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ARCHIVED REPORTS_XR0012200
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545890
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ARCHIVED REPORTS_XR0012200
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Last modified
7/22/2020 12:11:37 PM
Creation date
7/22/2020 11:36:44 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012200
RECORD_ID
PR0545890
PE
3526
FACILITY_ID
FA0025958
FACILITY_NAME
ROEK BROTHERS CONSTRUCTION
STREET_NUMBER
102
Direction
S
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
15502065
CURRENT_STATUS
02
SITE_LOCATION
102 S WILSON WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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I <br /> 7 Mr Ron Rowe <br /> Page 2 of 5 <br /> gvapor P <br /> groundwater was also measured in or wells VW1 and VW3 through VW6 Wellhead <br /> elevations have not been determined for the vapor wells Water levels rose an average of 1 80 <br /> feet since last monitored on February 2, 2000, and are now at the highest levels recorded <br /> Groundwater flow direction was generally towards the east with a gradient averaging <br /> approximately 0 003 feet per foot A groundwater gradient map generated using the May 9, 2000 <br /> monitoring data is shown on Figure 2 Recent groundwater monitoring data are summarized in <br /> Table 1 Monitoring logs and well construction information are included in Attachment A <br /> On May 9, 10 and 11, 2000 Ground Zero collected groundwater samples from groundwater <br /> monitoring wells MW 1 through MW 11 and MW 13, and vapor wells VW 1 and VW3 through <br /> ' VW6 Except for MW9, at least three well casing volumes were purged from each well prior to <br /> sampling Physical parameters (pH, conductivity, temperature) were monitored during purging <br /> and allowed to stabilize prior to sampling Samples were collected after groundwater recharged <br /> ' to 100% of the original level Purged water was contained in 55-gallon drums approved by the <br /> Department of Transportation and stored onsite in a locked enclosure Purge logs are included in <br /> Attachment A <br /> Samples were placed on ice and transported under chain of custody to Argon Laboratories (FLAP <br /> 42359) Samples were analyzed for TPHg using modified EPA method 8015 and BTEX using <br /> EPA method 8020 Oxygenates, EDB and 1,2 DCA were analyzed using EPA method 8260 <br /> Analytical results for TPHg, BTEX and MTBE are summarized in Table 2, oxygenate results are <br /> summarized in Table 3 Attachment B contains laboratory reports and chain of custody <br /> ' documentation <br /> Groundwater Analytical Results <br /> 1 <br /> Groundwater Monitonng Wells <br /> The potentiometric surface was above the top of the screened intervals to all monitoring wells <br /> except MW13 Petroleum hydrocarbons were detected in groundwater samples collected from all <br /> wells Well MW 12 was inaccessible and not sampled, however, MW 12 has historically been at <br /> non-detectable concentration for petroleum hydrocarbons The highest concentrations of TPHg <br /> and BTEX were detected in samples collected from wells MW3, MW4, MW5 and MW13 <br /> Except for a noticeable increase in well MW2, petroleum hydrocarbon concentrations generally <br /> remained stable in wells affected by the onsite release <br /> Wells MW3 and MW4 are located along the southern boundary of the subject property and are <br /> ' affected by offsite release(s) MW7, located slightly north of MW3, and well MW11 located to <br /> the east are now apparently also affected Hydrocarbon concentrations in MW3 and MW4 are <br /> showing continual increases TPHg and BTEX concentrations are summarized in Table 2 <br /> ' roeklgmr12QM2000 <br />
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