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ARCHIVED REPORTS_XR0011032
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545039
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ARCHIVED REPORTS_XR0011032
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Last modified
12/10/2019 2:39:04 PM
Creation date
12/10/2019 11:44:22 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011032
RECORD_ID
PR0545039
PE
3528
FACILITY_ID
FA0010186
FACILITY_NAME
DEL MONTE FOODS PLNT #33 - DISCO WH
STREET_NUMBER
110
Direction
N
STREET_NAME
FILBERT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15702009
CURRENT_STATUS
02
SITE_LOCATION
110 N FILBERT ST
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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QUARTERLY MONITORING RESULTS <br /> Field notes indicate D.O. readings of less than 0.5 mg/L which is considered the minimum <br /> I <br /> reproducible detection limit. <br /> In the degradation of BTEX,nitrate is converted to aqueous nitrogen by a process known as <br /> denitrification where nitrate is the electron acceptor. The nitrate concentration around the <br /> j zone of significant contamination(MW-DIS-2 and 3)is below the detection limit. <br /> Background nitrate concentration appears to be on the order of 6 to 8 mg/L(MW-DIS-4 and <br /> 9). <br /> Insoluble Fe'accepts an electron and becomes soluble Fe",in the degradation of BTEX. <br /> Figure 3 shows elevated levels of Fe+2 in the zone of significant contamination with an <br /> average concentration in MW-DIS-2 of 0.9 mg/L. <br /> Sulfate is converted to aqueous hydrogen sulfide in the degradation of BTEX.Figure 3 <br /> shows depressed levels(5.0 mg/L)of sulfate in the zone of significant contamination in <br /> contrast to 11 to 47 mg/L outside the zone (MW-DIS-4 and 9). <br /> The anaerobic fermentation of BTEX converts carbon dioxide into dissolved methane.After <br /> three quarters of monitoring,fermentation does not appear to play a significant role in <br /> BTEX degradation at this site. <br /> The measured change in concentration of dissolved oxygen,nitrate,ferrous(FE") iron,and <br /> sulfate between background samples and the samples collected from within the BTEX <br /> plume,provides a means for estimating the rate of BTEX removal from groundwater. <br /> Table 5 presents the concentration of these natural attenuation indicators. <br /> TABLE 5 <br /> Geochemical Indicators of Natural Attenuation <br /> Del Monte Disco Property <br /> Indicator Background* In the Plume* Change <br /> Dissolved Oxygen 4.6 mg/L <0.5 mg/L 4.1 mg/L <br /> Nitrate 6.9 mg/L <0.2 mg/L 6.7 mg/L <br /> Ferrous Iron <0.1 mg/L 0.9 mg/L 0.8 mg/L <br /> Sulfate 24 mg/L** 2 mg/L 22 mg/L <br /> Based on average values from quarterly data. <br /> Based on the average of average for MW-DIS-4 and 9. <br /> Based on a mass ratio between each indicator and a benzene molecule (C6Hd,the mass <br /> removal of BTEX can be determined for each indicator as described in Table 6. For each liter <br /> of background water that enters the BTEX plume,7.6 mg of BTEX is potentially removed. <br /> i <br /> SFO1G:IPROJECTSIOELmouTEIPLANT MiFLREP.Dx 15 <br />
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