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2900 - Site Mitigation Program
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PR0517454
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
1/29/2020 5:29:17 PM
Creation date
1/29/2020 4:00:18 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0517454
PE
2960
FACILITY_ID
FA0013435
FACILITY_NAME
SHELL PIPELINE (FORMER)
STREET_NUMBER
24550
STREET_NAME
HANSEN
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
24550 HANSEN RD
QC Status
Approved
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EHD - Public
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CONESTOGA-ROVERS <br /> &ASSOCIATES <br /> April 5,2011 -3- Reference No.060223 <br /> events,TPHc concentrations in well MW-5B were 740µg/L after the first event,and less than <br /> the TPHc method reporting limit of 250 µg/L after the second event. Similar results were <br /> observed between boring B-66 and well MW-5C where up to 74,000 µg/L TPHc was detected at <br /> 171.5 ft bgs in the depth discrete groundwater sample collected from B-66, and no TPHc has <br /> been detected in well MW-5C at the same depth. As a result,the depth discrete groundwater <br /> analytical data do not agree with the groundwater analytical data collected from wells screened <br /> at the same depths. This further confirms that cross contamination during drilling and <br /> sampling operations is likely the reason for the elevated TPHc detections in the depth discrete <br /> samples. <br /> Based on the above discussion,we believe collecting groundwater samples from a properly <br /> constructed monitoring well will provide more reliable (and repeatable) data than collecting <br /> depth discrete samples during drilling activities. <br /> Installing wells will also allow for evaluating groundwater flow direction and gradient in the <br /> deeper water-bearing zones beneath the site. This approach is also consistent with comment <br /> number 2 in CVWB's 5 November 2010 letter,which states: "The laboratory analytical result of ND <br /> for the groundwater sample colleted from MW-SC preliminarily indicates that the vertical extent of the <br /> TPH release from the pipelines in the vicinity of Trench 3 has been delineated. However, the <br /> groundwater data obtained from B-77 and B-78 in October 2008 shows that the lateral extent of the <br /> pipeline release in the Trench 3 area has not been delineated. Figure 3b in the Work Plan shows that <br /> TPHc has been detected at 570µg/L about 250 east of Trench 3 at a depth of 146 feet bgs. This pollution <br /> could have migrated with the flow of deep zone groundwater because no contaminants of concern were <br /> detected above 100 feet bgs in borings B-77 and B-78. The flow direction of groundwater in aquifers <br /> underlying the shallow zone has not been determined. Additional investigation and monitoring wells are <br /> needed in this area to delineate the lateral extent of COCs below the shallow zone." <br /> The proposed deep well cluster in the vicinity of borings B-77 and B-78 may not define the <br /> plume's extent in the northeasterly direction as CVWB staff suggest. Therefore,the well cluster <br /> will be moved approximately 80 feet further northeast of boring B-78,which should adequately <br /> define the plume's extent in this direction(Figure 1). The screened intervals of the two deep <br /> wells will be constructed to coincide with the water-bearing zones monitored by wells MW-5B <br /> and MW-5C. <br /> Worldwide Engineering, Environmental, Construction, and IT Services <br />
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