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ARCHIVED REPORTS_2012_6
Environmental Health - Public
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ARCHIVED REPORTS_2012_6
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Last modified
7/17/2020 7:24:10 PM
Creation date
7/3/2020 11:05:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2012_6
RECORD_ID
PR0440003
PE
4434
FACILITY_ID
FA0003698
FACILITY_NAME
CORRAL HOLLOW LANDFILL
STREET_NUMBER
31130
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25303010
CURRENT_STATUS
01
SITE_LOCATION
31130 CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4434_PR0440003_31130 CORRAL HOLLOW_2012_6.tif
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EHD - Public
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standards outlined in the EMP Workplan. Groundwater samples were retained for <br /> submittal to a chemical analytical laboratory following well development. <br /> Data loggers were deployed in the sounding ports of the wells and were used to record <br /> water levels during well development and post development recovery. Stored data <br /> were downloaded onto a portable computer and well recovery analyses were <br /> performed to calculate the hydraulic conductivity of the aquifer materials. <br /> f surging the well screen to loosen fine sand silt and clay <br /> Well development consisted o su g g Y <br /> ' and bailing groundwater from the well to remove sediment, induce formational water <br /> flow into the well, and reduce the turbidity of the water. Select monitoring parameters <br /> were measured and recorded in the field as water was bailed from the well. <br /> Development was considered complete when the monitoring parameters stabilized and <br /> turbidity was reduced to an acceptable level (approximately 5 NTU). <br /> Development Method —The Phase II monitoring wells were developed using a bailer <br /> equipped with a rubber gasket to surge groundwater through the screened section of <br /> the well. The gasket was approximately the same size as the inside diameter of the well <br /> casing, effectively forcing water through the screen to loosen fines and induce <br /> formational water into the well. Each well screen was surged in 18-inch increments <br /> over the course of 25 to 35 minutes until the entire saturated portion of the well screen <br /> was surged. After surging was completed, groundwater was bailed from the well and <br /> retained in a 55-gallon drum. Volumes of water removed from the wells were <br /> ' calculated by measuring the height of water in the drums. <br /> Monitoring Parameters - A Horiba U52 water quality meter was used in the field to <br /> ' measure indicator parameters at graduated volumes. The following indicator <br /> parameters were recorded: <br /> • Temperature (degrees Celsius) <br /> • pH (units) <br /> • Oxidation Reduction Potential (milliVolts) <br /> • Electrical Conductivity (millimhos/centimeter) <br /> • Turbidity (Nephelometric Turbidity Units) <br /> ' Groundwater was bailed from the wells until the indicator parameters stabilized. Due to <br /> problems caused by rainy conditions in the field, turbidity was only recorded in well <br /> MW-9A. Wells MW-10A and MW-11A were developed until relatively clear water was <br /> removed from these wells and all other indicator parameters stabilized. <br /> ' Development Log-A log of well development was recorded in the field. The following <br /> information was included on each log sheet: <br /> EMP Report—Phase IIGeo-Logic Page ■ 13 <br /> Corral Hollow Sanitary Landfill ASSOCIATES <br /> August 21,2012 <br />
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