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ARCHIVED REPORTS XR0010894
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2900 - Site Mitigation Program
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PR0505234
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ARCHIVED REPORTS XR0010894
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Entry Properties
Last modified
8/1/2019 3:29:28 PM
Creation date
8/1/2019 2:25:24 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010894
RECORD_ID
PR0505234
PE
2951
FACILITY_ID
FA0001103
FACILITY_NAME
Elkhorn Golf Club
STREET_NUMBER
1050
STREET_NAME
ELKHORN
STREET_TYPE
DR
City
STOCKTON
Zip
95209
CURRENT_STATUS
02
SITE_LOCATION
1050 ELKHORN DR
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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... .. . <br /> rc� 3.0 PROCEDURES <br /> 3.1 Drilling and Sampling <br /> On June 20, 1994, one soil boring (B-1) was drilled at the site. The boring was drilled near <br /> the center of the former underground storage tank (UST), and advanced to a depth of 38 <br /> feet. Because hydrocarbon-impacted soil was encountered during the drilling of B-1, three <br /> monitoring wells were installed at the site. <br /> On August 30, 1994, three additional borings were drilled at the site to depths of 49 feet <br /> and completed as groundwater monitoring wells MW-1, MW-2 and MW-3. The locations <br /> of the borings are shown on Figure 2. <br /> ' I <br /> Each boring was drilled using a truck-mounted CME 75-HT drill rig. The drill rig and two- <br /> man crew were supplied by Mitchell Drilling Environmental (MDE) of Rancho Cordova, <br /> California, <br /> Samples were collected at five-foot intervals in each boring using a split tube sampler Ioaded <br /> with three clean, 2 by 6-inch brass sleeves. A 140-pound hammer was used to advance the <br /> - sampler 18 inches; the number of blows required to advance the sampler in 6-inch <br /> increments was recorded on the boring logs. All sampling equipment was washed in an <br /> Alconox solution and 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 McCampbell Analytical, Inc. (MAI) in Pacheco, CA. <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 /> i 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 Logs, <br /> Appendix A). <br /> 3.3 Well Completion <br /> Borings MW-1, MW-2 and MW-3 were completed as a groundwater monitoring wells using <br /> a 2-inch diameter PVC casing with 0.020-inch slotted screen from 29 to 49 feet. The filter <br /> pack (#3 lonestar sand)was installed from 27 to 49 feet. Bentonite chips were used to make <br /> a two foot plug and the well was grouted to the surface with Portland cement. Boring B-1 <br /> Cmbg"l A.Q&--.Loc 4 <br /> PJkb..MEXOMS.pt L9Lb <br /> f <br />
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