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ARCHIVED REPORTS XR0006135
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3500 - Local Oversight Program
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ARCHIVED REPORTS XR0006135
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Last modified
6/21/2019 4:04:15 PM
Creation date
6/21/2019 11:17:54 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006135
RECORD_ID
PR0544590
PE
3528
FACILITY_ID
FA0003932
FACILITY_NAME
KWIKEE FOODS
STREET_NUMBER
2081
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204
APN
12315225
CURRENT_STATUS
02
SITE_LOCATION
2081 COUNTRY CLUB BLVD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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the first quarter (March) and fourth quarter (October) confirm that all three Kwikee wells were <br /> impacted at high concentrations. Concentrations were even higher in the Chevron wells, with both <br /> MW-3 and MW-4 above 60,000 ppb and MW-1 at 56,000 ppb. Gasoline was even detected in the <br /> most upgradient well (MW-5) at 240 ppb. <br /> 4.2 Northward Migration: 1996 <br /> The shape of the plume changed somewhat in 1996, and although the northwest-southeast <br /> elongation from MW-4 toward MW-1 was still evident, a secondary southwest-northeast axis from <br /> MW-1 toward MW-7 had also appeared (Figure 23). This axis extended as far north as MW-9, <br /> which was somewhat less impacted than in 1995. Because groundwater flow was northward toward <br /> MW-9 in 1996, this decline in the TPH-g concentration could not be due to cessation of plume <br /> movement to the north. A more likely explanation is that the decline is due to lateral diffusion. <br /> TPH-g concentrations also declined in both MW-3 and MW-5, which is to be expected with <br /> northward groundwater flow, but the increase from 11,000 to 15,000 ppb in MW-8 is not consistent <br /> with northward flow. The reason for the increase is not apparent from the data. <br /> 4.3 Continued Northward Expansion: 1997 <br /> Further northward elongation of the plume took place in 1997, and the TPH-g concentration in <br /> MW-9 peaked at 15,000 ppb (Figure 24). This coincided with the maximum development of <br /> northward groundwater flow, as shown in Figure '14. Rather surprisingly, none of the three wells <br /> north of MW-9 became impacted, although MW-10 and MW-11 were clearly downgradient and on <br /> trend of the plume. The concentration in MW-3 declined further, and the concentration also <br /> declined in MW-8, meaning that both of these wells recorded the expected decline under conditions <br /> of northward groundwater flow. However, the concentration increased slightly above the detection <br /> limit in MW-5, which would not be anticipated. <br /> Upgradient Environmental did not sample the Kwikee site in 1997, but samples were collected by <br /> Chevron's consultant on August 26, at the same time the Chevron site was sampled, and the results <br /> are shown in Figure 24. Elevated concentrations were still present over at least the southern half of <br /> the Kwikee site, but concentrations had declined somewhat from those in 1995 and the TPH-g <br /> contours have retreated slightly westward from their 1995 position (Figure 22). <br /> 4.4 Reversal: Southward Migration, 1998 <br /> In 1998, groundwater flow reversed and became due south (Figure 15). The gasoline plume <br /> responded to this change, and a strong, narrow, northeast-southwest elongation developed, <br /> extending all the way to MW-5 and culminating with that well reaching a much greater TPH-g peak <br /> than it had ever recorded previously (Figure 25). The concentration of 9,600 ppb stands out as a <br /> major red flag for this well, which had not experienced concentrations in excess of 1,000 ppb in <br /> more than more than four years. At the same time, concentrations declined further in MW-3 and <br /> 16 <br />
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