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2900 - Site Mitigation Program
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PR0537618
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Last modified
11/20/2024 8:49:43 AM
Creation date
6/15/2020 3:12:05 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0537618
PE
2950
FACILITY_ID
FA0021662
FACILITY_NAME
ORLANDO'S MARKET
STREET_NUMBER
18754
STREET_NAME
STATE ROUTE 26
City
LINDEN
Zip
95236
APN
10517048
CURRENT_STATUS
01
SITE_LOCATION
18754 HWY 26
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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18 July 2013 <br /> AGE Project No. 12-2466 <br /> Page 2 of 4 <br /> dispenser area; borings B4 through B6 were advanced to depths of 20 feet bsg near the <br /> UST area and borings 1310 and 1311 were advanced to depths of 18.5 feet bsg near the <br /> oil/water separator. Soil boring locations are illustrated in Figure 2 and Appendix A. <br /> Soil borings were advanced utilizing a truck-mounted AMS Powerprobe drill-rig equipped <br /> with 1.25-inch diameter probing rods. The AMS powerprobe uses a hydraulic hammer to <br /> drive sampling tools to specified depths. <br /> SOIL SAMPLE COLLECTION AND ANALYSIS <br /> Soil samples were collected from borings B1, B2, B3, B7, B8 and B9 at 5 feet and 10 feet <br /> bsg, from borings B4, B5 and B6 at 10 feet, 15 feet and 20 feet bsg, and from borings 1310 <br /> and 1311 at 13.5 feet and 18.5 feet bsg, using a 1.5-inch diameter macro-core sampling <br /> assembly loaded with one 4-foot long acetate liner. After collection, 6-inch portions of the <br /> continuous samples selected for analysis were separated, the ends covered with Teflon <br /> sheets, capped and sealed with tape. Soil samples were labeled with soil boring location, <br /> depth, time, date and sampler's initials and then placed in a chilled container. Soil samples <br /> were transported under chain-of-custody to Cal Tech Environmental Laboratories (CTEL) <br /> a State of California Department of Public Health-certified analytical laboratory. Selected <br /> samples were analyzed for: <br /> • Total petroleum hydrocarbons as gasoline, diesel and motor oil (TPH-g, TPH-d, <br /> TPH-mo) in accordance with EPA Method 8015 Modified (131 through 1311); and <br /> • Volatile organic compounds (VOCs) in accordance with EPA method 8260B (131 <br /> through B9 only). <br /> Soil sample duplicates were extruded into plastic bags and field-screened for the presence <br /> of organic vapors using an organic vapor meter (OVM), equipped with a photo-ionization <br /> detector (PID). Additionally, the soil was visually classified in accordance with the Unified <br /> Soil Classification System (USCS). PID readings and soil classifications were recorded on <br /> boring logs, provided in Appendix B. <br /> EQUIPMENT DECONTAMINATION <br /> Prior to sample collection, soil sampling equipment was thoroughly rinsed with clean water <br /> after being washed with a solution of Alconox. Powerprobe rods were thoroughly cleaned <br /> prior to soil probe boring advancement. <br /> Advanced Geo Environmental,Inc. <br />
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