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ARCHIVED REPORTS_XR0012232
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545890
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ARCHIVED REPORTS_XR0012232
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Last modified
7/22/2020 12:12:42 PM
Creation date
7/22/2020 11:52:48 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012232
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 /> Mr Nuel Henderson <br /> Page 2 of 4 <br /> . A potentiometric surface map generated using the groundwater elevation data from all site monitoring <br /> wells is shown on Figure 2 Groundwater monitoring data are summarized in Table 1 Monitoring <br /> data sheets and well construction details are included in Attachment A <br /> On May 28, 29 and 30, 2003, a Ground Zero technician collected groundwater samples from <br /> monitoring wells MW3 through MW6, MW8, MW10, MW11, MW13B through MW16B and from <br /> vapor wells VW4 and VW6 Samples were not collected from vapor wells VW2 and VW5 as they <br /> were dry (Table 1) <br /> A minimum of three well casing volumes was purged from each well prior to sampling During the <br /> purging process, physical parameters (pH, electrical conductivity, and temperature) were monitored <br /> Subsequent to parameter stabilization, and a minimum of 80% recovery of initial depth to groundwater <br /> measurements, groundwater samples were collected and placed in an iced cooler for transport to <br /> Argon Laboratories (ELAP #2359) under chain of custody protocol <br /> Analysis consisted of gasoline oxygenates, EDB and 1,2-DCA by EPA Method 8260, TPHg by EPA <br /> Method 8015 modified and BTEX by EPA Method 8021B Purge water was transferred into labeled <br /> 55-gallon drums approved by the Department of Transportation (DOT) The waste is stored onsite <br /> within a secured area Purge logs are included in Attachment A <br /> GROUNDWATER ANALYTICAL RESULTS <br /> Groundwater Monitoring Wells <br /> TPHg was detected in all sampled wells except MW6, MW10, MW11, MW15A and MW15C <br /> Benzene was detected in all wells sampled except for MW6, MW I0, MW 11, MW15A and MW 15B <br /> Dissolved TPHg and BTEX levels in the remaining monitoring wells were within historical ranges, <br /> and appear to be stable to decreasing TPHg and BTEX concentration data are summarized in Table <br /> 2 Attachment B contains laboratory reports and chain of custody documentation Graphs depicting <br /> TPHg and benzene concentrations over time are included in Attachment C <br /> MTBE continues to below laboratory method detection limits in wells MW5, MW6, MW8, MW 13B <br /> and MW15C MTBE was detected in wells MW3 (28,000 parts per billion - ppb), MW4 (10,000 <br /> ppb), MW11 (26 ppb) and MW14 (100,000 ppb), which are located along the southern portion of the <br /> site (Figure 2) In downgradient wells MW10 (north side of Market Street), MW15A and MW15B <br /> (Eugema and Market) MTBE was reported at concentrations of 2 5 ppb, 33 ppb and 190 ppb, <br /> respectively Elevated levels of MTBE were also found in cross-gradient wells MW 16A and MW 16B <br /> These wells are clearly affected by offsite releases <br /> DIPE was at non-detectable levels in all sampled wells except for well MW 11 (2 9 ppb) EDB was <br /> not detected in any of the monitoring wells sampled 1,2-DCA was detected in wells MW10, MWl I, <br /> MW 1313, MW 15A and MW 15B Concentrations of 1,2-DCA ranged from 4 7 ppb (MW 15A) to 940 <br /> ppb (MW 13B) Analytical results for gasoline oxygenates, EDB and 1,2-DCA are summarized in Table <br /> 3 Attachment B contains laboratory reports and chain of custody documentation <br /> G 1GROUNDZEIROEKIQMR1200312gm2003 doc <br />
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