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ARCHIVED REPORTS_XR0011009
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545039
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ARCHIVED REPORTS_XR0011009
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Last modified
12/10/2019 7:32:18 PM
Creation date
12/10/2019 11:28:03 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011009
RECORD_ID
PR0545039
PE
3528
FACILITY_ID
FA0010186
FACILITY_NAME
DEL MONTE FOODS PLNT #33 - DISCO WH
STREET_NUMBER
110
Direction
N
STREET_NAME
FILBERT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15702009
CURRENT_STATUS
02
SITE_LOCATION
110 N FILBERT ST
P_DISTRICT
001
QC Status
Approved
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KLEINFELDER <br /> I <br /> 4 ACTIVITIES CONDUCTED <br /> Kleinfelder conducted the groundwater sampling for the Fourth Quarter 2004 groundwater <br /> monitoring. Kleinfelder measured water levels in all of the monitoring wells, and sampled 7 <br /> monitoring wells (MW-DIS-11s, MW-DIS-11d, MW-DIS- 12, MW-DIS-13, MW-DIS-14s, <br /> MW-DIS-14d, and MW-DIS-15). All of the wells and piezometers were previously surveyed by <br /> Kjeldson, Sinnock, Neudeck, Inc. (KSN, Inc.) of Stockton, California so groundwater gradients <br /> could be calculated. Data obtained from the wells was used to evaluate groundwater flow, <br /> groundwater impacts and the deed for additional assessment. Additionally, Photo-ionization <br /> detector (PID) samples were taken from vapor extraction well (VE-1) each month during the <br /> Fourth Quarter 2004. Air inlet and outlet sampling was conducted on the thermo/catalytic <br /> oxidizer. <br /> t <br /> 4.1 MEASUREMENT OF WATER LEVELS <br /> f In order to assess the groundwater gradient at the time of sampling, water level measurements <br /> were made in each of the twenty(20) monitoring wells and three (3)piezometers at the beginning <br /> of the sampling round, prior to purging and sampling of the wells (see Record of Water Level <br /> Measurements in Appendix B). The depth-to-water was measured in each well according to the <br /> protocol described in Appendix A, Section A-4.1. The depth-to-water measurements were then <br /> converted to relative groundwater elevations with respect to a surveyed benchmark by subtracting <br /> them from the surveyed casing elevations. <br /> The resulting pertinent groundwater elevations were used to assess the direction of the <br /> groundwater flow and gradient at the time of sampling. This information was then used to assess <br /> which wells represent upgradient and which wells represent downgradient groundwater <br /> conditions. See Table 1 for the groundwater elevation data. <br /> Plates 2 shows the location of the groundwater monitoring wells. Groundwater elevations for the <br /> monitoring wells ranged from—35.72 feet (MW-DIS-6) to —38.00 feet (MW-DIS-15). The depth <br /> to groundwater ranged from 46.54 feet below the top of the well casing (MW-DIS-I Is) to 5 7.6 8 <br /> feet below the top of the well casing (MW-DIS-15). A groundwater gradient and flow direction <br /> r i was calculated based on depth-to-water data collected from the wells on December 20, 2004, <br /> using data collected during a survey produced by KSN Inc. on February 14; 2002. Groundwater <br /> flow direction at the site is estimated to be generally towards the east/northeast with a relatively <br /> flat gradient of approximately 0.0005 ft./ft. This flow direction is a shift from previous <br /> south/southeast flow directions. A groundwater contour map is included as Plate 3. In areas of <br /> relatively flat groundwater gradients such as this site, groundwater flow directions may <br /> significantly fluctuate due to rainfall, groundwater recharge, groundwater pumping, etc. <br /> Therefore, changes in groundwater flow directions may vary at this site with time, however, past <br /> ( data consistently has suggested a similar groundwater gradient and flow direction. <br /> 12280.MON/ST05RI73/7Z:1v Page 6 of 1 <br /> 0 2005,Kleinfelder,Inc. February 11,2005 <br /> I <br />
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