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ARCHIVED REPORTS XR0002723
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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HARDING
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3500 - Local Oversight Program
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PR0544425
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ARCHIVED REPORTS XR0002723
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Entry Properties
Last modified
5/6/2019 3:00:43 PM
Creation date
5/6/2019 2:54:31 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002723
RECORD_ID
PR0544425
PE
3528
FACILITY_ID
FA0006249
FACILITY_NAME
VILLAGE PROPERTIES
STREET_NUMBER
140
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
13707051
CURRENT_STATUS
02
SITE_LOCATION
140 HARDING WAY
P_DISTRICT
001
QC Status
Approved
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SJGOV\wng
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EHD - Public
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3. 0 PROCEDURES <br /> ' 3. 1 Drilling and Sampling <br /> Borings B17 and B18 and monitoring well MW-5 were drilled on August <br /> ' 25 and 26, 1993 . The 2-man drilling crew and truck-mounted drill <br /> rig equipped with 8-inch-diameter hollow-stem augers were provided <br /> by West Hazmat Drilling Co. of Rancho Cordova, California. In order <br /> to investigate the northern extent of soil contamination in the <br /> ' vicinity of 14W-4 , boring B17 was drilled at an angle of 300 from <br /> vertical and bottomed at a depth of 38 feet, approximately 5 feet <br /> north of the sidewalk on the south side of Harding Way (Figure 2) . <br /> ' Boring B18 investigated the southern extent of the contamination <br /> detected in MW-4 , and was continuously cored from a depth of 20 to <br /> 40 feet. The core was screened for volatile organic vapors using a <br /> portable photo-ionization detector (PID model OVA-580A calibrated <br /> ' to isobutylene) and the readings were recorded on the boring log. <br /> Samples were collected from the core at approximately 5-foot <br /> intervals, and -each sample was packed into a 6-inch brass tube, <br /> ' capped, and sealed. A center line was then scribed down the core, <br /> and the core was described on the boring log in accordance with the <br /> Unified Soil Classification System. <br /> Mr In MW-5 and B17 , soil samples were collected- at 5-foot intervals, <br /> starting at a depth of 20 feet. A 140-pound down-hole hammer was <br /> used to advance a split-tube sampler loaded with three brass <br /> sleeves. The number of blows required to advance the sampler 18 <br /> inches was recorded on the boring log (Appendix A) . Samples were <br /> screened for volatile organic vapors using a PID and the readings <br /> ' were recorded on the boring log. The ends of the sample tube were <br /> then covered with sheets of aluminum foil, capped, and sealed with <br /> tape. Samples were labelled, logged on the boring log and chain of <br /> custody form, and placed on ice until delivery to McCampbell <br /> Analytical for analysis. Soil in the middle and upper tubes was <br /> extruded and described on the boring log. To avoid contamination of <br /> subsequent samples, the tubes and sampler were then triple-rinsed <br /> in a phosphate solution; the augers were steam-cleaned between <br /> borings. <br /> 3 .2 Well Completion <br /> MW-5 was completed by the installation of . 020-inch slotted PVC <br /> casing from 60 feet to 40 feet. The well was manually developed for <br /> approximately 20 minutes to tighten the sand pack, which settled <br /> approximately 1. 5 feet. Details of the well design are shown on the <br /> boring log. Borings B17 and B18' were grouted with a slurry of <br /> ' Portland cement from total depth to surface. <br /> 3 . 3 Well Monitoring and sampling <br /> The elevation of MW-5 was surveyed on August 27, 1993 . The top of <br /> the casing was surveyed relative to the casing in MW-1. A permanent <br /> ' 4 <br />
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