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ARCHIVED REPORTS_XR0010500
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545693
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ARCHIVED REPORTS_XR0010500
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Last modified
5/27/2020 12:09:44 PM
Creation date
5/27/2020 12:08:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010500
RECORD_ID
PR0545693
PE
3528
FACILITY_ID
FA0005746
FACILITY_NAME
TRACY GARBAGE SERVICE
STREET_NUMBER
99
STREET_NAME
SIXTH
STREET_TYPE
ST
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
99 SIXTH ST
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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i <br /> .1 II <br /> S <br /> subsurface utilities An access entry agreement had not been reached with the private property <br /> Mowner for that work at the time of the drilling, consequently additional borings were not <br /> advanced on the Delta Disposal property <br /> All drilling equipment and sampling tools were cleaned prior to arriving, and before leaving the <br /> site The sampler was retrieved and dissembled, and the soil filled acetate liner was sealed with <br /> Teflon paper or foil and plastic endcaps, labeled, logged onto chain-of-custody forms and place <br /> in a chilled ice chest on crushed ice Soil sample intervals retained for chemical analysis were <br /> cut from the liners at depths of suspected contaminant presence <br /> The boreholes were logged using the Unified Soil Classification System under the supervision of <br /> a registered geologist Additional lithologic information was collected to describe the subsurface <br /> geology Soil samples were field screened for petroleum soil vapor using a photoiomzation <br /> vapor meter calibrated to the manufacturers specifications Soil samples were collected at <br /> minimum five-foot intervals, at intervals of apparent obvious contamination and/or at <br /> stratigraphic features of interest Upon completion of the borehole drilling and collection of <br /> water samples, all boreholes were backfilled with grout, placed from the bottom to top of the <br /> borehole and a PHS EHD representative witnessed the borehole sealing process as well as <br /> portions of the drilling and sampling work <br /> Groundwater Samples <br /> Each exploratory boring was sampled The ground water samples collected from the boreholes <br /> were used for a reconnaissance of the site groundwater contamination A brief summary of these <br /> procedures follows Each borehole was advanced into the aquifer and temporarily cased for <br /> sampling Depth to groundwater measurements in some boreholes were made to the nearest one- <br /> one hundredth of one foot to the surface grade, and also checked for the presence of separate <br /> phase product The water entering the borehole was sampled using a clean disposable bailer or <br /> downhole sampling tube, and carefully poured into the appropriate laboratory prepared container <br /> with m,mmum cavitation Each water sample was labeled, logged onto a chain-of-custody form, <br /> and placed in a chilled ice chest for transport to the laboratory <br /> Subsurface Conditions <br /> Three borings were advanced in the public right of way in front of the referenced site Borings <br /> B-1 and B-2 were advanced through the asphalt patches assumed to correspond with the former <br /> tank pit locations The borings revealed sandy clay and sandy silt to depths of nine to 14 feet <br /> below surface grade A sequence of interbedded sand, sandy clay and clayey sand under the clay <br /> and silt strata to depths of 19 to 24 feet. These strata compose the uppermost aquifer strata <br /> Clayey salad and silty clay underlie the aquifer strata These clayey strata appear laterally <br /> discontinuous in the general area of the site investigation (see Figure 1) Groundwater occurs at <br /> depths of 15 5 to 16 feet and appeared to be unconfined however boreholes were not open long <br /> efi,o4gh to allow for 24 hours of stabilization for additional groundwater measurements <br /> • <br /> Page 2 of 6 <br /> t <br />
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