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SITE INFORMATION AND CORRESPONDENCE_FILE 1
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0506171
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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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Last modified
1/9/2020 4:31:53 PM
Creation date
1/9/2020 4:19:31 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0506171
PE
2950
FACILITY_ID
FA0003863
FACILITY_NAME
SOHAL #3
STREET_NUMBER
2494
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15328008
CURRENT_STATUS
02
SITE_LOCATION
2494 E FREMONT ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Shell station page 2 <br /> 2494 E. Fremont St., Stockton. <br /> In addition, the concentrations of 1,2-DCA detected in the groundwater samples <br /> from S131 are similar to those found around Shell's site in SB-4, SB-7, SB-8, <br /> SB-9 and SB-10. Soil data that shows a source area or repeated groundwater <br /> sample data that supports the idea that 2491 Fremont Street had a petroleum <br /> leak from the former UST system is required before EHD can direct the owners <br /> of 2491 Fremont to perform investigation of a leak at their site. <br /> Shell must install monitoring wells north of their site in appropriate zones to <br /> delineate their plume of contaminated groundwater. Well screens are to be <br /> installed at depths where CPT borings have identified permeable zones and <br /> where existing onsite monitoring wells for the zones are screened (i.e: 45' to 65' <br /> bgs, 75' to 85' bgs, and deeper if the 75' to 85' bgs zone wells have repeated <br /> elevated levels of petroleum). <br /> Shells' rationale for not performing vertical assessment "in the source area" is <br /> that drilling through shallow impacted groundwater to assess the deeper <br /> groundwater zones produces questionable data. Shell's example is that 1,640 <br /> parts per billion (ppb) of 1,2-DCA was detected in the groundwater sample <br /> obtained from CPT boring, SB-4 at 72 feet below surface grade (bsg) and that <br /> the level of 1,2-DCA in the groundwater samples from S-4-83 are much lower. <br /> EHD brings to Shell's attention that the CPT log for SB-4 shows that the sample <br /> in question, SB-4-72', was taken from a two-foot CPT screened sampler in silty <br /> sand/sand, whereas monitoring well S-4-83, is screened from 73' to 83' bsg and <br /> this interval is shown on the CPT log to be gravely sand/sand. Also, the <br /> groundwater grab sample, SB-4-82, of 141 ppb is similar to the groundwater <br /> samples from monitoring well S-4-83 that have ranged from 74 to 130 ppb. <br /> Further demonstration that assessing the vertical extent by drilling through <br /> shallow impacted ground water is acceptable is provided by the fact that <br /> monitoring well S-4, screened 37' to 57' bgs has lower concentrations of 1,2- <br /> DCA than those found in the deeper monitoring well, S-4-83. Shell's concern <br /> that questionable data is produced does not appear to be the case for this site. <br /> EHD does not accept Shell's rationale for not conducting a vertical investigation <br /> near the source area. <br /> Shell's original intention to place soil boring S-19 in the core/source area to 150 <br /> feet bgs and ONLY sample for lead in the soil has still not been resolved. EHD <br /> has made it clear that conducting an investigation for 1,2-DCA based on only <br /> lead analysis of the soil is unacceptable. Please clarify your intentions and note <br /> the EHD directive for SB-19 in EHD correspondence dated September 22, 2003. <br /> If Shell wants to move the location of proposed SB19 down gradient of the <br /> northern island area (source), in the area of S-4, EHD will approve the new <br /> location. <br />
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