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ARCHIVED REPORTS XR0012278
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ARCHIVED REPORTS XR0012278
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Last modified
11/19/2024 10:19:09 AM
Creation date
9/4/2019 11:17:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012278
RECORD_ID
PR0544801
PE
3528
FACILITY_ID
FA0003210
FACILITY_NAME
TEXACO TRUCK STOP
STREET_NUMBER
7500
Direction
W
STREET_NAME
ELEVENTH
STREET_TYPE
ST
City
TRACY
Zip
95378
APN
25015018
CURRENT_STATUS
02
SITE_LOCATION
7500 W ELEVENTH ST
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Report:Groundwater-quality Monitoring_December 20-2I,2005, 7500 West Eleventh Street, Tracy, Cit. Page 11 <br /> 2.1.1 Groundwater Mound <br /> A significant feature of the groundwater contours shown on Figure 2 is the groundwater <br /> mound centered near Monitoring Well MW-16. The existence of that mound was first <br /> observed in the groundwater measurements made on February 24, 2005 (The San Joaquin <br /> Company 2006c). As was noted at that time, SJC believes that it can be attributed to a <br /> failing septic tank leach field that is located in an area to the east of the Capitol Furniture <br /> building at 7501 West Eleventh Street. <br /> The depth to groundwater in Monitoring Well MW-16 on December 20, 2005 was <br /> measured at 4.05 ft. BGS, which is 2.60 ft, higher than the depth to groundwater last <br /> measured in that well on October 20, 2005. However, the December 2005 amplitude of <br /> the groundwater mound was not as great as when it was first observed in February 2005 <br /> when the depth to groundwater in Monitoring Well MW-16 was only 2.6 ft. The presence <br /> of the groundwater mound remains a striking feature of the groundwater contours in the <br /> area north of West Eleventh Street, as is the highly complex pattern of groundwater <br /> contours to the south of the groundwater mound that were first observed during the <br /> ..r <br /> October 2005 round of groundwater monitoring. <br /> • Despite the continuing presence of the mound of groundwater, at the scale of the site as a <br /> whole, the general direction and gradient of groundwater flow remains to the north- <br /> northeast at approximately 0.003 ft/ft, as generally has been the case throughout the six- <br /> year period that groundwater depths have been monitored at the site. <br /> 2.2 Purging of Groundwater-quality Monitoring Wells <br /> After the depths to groundwater in the seventeen groundwater-quality monitoring wells to <br /> be sampled were measured, a small-diameter, submersible pump was used to purge each <br /> of stagnant water. The pumped water was discharged into 5-gallon pails, each of which <br /> was, in turn, discharged into a 55-gallon drum. The water in the drum was periodically <br /> discharged into a 1,100-gallon holding tank on the 7500 West Eleventh Street property. <br /> During the purging procedure, the temperature and electrical conductivity of the stream <br /> of purge water were monitored by checking those parameters periodically using a multi- <br /> function electronic meter. Purging continued until both parameters stabilized (i.e., <br /> �.. variations between measurements were less than 10%) or, in the case of wells screened <br /> above the water table, until a minimum of 15 gallons of groundwater had been removed, <br /> whichever was greater. The array of parametric results for each well is recorded in SJC's <br /> `l field notes (see Field Notes, Appendix A). <br /> 2.2.1 Disposal of Purge Water <br /> As noted above, purge water extracted from the monitoring wells was discharged <br /> periodically into in a 1,100-gallon storage tank located on the Navarra Site. For economy <br /> ;— and efficiency, water will be held in that tank until it is full. It will then be pumped into a <br /> vacuum truck and transported to a recycling facility, where the petroleum hydrocarbons <br /> sic <br />
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