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2900 - Site Mitigation Program
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PR0508450
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Last modified
5/29/2019 11:42:43 AM
Creation date
5/29/2019 11:07:59 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0508450
PE
2960
FACILITY_ID
FA0008087
FACILITY_NAME
DDJC-TRACY
STREET_NUMBER
25700
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
01
SITE_LOCATION
25700 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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4) The report does not include sufficient data to evaluate <br /> the slug tests. Copies of the chart records, information on <br /> the type of transducer used, assumptions used in <br /> calculations, etc. should be submitted for this report and <br /> included in subsequent reports. DHS agrees with Radian that <br /> the slug tests results are somewhat suspect due to the <br /> factors discussed in sections 3 .4 and 4. 3 . Additionally, <br /> slug tests usually are accurate only within two orders of <br /> magnitude and, because of the spatial limitations inherent <br /> in the test, slug test results should not be extrapolated to <br /> characterize large untested portions of an aquifer. <br /> SOW for Next Phase <br /> 1) This scope of work continues the methodology of using <br /> soil vapor surveys as an initial screening tool for <br /> contamination. DHS considers this to be on the borderline <br /> of proven technology and therefore requires substantial <br /> documentation and verification of results by soil and <br /> groundwater testing. Additional required documentation is <br /> specified in attached Attachment II. <br /> The proposed methodology has one major failing in that it <br /> essentially chases the plume of contamination rather than <br /> monitors the leading edge and points beyond. With the <br /> results of a pump test(s) , piezometer data, and the <br /> sampling data Radian should be able to predict the <br /> approximate spatial and temporal aspects of plumes and place <br /> monitor wells in advance of and along the leading edge of <br /> these plumes. DHS recommends that flexibility in the SOW be <br /> provided to allow for this type of approach. Early <br /> placement of monitor wells in advance of the plume will also <br /> expedite selection and design of remedial actions and later <br /> evaluation of remedial actions. <br /> 2) Section 3 .9 . 1 (last sentence) : Monitoring of the <br /> deepest contaminated zones and initial monitoring of the <br /> underlying zone is required. The latter monitoring can be <br /> discontinued after samples confirm the lack of contamination <br /> at this depth. The potential for downward migration of <br /> contaminants at this site emphasizes the need for monitoring <br /> of the deeper zones. <br /> 3) Section 4 . 3 . 2 : Thin walled samplers should be given <br /> preference. <br /> 4) Section 4 . 3 . 4 : Grain size analysis must be done where <br /> the screen will be located to properly design the sand pack. <br /> 5) Section 4. 4 . 4 : DHS recommends a sand pack envelope <br /> between three and five inches. <br /> Jay IAXcas- Associate Engineering Geologist <br /> a� fig <br />
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