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SITE INFORMATION AND CORRESPONDENCE_2004-2014
Environmental Health - Public
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PR0506824
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SITE INFORMATION AND CORRESPONDENCE_2004-2014
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Last modified
4/7/2020 2:56:47 PM
Creation date
4/7/2020 2:44:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
2004-2014
RECORD_ID
PR0506824
PE
2960
FACILITY_ID
FA0007648
FACILITY_NAME
DDRW - SHARPES
STREET_NUMBER
850
Direction
E
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19802001
CURRENT_STATUS
01
SITE_LOCATION
850 E ROTH RD BLDG S-108
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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Mr. Maurice Benson <br /> July 8, 2008 <br /> Page 2 <br /> Comments <br /> 1) Page 1-13, Section 1.5.5; DTSC infers from the section that a benchscale test of <br /> the native soils at site P-5A was not conducted to assess both the potential for <br /> the conversion and mobility of naturally occurring metals such as arsenic in the <br /> soil, or the potential interference from other background metals in the soil matrix <br /> with the EHC. DTSC recommends that a benchscale test be performed on a <br /> representative soil sample taken at depth prior to the injection of the EHC slurry. <br /> 2) Page 1-13, Section 1.6, Hydraulic Fracturing; The injection of water under <br /> pressure (notching process) in order to create the necessary fractures or <br /> horizontal voids in the subsurface in combination with the slurry injection <br /> (11,000 gallons water) would also create a hydraulic flushing of the <br /> contaminants, potentially interfering with the engineering controls created by the <br /> operating extraction wells. Please describe in the work plan how Defense <br /> Enterprises Support San Joaquin California (DESJC) intends to mitigate the <br /> potential mobility of TCE to areas that are uncontaminated, less contaminated, or <br /> outside the hydraulic influence of the extraction well network. <br /> 3) Page 1-14, Section 1.6.3, Hydraulic Fracturing; Describe in the work plan how <br /> DESJC intends to ensure the hydraulic fracturing does not propagate along the <br /> natural fissures or cracks in the soil matrix, leading to non-uniform fractures, or <br /> fractures that would extend along a pathway not intended for treatment therefore <br /> affecting the effectiveness of the EHC contact with contaminants. <br /> 4) Page 2-2, Section 2.1.5, third sentence; The section states that two dual-nested <br /> monitoring wells will be installed in the target area to monitor groundwater both <br /> pre- and post injection of EHC. According to this section, one nested well will be <br /> installed approximately seven feet from the injection borehole with the second <br /> nested well "...located five feet downgradient and outside the radius of fracture <br /> (ROF)." The description of the well location is unclear, and leads one to interpret <br /> that the second nested well is only five feet downgradient of the first well, inside <br /> the ROF of approximately 20 feet, contradicting Figure 2-1. For clarity and <br /> consistency with Figure 2-1, the sentence should be restated as "One dual- <br /> nested well will be located downgradient, five feet outside the ROF." <br /> 5) Page 3-2, Section 3.4, Hollow-Stem Auger Drilling; DTSC recommends that <br /> continuous core samples of the area targeted are completed and analyzed pre- <br /> and post EHC injection to correlate the lithology with CPT data, but also assess <br /> initial soil concentrations of volatile organic compounds and background metals. <br />
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