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COMPLIANCE INFO_PRE 2019
Environmental Health - Public
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PR0505986
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COMPLIANCE INFO_PRE 2019
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Last modified
5/14/2019 11:42:08 AM
Creation date
11/1/2018 12:48:03 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
PRE 2019
RECORD_ID
PR0505986
PE
2220
FACILITY_ID
FA0005785
FACILITY_NAME
SFPP LP (STOCKTON TERMINAL)
STREET_NUMBER
2947
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
14503010
CURRENT_STATUS
01
SITE_LOCATION
2947 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\N\NAVY\2947\PR0505986\COMPLIANCE 1988 - 2015.PDF
QuestysFileName
COMPLIANCE 1988 - 2015
QuestysRecordDate
9/8/2017 8:18:45 PM
QuestysRecordID
3631569
QuestysRecordType
12
QuestysStateID
1
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EHD - Public
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SUR 0 • <br /> ' ground surface on approximately 20-foot centers. As observed during the site visit on <br /> ' July 24, 2006 with San Joaquin County personnel, limited residual petroleum <br /> hydrocarbon-impacted soil remains present beneath the concrete containment pad beneath the valve <br /> assembly. This soil was not excavated in order to avoid compromising the integrity of the pad. To <br /> assess concentrations of residual hydrocarbons present in soil immediately beneath the concrete <br /> pad, 4 soil samples were collected from beneath each of the excavation sidewalls of the concrete <br /> pad. <br /> Confirmation soil samples were collected in 2-inch-diameter brass liners using hand-sampling <br /> equipment. Upon collection, each sampling container was immediately capped, labeled, and placed <br /> ' into an ice-chilled cooler. <br /> Decontamination of reusable sampling equipment was conducted using the following procedures: <br /> ' • non-phosphate detergent and tap water wash, in a 5-gallon plastic bucket, using a brush <br /> ' • deionized/distilled water rinse, in a 5-gallon plastic bucket <br /> • decontamination water was transferred to the onsite oil-water separator <br /> Two groundwater samples, designated GW-1 and GW-2, were collected from the water table <br /> immediately beneath the floor of the excavation (Figure 2). At both locations, a boring was hand- <br /> advanced to approximately 24-inches below the floor of the excavation and a 0.01-inch screened <br /> PVC casing set. No product was observed in these temporary wells. Once static water levels were <br /> established at each location, a total of three casing volumes were purged by hand bailing using a <br /> ' new, unused disposable bailer. Groundwater samples were collected directly from the bailer into <br /> laboratory-supplied, 40-milliliter volatile organic analysis (VOA) vials. Water produced during <br /> groundwater sampling activities was transferred to the on-site oil-water separator for processing. <br /> ' Collected soil and groundwater samples were delivered to Alpha using strict chain-of-custody <br /> protocol and analyzed for TPH-DRO, TPH-GRO, and TPH - Jet Fuel Range Organics (TPH- <br /> ' JFRO) using EPA Method 8015M and BTEX compounds, MTBE, DIPE, ETBE, TAME, and <br /> TBA using EPA Method 8260B. <br /> ' Results of Remedial Response and Soil Sampling Activities <br /> ' Product Sample Results <br /> Analytical results for the product sample collected on July 24, 2006 indicated that the product <br /> ' present in the collected samples was comprised of approximately 50-percent TPH-DRO and 50- <br /> percent TPH-GRO. These data confirm that a transmix interface was released from the back- <br /> pressure valve on July 24, 2006. <br /> ' 5 <br />
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