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ARCHIVED REPORTS_XR0007287
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545106
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ARCHIVED REPORTS_XR0007287
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Last modified
12/19/2019 4:22:20 PM
Creation date
12/19/2019 4:04:35 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007287
RECORD_ID
PR0545106
PE
3529
FACILITY_ID
FA0003694
FACILITY_NAME
RIVER CITY PETROLEUM CARDLOCK
STREET_NUMBER
2211
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
11707050
CURRENT_STATUS
02
SITE_LOCATION
2211 N WILSON WAY
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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I <br /> • cone penetration determinations of soil classification Groundwater samples from below 115' were <br /> difficult to extract Some hydro punch samples required more than 4'of screen and required more than <br /> 15 minutes of collection time to retrieve 120 m1 of groundwater <br /> Conclusions from Sample Analysis and Cone Penetration Data <br /> The extent of hydrocarbon contamination of the groundwater is deeper than the 135'that was originally <br /> anticipated by the work plan for this CPT investigation In the area of the estimated spill point (near <br /> MW#1), CPT#2 water samples indicate contamination of the groundwater in the range of 10000 ug/L <br /> for TPHg, at a depth of 135 feet Most likely the groundwater contamination extends more than 150' <br /> below the surface <br /> It is the authors opinion that the major source of the gasoline contamination for this site is the UST's on <br /> the site or the related dispenser piping The contamination has spread from the UST and dispenser area <br /> to the northwest (see attached Contour Map of 1,2-DCA levels) <br /> Extraction of groundwater below 115' of depth will be very slow process The estimated permeability <br /> of the soil at this depth is in the range of k = 1 x10-6 to k= I xlO-7 for the areas investigated by the <br /> scope of this work plan <br /> The more permeable strata of sandy silts in the depths below 115'will be very difficult to isolate for any <br /> extraction remediation methods As a result, cross contamination between strata during any type of <br /> groundwater extraction method is highly likely <br /> Recommendations for Future Work <br /> It is recommended that the site continue to be monitored on a quarterly basis A deep monitoring well <br /> should be installed near the location of CPT#2 to a depth of 150' below the surface The existing work <br /> plan required the installation of monitoring well MW#IOS and MW#IOD in the area of CPT#3 It is <br /> recommended that this work start with the depth of well for MW#I OS be 60', and the depth of well for <br /> MW i O#D be 150' <br /> Recommendations for Soil and Groundwater Remediation(Requested by J Barton RWQCB) <br /> The soil contamination above groundwater could be reduced using vapor extraction in the general area <br /> of the UST's and the dispensers The well defined sand strata from I O'to 30'ofdepth will serve as a good <br /> conduit for soil vapor movement <br /> The remediation of the groundwater on this site is much more difficult Results will be very slow under <br /> any remediation method due to very low permeability Groundwater extraction and treatment will be the <br /> most successful in the sandy silt strata at depths from 80' to 115'below the surface Below 115' foot of <br /> depth, any method of remediation will be extremely slow due to the low permeability of those soils <br /> Muchmore work will be required to design an effective groundwater remediation system To complicate <br /> the problem, the must desirable location for extraction wells is in the building <br /> Suspected Errors in Chemical Analysis <br /> The soil samples from CPT#3 and CPT#4 indicate the presents of MTBE These samples were part of <br /> ithe same run done by Castle and likely were subject to contamination within the laboratory The analysis <br /> for each sample are basically the same, which is very uncommon for any set of samples (see Soil <br /> 3 <br />
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