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3500 - Local Oversight Program
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PR0544229
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Last modified
3/5/2019 7:48:12 PM
Creation date
3/5/2019 3:42:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0544229
PE
3528
FACILITY_ID
FA0006051
FACILITY_NAME
NOMELLINI CONSTRUCTION COMPANY
STREET_NUMBER
939
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16323046
CURRENT_STATUS
02
SITE_LOCATION
939 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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+..� •*411 <br /> 2.3 Groundwater Depth and Flow Direction <br /> The groundwater depth at the site is approximately 35 feet based upon groundwater depth <br /> measured at the site located at 1045 West Charter Way, also owned by NCC. The <br /> groundwater flow direction at the 1045 West Charter Way site has varied, but currently is <br /> east-northeast. Since the subject site is approximately 2 blocks away from 1045 West <br /> Charter Way, it is assumed that the groundwater flow direction is the same. <br /> 3.0 PROCEDURES <br /> 3.1 Drilling and Sampling <br /> On December 20, 1994, one soil boring was drilled at the site. The boring was drilled near <br /> the center of the former USTs, and advanced to a depth of 30 feet. When drilling was <br /> complete, the boring was backfilled to the surface with Portland Cement. The location of <br /> the boring is shown on Figure 2. <br /> The boring was drilled using a truck-mounted CME 75-HT drill rig. The drill rig and two- <br /> man crew were supplied by Soils Environmental Services (SES) of Benecia, California. <br /> Soil samples were collected at five-foot intervals using a split tube sampler loaded with three <br /> clean, 2-inch by 6-inch brass sleeves. A 140-pound hammer was used to advance the sampler <br /> 18 inches; the number of blows required to advance the sampler in 6-inch increments was <br /> recorded on the boring logs. All sampling equipment was washed in an Alconox solution and <br /> rinsed twice with water prior to each sampling run. <br /> For each sample, both ends of the lead tube were covered with aluminum sheets, capped <br /> and sealed with tape. The samples were then stored on ice and transported under chain-of- <br /> custody to Analytical Bio-Chemistry Laboratories Pan-Ag Division (Pan-Ag) in Madera, <br /> California. <br /> During drilling, auger returns were monitored for the presence of organic vapors using a <br /> photo-ionization detector (PID: Thermo Environmental 580A, 10.0 eV, calibrated to <br /> isobutylene). Auger returns were then placed on plastic sheeting and stored on-site. <br /> 3.2 Logging <br /> Soil was extruded from the second brass tube and screened for the presence of organic <br /> vapors, using a PID, and the readings were recorded on the boring logs. The soil was then <br /> described in accordance with the Unified Soil Classification System (see Boring Log, <br /> Appendix A). <br /> 0-4.S"I A.du S.ry.lac. 4 <br /> Pbmelliai 939 PIEM037/D-1991 <br /> .r <br />
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