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ARCHIVED REPORTS XR0007060
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 XR0007060
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Entry Properties
Last modified
7/10/2019 7:34:32 PM
Creation date
7/10/2019 10:19:15 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007060
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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SJGOV\wng
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EHD - Public
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v o <br /> A S S O C I A T E S I N C <br /> In July and August 1999, ATC Associates Inc advanced ten soil borings (Figure 2) to evaluate <br /> the extent of petroleum hydrocarbons and trace amounts of free product detected by SECOR <br /> Soil borings advanced along the levee, southwest of the location of the former USTs and the <br /> current AST location contained elevated concentrations of total petroleum hydrocarbons as <br /> gasoline (TPHg), total petroleum hydrocarbons as diesel (TPHd), and methyl tertiary butyl ether <br /> (MTBE) The extent of impacted soil was defined and generally extended along the backside of <br /> the levee, west of the store The Ariel extent was approximately 200 feet in length and 65 feet in <br /> width and was limited to depths between 5 and 15 feet bgs Additionally, MTBE impacted soil <br /> extended eastward, between the store and office building <br /> The groundwater plume generally extended along the backside of the levee, west of the store, and <br /> was approximately 225 feet long and 70 feet wide Concentrations were highest in the boring <br /> adjacent to the former and current product lines The extent of TPHg in groundwater was not <br /> fully defined to the west and south but samples indicated that the borings in those directions were <br /> near the edge of the plume Additionally, TPHd and MTBE have migrated eastward <br /> GROUNDWATER MONITORING <br /> The fourth quarter groundwater monitoring and sampling of monitoring wells MW 1 through MW5, <br /> and MW7 was conducted by ATC Associates Inc personnel on November 15, 2002 A vehicle <br /> was parked over well MW6 and it was not monitored during this event Water level measurements <br /> were collected from the monitoring wells prior to purging and sampling Well locations are shown <br /> on Figure 2 <br /> Subsequent to monitoring, each well was purged by extracting a minimum of three well casing <br /> volumes of groundwater While purging, groundwater parameters (temperature, conductivity, and <br /> pH) were monitored and allowed to stabilize before water samples were collected Samples were <br /> collected using dedicated, disposable bailers with bottom emptying devices to reduce volatilization <br /> All purged groundwater was contained in 55-gallon drums approved for hazardous liquid storage <br /> on-site pending appropriate disposal Groundwater well purge and sample logs are contained in <br /> Attachment 1 <br /> The groundwater samples collected from each well were placed on ice and transported under <br /> chain-of-custody documentation to Argon Laboratories (ELAP #2359) in Ceres, California The <br /> groundwater samples were analyzed for TPHd, TPHg, benzene, toluene, ethylbenzene, and <br /> xylenes (BTEX) utilizing EPA methods 8015/8020 and total lead utilizing EPA method 200 9 <br /> Fuel oxygenate additives including MTBE were analyzed by EPA method 8260 <br /> RESULTS <br /> Water levels have decreased an average of 0 29 feet since the last monitoring event on August 1, <br /> . 2002 (Table 1) A groundwater gradient map was created using the data collected on November 15, <br /> w lwordpro1625141quanlyl4gr-2002 doc 3 <br />
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