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ARCHIVED REPORTS_2008_14
Environmental Health - Public
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ARCHIVED REPORTS_2008_14
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Last modified
7/17/2020 3:53:28 PM
Creation date
7/3/2020 10:53:28 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2008_14
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2008_14.tif
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EHD - Public
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was present to collect samples from lysimeters W-2, LY-A, and LY-BG1. Of note, <br /> lysimeter D-01 has been buried and lysimeters E-1, LY-E 1 A, LY-EIB, LY-E2A, <br /> LY-E2B, FU-03, and WMU D-02 appear to be damaged since they can no longer hold a <br /> vacuum. <br /> A single sample set was collected from each point containing sufficient liquid and <br /> submitted to BC Laboratories, Inc. (BC)of Bakersfield, California, a state certified <br /> laboratory under contract to Forward. During the third quarter 2008 monitoring period, <br /> samples were analyzed for the routine monitoring parameters stipulated in RWQCB <br /> Order No. R5-2003-0049. In addition, well MW-24 was sampled for the five-year list of <br /> constituents of concern(COCl), and confirmation samples were collected from well <br /> MW-2A for chlorinated herbicides. Table 2-1 summarizes site monitoring parameters, <br /> analytical methods, and monitoring frequency. Water quality samples were also analyzed <br /> in the field for dissolved oxygen, turbidity, temperature, specific conductance, and pH <br /> and recorded on well data sheets. The groundwater monitoring wells, surface water <br /> monitoring points, and leachate monitoring points were sampled in accordance with the <br /> sampling and analysis procedures detailed in Appendix B. The well data sheets, <br /> laboratory data, certificates of analyses, and chain-of-custody records for the sampling <br /> program are included in Appendix C. The laboratory analyses and field results for <br /> groundwater monitoring wells, surface water stations, lysimeter and leachate sampling <br /> stations are summarized in Tables 2-2 through 2-8. <br /> 2.1.2 QA/QC Results <br /> The quality assurance/quality control (QA/QC)program completed for the third quarter <br /> 2008 water quality monitoring event included analyses of five field blanks, five trip <br /> blanks, five laboratory method blanks, two equipment blanks, and one duplicate sample. <br /> The trip, field, and laboratory method blanks were analyzed for volatile organic <br /> compounds (VOCs)by EPA Method 8260. Laboratory method blanks were analyzed for <br /> all of the analytes included in the monitoring program. The results of the QA/QC <br /> program indicate that acetone, bis(2-ethylhexyl)phthalate, bromoform, <br /> dibromochloromethane, methylene chloride, and t-butyl alcohol were detected in one or <br /> more of the QA/QC blanks during the monitoring period. Review of the primary sample <br /> results indicates that a similar concentration of acetone, bis(2-ethylhexyl)phthalate, and <br /> t-butyl alcohol were detected in several of the primary samples collected during the <br /> monitoring period and were flagged as suspected field/laboratory contaminants. During <br /> the third quarter 2008 monitoring event, a duplicate sample was collected from well <br /> MW-17 and labeled DUP. As shown on Table 2-2, the duplicate sample analyses yielded <br /> good correlation (within 10%)with the primary sample results. Of note, concentrations <br /> less than the practical quantitation limit(PQL)were not included in the duplicate <br /> comparison, since these are estimated values. <br /> Review of third quarter 2008 sampling dates and laboratory analytical certificates <br /> indicates that with the exception of the nitrate as nitrogen concentrations measured in two <br /> lysimeter samples, the laboratory analyses were completed within required holding times. <br /> The holding times for nitrate as nitrogen was missed by less than 1 hour and are believed <br /> D:\2M_001"A 3".doc <br /> 4 Geologic Associates <br />
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