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2900 - Site Mitigation Program
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PR0541800
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Last modified
3/16/2020 4:49:55 PM
Creation date
3/16/2020 2:00:11 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0541800
PE
2960
FACILITY_ID
FA0023969
FACILITY_NAME
CANCUN RESTAURANT
STREET_NUMBER
135
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
13908010
CURRENT_STATUS
01
SITE_LOCATION
135 E MINER AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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26 September 2008 <br /> AGE-NC Project No. 07-1587 <br /> Page 2 of 7 <br /> 2.2. SOIL SAMPLE COLLECTION AND ANALYSIS <br /> Samples were collected from the borings at discreet 5-foot intervals using a 1.25-inch Geoprobe soil <br /> sampling assembly loaded with four six-inchbrass sleeves.For each soil sample collected,both ends <br /> of the second or other selected sleeve were covered with Teflon sheets,capped,and sealed with tape. <br /> Samples were labeled, stored on ice and transported under chain-of-custody to Cal Tech <br /> Environmental Laboratories (CTEL) a State of California Department of Public Health (CDPH)- <br /> certified analytical laboratory. Selected samples were analyzed for: <br /> • Total petroleum hydrocarbons as gasoline(TPH-g)and as diesel(TPH-d)in accordance with <br /> EPA Method 8015 Modified; and <br /> • Benzene,toluene,ethylbenzene and total xylenes(BTEX)and the fuel additives methyl-tert- <br /> butyl ether (MTBE), tertiary butyl alcohol(TBA), di-isopropyl ether(RIPE), ethyl tertiary <br /> butyl ether (ETBE), tertiary amyl methyl ether (TAME),1,2-dibromoethane (EDB) and <br /> 1,2-dichloroethane (1,2-DCA)in accordance with EPA Method 8260B. <br /> Additionally, soils were screened for the presence of volatile organic compounds using an organic <br /> vapor analyzer(OVA)equipped with a photo-ionization detector(PID)calibrated to an appropriate <br /> isobutylene standard.All sampling equipment was washed in an Alconox solution and rinsed twice <br /> with water prior to each sampling run. All rinseate generated by drilling-related activities was <br /> containerized in properly labeled department of transportation (DOT)-approved 55-gallon drums, <br /> and was stored on-site in an area lacking public access. All soil borings were backfilled over their <br /> entire depth with either a Portland cement grout mix or a Portland cementibentonite slurry. <br /> 2.3. SOIL LOGGING <br /> After sample preservation, soil was extruded from the remaining sleeves. Soils were visually <br /> classified by an AGE geologist in accordance with the Unified Soil Classification System(USCS). <br /> Soil boring logs exhibiting soil profiles are depicted in Appendix C. <br /> 2.4. GRAB GROUND WATER COLLECTION AND ANALYSIS <br /> After collecting three observed saturated samples, the ground water table was measured and <br /> observed to be between approximately 17 to 22 feet bsg. Two `grab' ground water samples were <br /> collected from the borings; the first at the water table (labeled as GWI) and the second from the <br /> maximum depth of each boring at approximately 55 to 60 feet bsg (labeled as GWII). B2 was an <br /> exception with just one `grab' ground water sample collected from the GWII interval.Ground water <br /> Advanced GeoEnvironcnental,Inc. <br />
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