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PR0524190
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Last modified
4/3/2020 2:03:19 PM
Creation date
4/3/2020 1:57:05 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0524190
PE
2965
FACILITY_ID
FA0016241
FACILITY_NAME
STOCKTON REGIONAL WATER CONTROL FAC
STREET_NUMBER
2500
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16333003
CURRENT_STATUS
01
SITE_LOCATION
2500 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Work Plan and Time Schedule for Analyses of Background Groundwata Quality <br /> City of Stockton Regional Wastewater Control Facility <br /> Page 9 <br /> Analysis Plan (revised) in Appendix 4. Vehicular access to all proposed Geoprobee boring and sampling <br /> sites is possible by following established paved and unpaved roads(Figure 5). The rationale for the sampling <br /> locations is described below. <br /> 9.1.1 Oxidation Ponds Background Groundwater Quality Sampling <br /> To assess natural background variability, groundwater samples will be collected at nine (9) sites over a <br /> wide area south of the current ponds. Proposed sample sites labeled El through E9 are located southwest <br /> of MW-15 as shown on Figure 5. Additional samples will be collected at four (4) sites in an array west <br /> (downgradient) of the ponds shown as sites E10 through E13 on Figure 5. In order to correlate grab <br /> samples at these locations to the monitoring well data, identical sample procedures will be conducted at <br /> each of the monitoring wells located outside the groundwater interceptor system. These sample sites are <br /> designated as W3, W15, W18, W7, and W16 on Figure 5. All data from these areas will be statistically <br /> evaluated across all samples combined with samples grouped by depth and area. These data will be used <br /> to determine whether background water quality values can be applied to all COC or whether intra-well <br /> comparison must be used. <br /> 9.1.2 Eastside Background Groundwater Quality Sampling <br /> To assess spatial variability along flow paths east of the SJR, samples will be collected along four <br /> transects, designated as A, B, C and D. These are shown on Figure 6. Transect A will evaluate <br /> groundwater along a flow path from MW-11. Transect B will evaluate groundwater along a flow path <br /> from MW-14. Transect C will evaluate groundwater along a flow path removed from the facility and will <br /> be used to represent background conditions. Transect D includes samples that are approximately <br /> equidistant from the river and will provide an opportunity to test degradation rates derived from the other <br /> transects. Transects A,B, and D include grab sampling pairs at well locations. As in the Oxidation Ponds <br /> Background program, these samples provide an opportunity to correlate grab sampling with the longer <br /> monitoring histories at each monitoring point and to assess the impact screen submergence can have on <br /> background thresholds. <br /> 10.0 WEST SIDE UPGRADIENT MONITORING NETWORK <br /> 10.1 HOLLOW STEM AUGER WELL INSTALLATION PROGRAM <br /> Hollow stem drilling methods will be employed to install additional groundwater monitoring wells. <br /> Drilling permits will be obtained from the SJCEHD prior to drilling and the areas will be marked for USA <br /> 72 hours prior to drilling. A site specific health and safety plan has been prepared(Appendix 5) and will <br /> be reviewed and signed by all field workers prior to commencing activities. The work will be completed <br /> by a C-57 licensed contractor under the supervision of a field geologist working under the direct <br /> supervision of a California Professional Geologist. Drilling equipment will be cleaned between borehole <br /> locations. Cuttings will be discharged to the surface near the boring locations. Vehicular access to all <br /> proposed monitoring well locations is possible by following established paved and unpaved roads(Figure 7). <br /> Wells will be completed in accordance with typical completion diagrams provided on Figure 8 and Figure <br /> 9. Any filter sands used in construction must not generate high saline solutions when mixed with water. A <br /> saturated paste extract from construction sand and tap water must not result in an electrical conductivity <br /> measurement greater than 500 uS/cm. Each batch of sand brought to the construction site will be field <br /> tested by the supervising geologist. At least 48 hours after well completion, the wells will be developed <br /> by surging and bailing until the water is clear to the unaided eye. Development water will be discharged <br /> to the surface near the wells. Sample collection and shipping methods are described in the Sampling and <br /> Analysis Plan(revised) in Appendix 4. The wells will be surveyed by a licensed surveyor to GeoTracker <br /> standards.The rationale for the sampling locations is described below. <br /> A <br /> ti� COND <br />
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