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ARCHIVED REPORTS XR0007040
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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EIGHT MILE
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11530
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2900 - Site Mitigation Program
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PR0541077
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ARCHIVED REPORTS XR0007040
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Entry Properties
Last modified
7/10/2019 11:58:59 AM
Creation date
7/10/2019 10:11:34 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007040
RECORD_ID
PR0541077
PE
2960
FACILITY_ID
FA0023517
FACILITY_NAME
PS MARINA 5 / KING ISLAND RESORT
STREET_NUMBER
11530
Direction
W
STREET_NAME
EIGHT MILE
STREET_TYPE
RD
City
STOCKTON
Zip
95219
APN
07119006
CURRENT_STATUS
01
SITE_LOCATION
11530 W EIGHT MILE RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Jul -07-99 02 : 43P Larry Button 916-689-6577 PC)2 <br /> 1.9 UST REMOVAL SAMPLE SUMMARTY <br /> 1.1 Site History and Description <br /> This site is known as Kung Island Resort, located at 11530 West Eight Mile <br /> Road in Stockton, California The site is IoLated on the Fast Side of levee � <br /> The site currently has a main structure, which is operated as a small market, <br /> as well as numerous slits for docking boats (Figure 1) On March 9, 1999 <br /> two UST's were removed from the site The two tanks. a 6,000-gallon which <br /> contained gasoline and 4,000-gallon that also continued gasoline, but had <br /> once contained diesel The surrounding area k Lonipri,,ed primarily cif light <br /> commercial and residential <br /> 1.2 Site Summary <br /> Two diesels UST's were removed from the site on March 9, 1999 <br /> Six wil samples were collected, four of the samples were collected beneath <br /> the two tanks The other two samples were collected from soils stacked to <br /> the side of the tank pit <br /> All samples from under the diesel tank were analyzed by EPA Method 8015 <br /> • for Total Petroleum Hydrocarbon as gasoline (TPHgas),EPA Method 8020 <br /> for Benzene, Toluene, Ethylbenzene and Xylenes (B rEX) by EPA Method <br /> 8260 oxygenates which included Tertiary Butyl Alcohol {TBA), Di- <br /> isopropyl Ether (DIPS), Merhyl 1'ernary Butyl Fther(MTBE), Ethyl Ternary <br /> Butyl Ether(E,IBE), Tertiary Amyl Methyl Ether (TAME:) and 1,2- <br /> Dichloroethane, and EPA Method 6010 for total lead All samples except <br /> 99-King 405 and 99-King-006 were analyzed by EPA Method 5015 for <br /> Total Petroleum hydrocarbon as diesel('1 PHdiesel) All analytical data has <br /> been summarized in Table 1 and 2 <br /> The results of the soil samples were below detection limits for both EPA <br /> Method 8015 for Total petroleum Hydrocarbon as gasoline ('i Pligas), and <br /> EPA Method 8020 for Benzene, Toluene, Ethylbenzene and Xylenes <br /> (BTEX). <br /> However,the results of the soil samples showed elevated level% for both <br /> EPA Method 8015 for l otal Petroleum Hydrocarbon as dtescl ('I Plldiesel), <br /> and EPA Method 8260 oxygenates which inLluded Tertiary Butyl Alcohol <br /> (113A), Di-isopropyl Ether (DIPS) Methyl Ternary Butyl Ether (M'[ BF), <br /> Ethyl Ternary Butyl Ether (FTAF.), Tertiary Amyl Methyl Fther (TAME) <br /> and 1,2-Dichloroethane 99-King-001, 99-King-003, and 99-King-004 <br /> ranged Irom 2 3-33 0 mg/kg for TPHdiesel 99-Kang-006, 99-King-005- and <br /> 99-King-002 ranged from 2 0-0 12 mg/kg for MTBE by F PA method 8260 <br /> i <br /> 1 <br />
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