' of Figure 5) are plotted along <br /> with their respective dissolved oxygen concentrations on the graph in Table 7 A decrease <br /> in dissolved oxygen, evident in samples collected from those monitoring wells with <br /> 1 detectable concentrations of benzene, indicates that aerobic biodegradation is occurring <br /> Benzene concentrations for samples collected from the wells along profile A-A' are also <br /> 1 plotted along with the other biodegradation parameters in Table 8 Decreases in nitrate <br /> and sulfate concentrations, and negative redox potential values are evident in the <br /> • <br /> 1 <br /> E 121382112599714gtr96 doc <br /> 1 <br />
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