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2900 - Site Mitigation Program
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PR0523853
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Entry Properties
Last modified
2/6/2020 9:21:06 AM
Creation date
2/6/2020 8:24:19 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0523853
PE
2965
FACILITY_ID
FA0012794
FACILITY_NAME
STOCKTON PORT DISTRICT
STREET_NUMBER
0
Direction
W
STREET_NAME
HOUSE
STREET_TYPE
RD
City
STOCKTON
Zip
95203
CURRENT_STATUS
01
SITE_LOCATION
W HOUSE RD
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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• . <br /> GROUND WATER MONITORING WORK PLAN <br /> DREDGE MATERIAL DISPOSAL SITE 1,ROBERTS ISLAND,PORT OF STOCKTON <br /> should be readily distinguished from the lighter colored clay, silt, and sand that characterize the <br /> dredge materials. <br /> Standard single wall boring equipment is anticipated to be adequate to advance the boreholes <br /> to the desired depth. Care will be taken to assure that water in overlying dredge materials do <br /> not mix in the borehole with water in the peat layer. Similar care will be taken to assure that <br /> water in the dredge material and peat layer does not mix in the borehole with water in the <br /> sandy aquifer. The primary method of care will include advancing the single wall boring <br /> equipment into the clay underlying the dredge materials and evacuating the water from the <br /> borehole. If water continues to enter the borehole, indicating that an adequate seal between <br /> water bearing units cannot be achieved, then separate boreholes may be advanced to enable <br /> collection of water samples from discrete geologic materials. <br /> If necessary to maintain sample integrity, dual wall boring equipment may be utilized. This <br /> method entails setting the outer wall of the dual wall system in the clay underlying the dredge <br /> sediments to prevent water in the dredge sediments from mixing with water in the underlying <br /> peat. Once the outer wall is set in the clay, the inner wall will be extended to facilitate a sample <br /> of the peat and associated water. Similarly, the outer wall may then be extended into the clay <br /> underlying the peat, and then the inner wall will be extended to the underlying sandy aquifer to <br /> enable collection of samples. <br /> 3.1.2.3 Water Level Measurements <br /> The depth to water encountered in each geologic layer will be measured to the nearest 0.01 feet <br /> using an electric water level probe. Observations of both the depth to saturation and the depth <br /> to the potentiometric or water table surface will be recorded. Repeated measurements will be <br /> made over a period of 5 to 10 minutes to establish the equilibrated depth to water. <br /> Measurements will continue until the depth to water is stable to within 0.05 feet over a 5 minute <br /> period. The purpose of these measurements is to determine possible differences in head <br /> pressures within each geologic unit. Water samples will be collected according to the methods <br /> provided below and after measurements of depth to water are complete. <br /> 3.1.2.4 Soil Sampling <br /> As described above, the borehole will be advanced sequentially into and through each of the <br /> geologic materials: dredge materials, foundation soil and peat, and sandy aquifer. Soil samples <br /> will be collected continuously and described with regard to soil type, relative moisture, and <br /> color in accordance with the Unified Soil Classification System. Soil samples will be collected <br /> within clear acetate tubes lining the inside of the boring equipment. <br /> Once the total thickness of the dredge materials is known, the sample intervals will be <br /> identified according to Table 1 and as depicted in the geologic cross-section schematic on Figure <br /> January 2005 Page 10 Environmental Risk Services,Corp. <br />
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