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ARCHIVED REPORTS_XR0012741
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3500 - Local Oversight Program
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ARCHIVED REPORTS_XR0012741
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Last modified
2/11/2020 4:50:47 PM
Creation date
2/11/2020 11:57:32 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012741
RECORD_ID
PR0545337
PE
3528
FACILITY_ID
FA0003629
FACILITY_NAME
ARCO STATION #434*
STREET_NUMBER
501
Direction
W
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
03119028
CURRENT_STATUS
02
SITE_LOCATION
501 W KETTLEMAN LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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";a. ;a '^.rs,--5 -.c� -ate. .;"„P�r� <br /> E <br /> Ida <br /> Mr. Kyle Christie <br /> July 16, 1990 <br /> Page 7 <br /> Prior to purging, water-level measurements were taken at each well location (see Figure 1). <br /> Purging, pH, and specific conductivity measurements, sample collection, storage, and <br /> transportation procedures, as well as sample equipment decontamination procedures, were the <br /> same as those used in November and December 1989. All groundwater produced during purging <br /> and sampling was disposed of by Armour. <br /> Field and Analytical Results--January 1990 <br /> The average depth to groundwater beneath the site in January 1990 was 57.54 feet. The <br /> groundwater flow direction was to the southeast under a hydraulic gradient of about 0.002 (10 <br /> feet per mile). <br /> Dissolved BETX concentrations in groundwater samples collected during January 1990 are <br /> included in Table 1. January 1990 benzene concentrations are shown on Figure 1. Complete <br /> laboratory reports of the January 1990 groundwater sample analyses are enclosed as Exhibit A. <br /> January 1990 analytical results show benzene concentrations in groundwater in monitoring wells <br /> W-2, W-2A, W-213, W-3, W-4, W-5,W-6, and W-7 are greater than the California Department <br /> of Health Services (DHS) Maximum Contaminant Level (MCL). Xylene was also above the <br /> DHS MCL in monitoring wells W-2 and W-3 for the January 1990 quarterly sampling. <br /> Ethylbenzene concentration was below its respective MCL. DHS MCLS for benzene, <br /> ethylbenzene, and xylene are 1.0 ppb, 680 ppb, and 1,750 ppb, respectively. Toluene was <br /> identified in concentrations greater than the DHS drinking water action level (action, level) in <br /> monitoring wells W-2, W-2A, and W-3. The action level for toluene is 100 ppb. <br /> Dissolved hydrocarbons (C4 to C12), ranging from <50 ppb to I8,000 ppb, were present in <br /> monitoring wells W-2, W-2A, W-3, W-5, W-6, and W-7 in January I990. <br /> As the water table declined in elevation between July and October 1989, the BETX <br /> concentrations decreased. As the water level returned between October 1989 and January 1990 <br /> f to a higher elevation where the majority of the hydrocarbons are located in the soil, the BETX <br /> e <br /> concentrations increased. <br /> Conclusions <br /> a BETX concentrations in groundwater in on-site and off-site monitoring wells are greater than the <br /> j BETX concentrations identified during the last quarterly sampling in October I989. The <br /> approximate 2-foot increase in the water table since October 1989 has significantly affected <br /> BETX concentrations. The water� table has risen from 2.11 to 2.44 feet_in-the_majority-of the_---- <br /> ----------- <br /> - --- -- -- - groundwater-groundwaterwells. In well W-2B, the water table has risen only 0.69 feet. The <br /> increase in groundwater elevation may have enabled the hydrocarbons adsorbed onto soils in the <br /> capillary fringe zone to re-enter the groundwater. <br /> Brawn and Caldwell <br /> Consultants <br />
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