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ARCHIVED REPORTS_XR0006705
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2900 - Site Mitigation Program
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ARCHIVED REPORTS_XR0006705
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Last modified
5/5/2020 10:25:56 AM
Creation date
5/5/2020 9:43:41 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006705
RECORD_ID
PR0543479
PE
2960
FACILITY_ID
FA0024679
FACILITY_NAME
CANEPA'S CAR WASH
STREET_NUMBER
6230
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95204
APN
081360030
CURRENT_STATUS
01
SITE_LOCATION
6230 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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Canepa s Car Wash <br /> 6230 Pacific Avenue,Stockton,CA <br /> Third Quarter Groundwater Monitoring report July 2005 <br /> Page 3 of 8 <br /> GROUNDWATER ELEVATIONS AND GRADIENT <br /> • <br /> Groundwater elevation contours estimated for the shallow monitoring wells MW-1 through MW-7 and <br /> MW-9 through MW-11 on July 28, 2005 indicated a groundwater gradient generally towards the <br /> north/northeast MW-1 is the primary groundwater extraction well for the treatment system, and a cone of <br /> depression related to pumping drawdown at that location is generally observed in the groundwater <br /> elevation contours However, the system was inadvertently shut down the evening prior to the third <br /> quarter monitoring event when a vehicle backed into the enclosure gate, damaged piping on the air <br />' stripper, and tripped the systems emergency shut-off switch As a result, the groundwater surface had <br /> largely recovered to static equilibrium and groundwater elevation contours did not form the localized <br /> cone of depression centered on MW-1 as observed during previous quarterly monitoring events <br /> An estimated groundwater gradient magnitude of 0 0049 ft/ft towards the north/northeast was calculated <br /> using water level data from monitoring wells MW-6 and MW-9 MW-6 and MW-9 are upgradient and <br /> down-gradient, with respect to MW-1 The average groundwater elevation measured in the shallow <br /> monitoring wells for this event decreased by approximately 0 42 feet since April 13, 2005 The <br /> groundwater elevation data for the third quarter sampling event is shown in Table 2, below A hydrograph <br /> of historic groundwater elevations is attached as figure 3 (Attachment A) <br /> Table 2 <br /> Groundwater Elevation Data (July 28, 2005) <br /> Well Casing Screen Well Collar Depth to Water Groundwater <br /> WELL Interval (feet-bgs) Elevation' (feet) (feet) Elevation <br />�. (feet) <br /> MW-1 50-70 1548 3922 -2374 <br /> MW-2 50-70 15 29 3870 -2341 <br /> MW-3 50-70 15 53 3948 -23 95 <br /> MW-4 50-70 15 83 3972 -23 89 <br /> MW-5 50-70 1471 3877 -2406 <br /> MW-6 45-65 1489 37 82 -2293 <br /> MW-7 45-65 1580 3896 -23 16 <br /> MW-9 25-45 1484 3891 -2407 <br />' MW-10 25-45 1472 1 37 86 -23 14 <br /> MW-11 25-45 15 12 39 10 -2398 <br /> MW-12D 100-110 1499 3829 -2330 <br /> Well Collar Elevations are measured from a mark on the top of the well casing and are referenced to GIGS benchmark HS0391 using NAVD 88 <br /> datum <br /> bgs=below ground surface <br /> LABORATORY ANALYTICAL RESULTS <br /> Groundwater samples collected from the monitoring wells and SV-4 were analyzed for total petroleum <br /> hydrocarbons quantified as gasoline (TPH-G) by EPA Method 8015M and benzene, toluene, ethyl <br /> benzene, and total xylenes (BTEX) and selected gasoline oxygenates/additives by EPA Method 8260B by <br /> Excelchem Environmental Labs of Roseville, California (Excelchem) The selected oxygenates/additives <br /> included MTBE, ethanol (EtOH), tertiary-butanol (TBA) di-isopropyl ether (DIPE), ethyl tert-butyl ether <br /> (ETBE), tert-amyl methyl ether(TAME), 1,2-dichloroethane (1,2-DCA), and 1,2-dibromoethane (EDB) <br /> • <br />' CONDOR <br />
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