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ARCHIVED REPORTS_XR0007362
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ARCHIVED REPORTS_XR0007362
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Last modified
6/8/2020 12:52:28 PM
Creation date
6/8/2020 12:46:26 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007362
RECORD_ID
PR0545741
PE
3528
FACILITY_ID
FA0006284
FACILITY_NAME
YAMADA BROS INC
STREET_NUMBER
15406
Direction
S
STREET_NAME
TRACY
STREET_TYPE
BLVD
City
STOCKTON
Zip
95206
APN
18917007
CURRENT_STATUS
02
SITE_LOCATION
15406 S TRACY BLVD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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l02 March 2000 <br /> AGE-NC Project No 98-0452 <br /> Page 2 of 5 <br /> 3 1 DRILLING AND SAMPLING <br /> On 23 November 1999, three soil borings were advanced at the site Boring MW-1, MW-2, and <br /> MW-3 were advanced using a CME-75 drill ng All three borings were advanced to a depth of 25 <br /> feet below surface grade (bsg) using 8-inch diameter hollow-stem augers The drill ng and two-man <br /> crew were supplied by Mitchell Environmental Drilling of Sacramento, California Auger returns <br /> generated by drilling were placed on plastic sheeting and stored on site pending laboratory analysis <br /> Soil samples were collected ahead of the dnll bit using a split-tube sampler loaded with three <br /> I pre-cleaned 2-inch by 6-inch brass sleeves The samples were collected at five-foot intervals, <br /> beginning at 5 feet bsg in borings MW-1, MW-2, and MW-3 using a 140-pound hammer to advance <br /> the sampler 18 inches The number of blows required to advance the sampler in 6-inch increments <br /> was recorded on the boring logs Sampling equipment was washed in an Alconox solution and rinsed <br /> with water prior to each sampling run to avoid cross-contamination <br /> IFor each sample,both ends of the leading sleeve were covered with Teflon sheets, capped and sealed <br /> with tape The samples were labeled, stored on ice and transported under chain-of-custody to <br /> • McCampbell Analytical, Inc (MAI), a State of California Department of Health Services (DHS)- <br /> certified analytical laboratory <br /> 32 LOGGING <br /> The soil sample duplicates were utilized for field characterization The soil was screened for the <br /> presence of organic vapor using an organic vapor meter equipped with a photo-ionization detector <br /> (PID Thermo Environmental 580A, 10 OeV, calibrated to isobutylene), and the readings were <br /> recorded on the boring logs Soil was visually described in accordance with the Unified Soil <br /> Classification System (Bonng Logs, Appendix A) <br /> 33 WELL AND BORING COMPLETION <br /> I Borings MW-1, MW-2, and MW-3 were completed as ground water monitoring wells using two- <br /> inch diameter PVC casing with 0 020-inch slotted screen installed from 25 feet to 5 feet bsg with <br /> blank casing extending to the surface The filter pack (No 3 Lonestar sand) was installed from 25 <br /> Ifeet to approximately 3 feet bsg The wells were then developed using a surge block to settle the sand <br /> pack A nominal 2-foot bentonite pellet plug was then installed above the filter pack and hydrated <br /> The wells were then grouted to near the surface with portland cement Water-tight, traffic-rated well <br /> boxes were then installed over the wells The ground water monitoring well design is presented in <br /> • Figure 4 <br /> Advanced GeoEnvironmental,Inc <br /> I <br />
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