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ARCHIVED REPORTS_FIRST SEMIANNUAL AND 2014 ANNUAL GROUNDWATER MONITORING REPORT
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ARCHIVED REPORTS_FIRST SEMIANNUAL AND 2014 ANNUAL GROUNDWATER MONITORING REPORT
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Last modified
6/22/2020 8:48:42 AM
Creation date
6/22/2020 8:32:43 AM
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
FIRST SEMIANNUAL AND 2014 ANNUAL GROUNDWATER MONITORING REPORT
RECORD_ID
PR0506738
PE
2960
FACILITY_ID
FA0007603
FACILITY_NAME
DEPAOLI DISPOSAL SITE
STREET_NUMBER
3900
STREET_NAME
WHISKEY SLOUGH
STREET_TYPE
RD
City
HOLT
Zip
95234
APN
13109022
CURRENT_STATUS
01
SITE_LOCATION
3900 WHISKEY SLOUGH RD
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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2.RESULTS FOR FIRST SEMIANNUAL PERIOD 2014 <br /> Slough Road toward the sandy sediments southeast of Whiskey Slough Road. The water <br /> table drains from the clayey sediments laterally into the sandy sediments at the band shown <br /> by water table elevation contours-1 foot msl and-8 feet msl. This flow results in a focusing <br /> effect where groundwater in the sandy sediments southeast of Whiskey Slough Road is <br /> naturally directed toward a common area in the vicinity of the two formerly operated <br /> extraction wells,RW-1 and RW-3. <br /> Locally,the former release area is bounded on three sides by a constant head—to the north <br /> and west by Trapper Slough and to the south by the area with standing water. These <br /> boundaries result in locally focused groundwater flow toward the area between the two <br /> access roads(of the former pipeline and the bypass pipeline) that then drains to the <br /> southeast. <br /> Groundwater Analytical Results t <br /> Analytical results for groundwater samples collected on March 5,2014,are presented in <br /> Table 3. TPHg and benzene concentration contours for these data are shown in Figures 4 <br /> and 5, respectively. These data are further presented as follows: <br /> • Appendix C-Tabulated with most recent eight monitoring events <br /> • Appendix D- Time series concentrations charts for wells with consistently detectable <br /> constituents(M-10, N-7,N-8,0-1,N-15, N-16,N-17, and RW-1) <br /> • Appendix E-Long-term trend concentration charts,by expanding the future scale of the <br /> charts in Appendix D to 2050 to better see the long-term concentration trends <br /> Shallow Groundwater <br /> Laboratory analytical results of shallow groundwater samples are consistent with data <br /> reported during previous quarters, as shown in the time-series concentration charts in <br /> Appendix D. The data indicate that the lateral extent of petroleum-affected shallow <br /> groundwater is stable. The downgradient lateral extent of petroleum-affected groundwater <br /> is defined by wells N-18,N-19,and N-20 (petroleum hydrocarbons were not present <br /> above the laboratory reporting limits in these wells). Compounds detected in shallow <br /> groundwater during the first semiannual period 2014 include the following: <br /> • TPHg was detected in shallow groundwater at wells N-7,N-8,N-16,N-17, and RW-1. , <br /> Reported concentrations of TPHg in these wells ranged from 10.70 milligrams per liter <br /> (mg/L) at well N-16 to 12 mg/L at well N-7. <br /> • TPHd was detected in shallow groundwater at wells N-7,N-17, and RW-1. Reported <br /> concentrations of TPHd in these wells ranged from 1.1 mg/L at well RW-1 to 8.7 mg/L <br /> at well N-7. <br /> • BTEX compounds were detected in shallow groundwater at wells N-7,N-8,N-15,N-16, <br /> N-17,0-1,and RW-1. Reported concentrations of benzene in these wells ranged from <br /> 0.61 micrograms per liter (µg/L) at well N-15 to 2,900 gg/L at well N-7. <br /> Deeper Groundwater <br /> No TPHg, TPHd,or BTEX compounds were detected in samples from deeper well N-24. <br /> This is consistent with data reported during previous sampling events. <br /> 2-4 ES041514081714SCO/HOLT_1SA14_TEXT_FINAL <br />
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