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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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EHD - Public
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GROUND WATER MONITORING WORK PLAN • <br /> DREDGE MATERIAL DISPOSAL SITE 1,ROBERTS ISLAND,PORT OF STOCKTON <br /> 3.1.2.1 Boring Locations <br /> The boring locations have been selected based on (1) a local shallow ground water gradient <br /> toward the interior of the island, and (2) land use. Five transects (A, B, C, D, E) consisting of <br /> three borings each are proposed that extend from the surface water body, through DMD1 <br /> (Transects B, C,D), and onto agricultural lands (Figure 4). <br /> Transects A and E are located beyond the limits of the DMD1 and parallel to the expected <br /> ground water gradient direction. Therefore, samples of geologic materials and water collected <br /> from Transect A and E borings are expected to represent background conditions. In addition, <br /> while the borings in Transect A are located close to surface water in the San Joaquin River and <br /> Burns Cutoff, the borings in Transect E increase in distance from the San Joaquin River. <br /> Accordingly, comparing ground water quality along these two transects is expected to differ <br /> due to differences in distance from the recharge zone. <br /> Transects B, C, and D extend in similar fashion across DMD1. The three borings along these <br /> transects are located near the center of DMD1, just beyond the inland levee bounding DMD1, <br /> and approximately 500 feet southwest from DMD1. Locations have been adjusted to allow the <br /> borings to be completed through the local earthen roads and avoid damage to the agricultural <br /> fields. <br /> Another feature of this sampling design is the ability to compare conditions across DMD1 and <br /> equidistant from DMD1 within the agricultural field. Comparing the chemical characteristics of <br /> the various samples is anticipated to adequately indicate if significant impacts to ground water <br /> from DMD1 has occurred. <br /> 3.1.2.2 Boring Advancement <br /> The borings will be advanced using hydraulic direct push equipment to approximately 30 feet <br /> to 40 bgs within DMD1 and to approximately 20 feet to 30 feet bgs beyond of DMD1. These are <br /> estimated maximum depths; the actual boring depth will be determined in the field. The <br /> borings will be advanced into the upper 10 feet of, or to the base of, the first shallow relatively <br /> permeable geologic unit that is at least 2 feet thick and encountered beneath the peat layer, <br /> whichever is less. A relatively permeable geologic unit is anticipated to consist predominantly <br /> of sand or silty sand. Clay layers are not interpreted to represent significant water bearing <br /> units. <br /> The borehole will be advanced sequentially into each of the geologic materials: dredge <br /> materials, foundation soil (including clay and peat layers), and sandy to silty sand aquifer <br /> (Figure 3). Proposed soil and water samples will be collected in the borehole prior to advancing <br /> to the next underlying geologic layer. The geologic materials comprising the Delta Islands, <br /> which are typically dark to black colored layers of clay, silt, and organic rich peat and clay, <br /> January 2005 Page 9 Environmental Risk Services,Corp. <br />
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