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2900 - Site Mitigation Program
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PR0518132
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Last modified
7/10/2019 8:09:04 PM
Creation date
7/10/2019 11:40:49 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0518132
PE
2960
FACILITY_ID
FA0013716
FACILITY_NAME
H & H MARINA
STREET_NUMBER
15135
STREET_NAME
EIGHT MILE
STREET_TYPE
RD
City
STOCKTON
Zip
95219
APN
06908021
CURRENT_STATUS
01
SITE_LOCATION
15135 EIGHT MILE RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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5 • • <br /> 14 August 2003 <br /> AGE-NC Project No. 01-0865 <br /> Page 2 of 6 <br /> 3.1. PERMITTING AND PRE-FIELD WORK PREPARATIONS <br /> Applicable site assessment permits will be obtained from the San Joaquin County Environmental <br /> Health Department(EHD).hi addition,an update to the health and safety plan presently on-file will <br /> be prepared in accordance with Occupational Safety and Health Guidance Manual for Hazardous <br /> Waste Site Activities (National Institute for Occupational Safety and Health Administration, U.S. <br /> Coast Guard and U.S. Environmental Protection Agency, 1985). Prior to mobilization, each probe <br /> boring location will be clearly marked and a utility clearance obtained through Underground Service <br /> Alert. <br /> 3.2. DRILLING AND SOIL SAMPLE COLLECTION AND ANALYSIS <br /> AGE proposes to advance four vertical soil probe borings at the site,using a van-mounted Geoprobe <br /> 5400 direct-push probing unit equipped with 1.25-inch probing rods,to further assess the impact to <br /> soil and ground water from the former UST area.Proposed probe boring locations are illustrated in <br /> Figure 2. <br /> Based on soil contamination encountered in the area of well MW-6 down-gradient of the former <br /> USTs,AGE proposes soil probe borings in the following locations: <br /> • Approximately 10 to 12 feet northwest of MW-6 and a minimum of five feet from the foot <br /> of the retaining wall. This is to further delineate vertical soil and shallow ground water <br /> contamination directly down gradient of the former USTs and up gradient of MW-6. <br /> • Approximately 45 to 50 feet east of MW-6 on the eastern side of the AST enclosure to <br /> further delineate vertical soil and shallow ground water contamination down gradient of the <br /> AST enclosure between MW-6 and MW-7. This boring's location may be modified due to <br /> existing trees and undulating surface topography in the immediate area. <br /> • Approximately 20 to 25 feet northeast of MW-6 on the western side of the ASTs, near the <br /> tank filling station and immediately north of the product piping from the ASTs to the <br /> dispensers. This boring will further delineate vertical and lateral soil and shallow ground <br /> water contamination adjacent to the AST enclosure. <br /> • Approximately 22 to 24 feet northwest of MW-5,this soil boring is to further determine the <br /> lateral extent of contamination in the northern portion of the property up-gradient of MW-5. <br /> Soil boring MW-5 had moderate methyl tertiary butyl ether(MTBE)concentrations detected <br /> in the soil, 1.0 mg/kg in sample MW54 and 0.017 mg/kg in sample MW-5-14; and the <br /> groundwater samples at MW-5 have had elevated amounts of MTBE and total petroleum <br /> hydrocarbons quantified as gasoline(TPH-g)the last three quarters. <br /> Advanced GeoEnvironmental,Inc. <br />
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