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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544294
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
3/29/2019 4:12:13 PM
Creation date
3/29/2019 4:04:35 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0544294
PE
3528
FACILITY_ID
FA0007044
FACILITY_NAME
SAFEWAY MEAT PROCESSING PLANT
STREET_NUMBER
1111
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16326007
CURRENT_STATUS
02
SITE_LOCATION
1111 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
WNg
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EHD - Public
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i <br /> CHRONOLOGY <br /> SAFEWAY MEAT PROCESSING PLANT <br /> 1111 NAVY DRIVE <br /> STOCKTON, CA 95203 <br /> 01/30/87 Tank #2 leak discovered during tank test. <br /> 02/05/87 Unauthorized Release Report (UAR) filed. <br /> 04/07/87 Soil borings B-1 to B-9 were advanced around the tank area. <br /> Soil samples were collected and analyzed. Highest results <br /> were 1, 100 mg/kg of TPH from B-2 sample at 20.7 feet below <br /> surface grade (bsg) . <br /> 07/07/87 Four 12, 000 gallon diesel underground storage tanks (USTs) <br /> State ID #6445001, 6445002, .6445003, 6445004 were removed <br /> and transported to H & H Ship Service Company, 220 China <br /> Basin Street San Francisco, and disposed to Sanitary Land <br /> Fill, San Francisco. A concrete slab was beneath the USTs, <br /> at about 13.5 feet bsg. Water entered the excavation and <br /> was about 9 feet bsg. A grab water sample was collected. <br /> Only Xylene at 1.1 ug/1 was detected. A Prop-65 was filed. <br /> 08/12/87 3 monitoring wells MW-1 to MW-3 were installed around the <br /> former tank area. Analytical results of the soil samples <br /> collected were non detect. The boring logs indicate water <br /> was at about 18 feet bsg. Monitoring well screens were MW1 <br /> 25 to 35 feet, MW2 23 to 33 feet and MW3 25 to 35 feet. <br /> Gradient was to the northwest. Analytical results of the <br /> water samples from the wells were non detect. <br /> 01/22/88 Five soil samples were collected from the sidewalls of the <br /> excavation. Analytical results showed the highest <br /> concentration of TPH was in the southwest corner of the <br /> excavation (3700 ppm) . <br /> 1/23-24/88 750 cubic yards of pea gravel- (that had been placed back in <br /> the excavation after the USTs were removed) were removed <br /> from the excavation and placed elsewhere on the site for <br /> aeration with other soil generated during the UST removal. <br /> 03/14/88 Two soil samples were collected from the sidewalls of the <br /> excavation. The sample from the northeast corner of the <br /> excavation was non detect for contaminants. The sample from <br /> the southwest corner was 420 ppm. <br /> 03/17/88 Soil samples (8-11)were collected beneath the cement slab at <br /> the bottom of the excavation after coring through the. slab. <br /> Only four of the samples were analyzed and the highest <br /> concentration of TPH was in SL-D (56 ppm) . It was decided <br /> that the contamination was around the perimeter of the slab <br /> not beneath it so the concrete slab was allowed to remain in <br /> place. <br /> 7/26-28/88 150 cubic yards of contaminated soil were excavated along <br /> the southern and western walls of the existing tank pit as- <br /> deep as 24 feet bsg and placed with the other stockpiled <br /> soil and pea gravel, bringing the combined volume of pea <br /> gravel and stockpiled soil to 1,200 cubic yards. Eight <br /> soil- samples were collected from the excavated area. The <br /> highest concentration was 3700 ppm in TP21-15 from the <br /> southwest .part of the excavation. Water was 23 feet bsg. <br />
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