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BENJAMIN HOLT
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2900 - Site Mitigation Program
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PR0546415
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Entry Properties
Last modified
4/22/2026 11:08:16 AM
Creation date
4/22/2026 10:54:25 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0546415
PE
2960 - RWQCB LEAD AGENCY CLEAN UP SITE
FACILITY_ID
FA0026300
FACILITY_NAME
LINCOLN CENTER ENVIRONMENTAL REMEDIATION TRUST
STREET_NUMBER
0
Direction
W
STREET_NAME
BENJAMIN HOLT
STREET_TYPE
DR
City
STOCKTON
Zip
95207
APN
09741079
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
W BENJAMIN HOLT DR STOCKTON 95207
Tags
EHD - Public
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Mr. Brattain <br /> October 19, 2020 <br /> Page 5 <br /> the Environment's(AFCEE's)Monitoring and Remediation Optimization System(MAROS). The <br /> ESTAT was used to perform a Mann-Kendall trend analysis on the data to assess the nature of <br /> COC, Cr(VI) and permanganate concentration trends with time. It must be noted that as part of <br /> this evaluation, Suite B parameters specified in the WDR-MRP (dissolved iron and manganese, <br /> total chromium and potassium and total dissolved solids) serve as surrogates to the primary <br /> byproducts of ISCO and the determinations made regarding Cr(VI) and permanganate monitoring <br /> requirements are also intended to apply to Suite B parameters. <br /> In addition, trend plots were developed to visually observe concentration trends in support of the <br /> decision-making process. A summary of the data evaluation including Mann-Kendall trend <br /> analysis is presented in Table 1. Attachments 1 and 2 present the historical data trends for the <br /> COCs and ISCO byproducts (permanganate and Cr[VI])respectively at each monitoring location. <br /> As part of the decision-making process,the following two-tiered approach is being used to justify <br /> exclusion of wells from the monitoring program or reduction in the monitoring frequency. Tier 1 <br /> criteria include the following: <br /> I. Is the well needed to evaluate remedy performance? : This criterion evaluates whether the <br /> well is located within the current plume footprint and allows for assessment of remedial <br /> performance for COCs and Cr(VI). <br /> 2. Is the well needed to define the plume boundary? : This criterion evaluates whether the <br /> well allows for evaluating plume dynamics and is useful for defining the plume boundary <br /> during active remediation. <br /> 3. Is the well needed to evaluate groundwater flow characteristics? : This criterion evaluates <br /> whether the data from the well allows evaluation of groundwater flow direction and <br /> gradients within the treatment zone, and overall site background as part of the remedial <br /> performance assessment process. <br /> If the well does not satisfy the Tier 1 criteria, it becomes a candidate for exclusion from current <br /> monitoring. If the well satisfies the Tier 1 criteria, it will be compared against the Tier 2 criteria <br /> listed below to evaluate whether it qualifies for a reduction in monitoring frequency: <br /> 1. Historical COC data trends: This criterion evaluates historical trends in COC <br /> concentrations to determine whether additional data collection at the current frequency <br /> provides continued benefit for performance assessment. For instance, if historical data <br /> engineers I scientists I innovators <br />
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