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2900 - Site Mitigation Program
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PR0503739
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
4/7/2020 2:15:59 PM
Creation date
4/7/2020 2:05:13 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0503739
PE
2951
FACILITY_ID
FA0005956
FACILITY_NAME
ROND PROPERTY TRUST
STREET_NUMBER
7001
STREET_NAME
ROND
STREET_TYPE
RD
City
LODI
Zip
95240
CURRENT_STATUS
02
SITE_LOCATION
7001 ROND RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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y <br /> i Rond Property, Lode <br /> - 2 " August 13, 1943 <br /> San Joaquin County 111 <br /> r <br /> 5. Whether "Middle q 10'" indicates that the sample was collected in the middle of the <br /> excavation, near the middle of the tanks at a depth of 10 feet as assumed and whether "Fill <br /> end ® 10'" indicates the sample was collected at a depth of 14 feet; <br /> 6. The depth of the bottom of the tanks; <br /> 7. The total depth of the excavation; <br /> 8. The presence and locations of domestic or agricultural wells on-site and nearby; <br /> 9. The presence of ground water in the pit during excavation: <br /> 10. The results of any analyses of ground water samples collected from the pit and/or on-site <br /> wells; <br /> I ] . Depth to-ground water; and <br /> 12. Direction of ground water flow. <br /> WHAT WE NEED <br /> 13ceause we lack information about the conditions remaining at the site and the tank itself, we have <br /> nothing on which to base a closure request. Although, in this case not all data may be necessary, <br /> we do need a minimum on which to base our decision. The following information must be provided <br /> to the Board in a single report in order to consider site closure: <br /> 1. The information listed above; <br /> 2. Distance to production wells for municipal, domestic, agriculture, industry and other uses <br /> within 2,000 feet of the site; <br /> 3. Tabulated results of all sampling and analytical results (soil sample locations are to be <br /> marked on a site map); <br /> 4. Site maps, to scale, showing contours, ground water flow directions, buildings, streets, <br /> subsurface utilities, nearby surface waters, locations of former tanks, excavations, monitoring <br /> wells, borings, cone penetrometers; <br /> 5. High and low ground water levels (below ground surface) and historical high; <br /> 6. Extent of soil contamination (and ground water contamination if present); <br /> 7- Methods of cleanup used; <br /> ,g. Zone of influence, area of capture, and area affected by the cleanup methods; <br /> `�. Concentrations remaining on site; and <br /> 10. Rationale why contamination remaining on site will not adversely impact water quality, <br /> health, industry, agriculture, or other beneficial uses. <br /> Board staff concurs with the County request to install three wells as the most sure way to detect <br /> ground water contamination and determine the direction of ground water flow. (To determine the <br /> direction of ground water flow, it is necessary to have at least three measuring points.) Other <br /> methods may be used to detect ground water contamination, however, they are not as comprehensive <br /> and not as reliable. Alternative methods include installation of one monitoring well through the tank <br /> pit and/or area of highest soil contamination or use of cone penetrometer-type instruments such as <br /> The "llydropunch". <br /> ti <br /> r <br />
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