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2900 - Site Mitigation Program
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PR0526717
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Last modified
2/19/2020 4:56:53 PM
Creation date
2/19/2020 4:39:05 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0526717
PE
2950
FACILITY_ID
FA0018089
FACILITY_NAME
TEIXEIRA-SOUZA PROPERTY
STREET_NUMBER
18353
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
20945014
CURRENT_STATUS
01
SITE_LOCATION
18353 W GRANT LINE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Report of Findings—Phase H Soil anu ;roundwater Assessment Page 3 <br /> Teixeira-Souza Dairy February 1,2007 <br /> WKA No.6504.45 <br /> Once finalized, the new tentative WDR document will be the most comprehensive operations <br /> and monitoring guidance for dairies to date. Additions to the updated WDR guidance, in <br /> comparison to previous WDRs, include a comprehensive periodic soil sampling program to <br /> monitor impacts to soils at dairy facilities. In anticipation of the tentative WDR document's <br /> approval and implementation by the RWQCB, WKA developed a scope of work for this <br /> assessment of soil and groundwater conditions at the site to incorporate key sampling <br /> requirements to meet the tentative WDR. <br /> FIELD ACTIVITIES <br /> On December 27 and 28, 2006, WKA field representatives directed the drilling and sampling of <br /> twenty direct-push borings (SB 1 through SB20)to profile current soil and groundwater <br /> conditions at various locations across the site (Figure 2). V&W Drilling of Isleton, California, <br /> provided a truck-mounted GeoProbe drilling rig for both days of sampling activities, while RST <br /> Drilling of Woodland, California provided a track-mounted GeoProbe drilling rig for the second <br /> day of sampling activities. The track-mounted GeoProbe drilling rig was added, as the western <br /> portion of the site was rendered inaccessible to the truck-mounted GeoProbe rig clue to saturated <br /> ground conditions resulting from recent winter storm events. <br /> The twenty boring locations were advanced to depths ranging from 20 to 24 feet below ground <br /> surface (bgs), depending on local soil conditions and the depth that groundwater was first <br /> encountered. Soil samples were collected from various depth intervals at each boring location at <br /> depths ranging from 1 to 14 feet bgs for lithologic observation and/or chemical analysis. Soil <br /> samples were taken from the acetate tube lining used in the GeoProbe drill stem and field <br /> screened for methane using a RKI Eagle landfill gas analyzer, then collected into eight-ounce <br /> glass jars with Teflon-sealed lids. Soil samples were promptly labeled and placed into an <br /> ice-chilled cooler for transport to the analytical laboratory under chain-of-custody <br /> documentation. Ten of the 33 soil samples collected over the two-day sampling event were <br /> chosen for laboratory analysis,the remaining 23 soil samples were held by the laboratory. All <br /> sampling equipment was decontaminated with a soap solution of AlconoxTM and rinsed in clean, <br /> potable water prior to collecting each sample. <br /> Groundwater samples were collected after placing a '/4-inch PVC casing into each borehole, with <br /> the bottom part of the casings screened to allow for groundwater to collect into the borehole. A <br /> plastic hose with check valve was used to collect water samples in the boreholes advanced by the <br /> truck-mounted GeoProbe rig while a peristaltic pump was used to collect water samples from the <br /> � ;.V <br />
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