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ARCHIVED REPORTS_XR0002525
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0542014
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ARCHIVED REPORTS_XR0002525
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Last modified
1/16/2020 5:43:54 PM
Creation date
1/16/2020 4:25:53 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002525
RECORD_ID
PR0542014
PE
2960
FACILITY_ID
FA0023306
FACILITY_NAME
LARRYS AUTO REPAIR
STREET_NUMBER
308
Direction
N
STREET_NAME
GRANT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
01
SITE_LOCATION
308 N GRANT ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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' All bonngs were drilled using a truck-mounted B-61 HDX drill ng The drill ng and two- <br /> man crew were supplied by V & W Drilling of Rio Vista, California The borings were <br /> advanced using eight-inch diameter continuous flight hollow stem augers Auger returns <br /> were monitored dunng drilling activities for the presence of organic vapors using a photo- <br /> ionization detector (PID Thermo Environmental 580A, 10 0 eV, calibrated to isobutylene) <br />' Discrete sosamples coIlected in borings at five-foot intervals A 140-Ib hammer <br />' was used to advance a sampler loaded with three precieaned 2-inch by 6-inch brass sleeves <br /> The number of blows required to advance the sampler in 6-inch increments was recorded <br /> on the boring logs (See Appendix A) To avoid cross contamination, the hollow stem augers <br /> and drill bit were steam cleaned by the drill crew utilizing a portable decontamination unit, <br /> prior to dulling each boring Prior to the collection of each sample, the sampling equipment <br /> was decontaminated in a tri-sodium phosphate (TSP) solution and rinsed twice with water <br /> IFor each sample, the lead brass tube was removed and immediately covered with aluminum <br /> sheets, capped, sealed with tape, and logged under chain of custody procedures The <br /> samples were immediately placed in a chilled container Upon completion of drilling <br /> activities, the samples were transported and relinquished to Sparger Technology, Inc , a state <br /> certified analytical laboratory, for analysis Soil from the middle brass tube was extruded into i <br /> a plastic bag and screened for organic vapors using a photo-ionization detector (PID) The <br /> reading was recorded on the boring log, and the soil was described in accordance with the <br /> Unified Soil Classification System <br /> 3.2 Well Completion <br /> Bonngs 131, B2, B3, and B4 were completed as groundwater monitoring wells, designated <br /> MW-1, MW-2, MW-3, and MW-4, respectively The screened intervals in MW-1 is from 55 <br /> I feet to 75 feet, MW-2 and MW-3 from 54 feet to 74 feet, and MW-4 from 45 feet to 70 feet <br /> A typical well design is illustrated as Figure 4 Bonng B5 was grouted from 55 feet below <br /> ground surface to the surface with Portland cement <br /> I3.3 Well Surveying, Monitoring, and Sampling <br /> On February 15, 1994, the tops of the well casings were surveyed relative to an arbitrary <br /> datum of 100 00 feet established on site The datum point is located at the southwest comer <br /> of the structure located on site The elevation of each well casing top, depth to <br /> groundwater, and relative groundwater elevation for all wells is presented in Table 1 The <br /> relative groundwater elevations were calculated from these data <br /> A Solinst water level meter was used to measure depth to water in all monitoring wells on <br /> February 22, 1994 The water level in all wells were measured relative to each notched well- <br /> casing top <br /> After measuring depth to water in all wells, the wells were purged utilizing dedicated PVC <br /> Gww�.l Audit S.-Inc 6 <br /> L rry a Aum Aep..r Q(2"X17 S <br /> I <br />
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