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COMPLIANCE INFO
Environmental Health - Public
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EHD Program Facility Records by Street Name
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4400 - Solid Waste Program
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PR0504187
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COMPLIANCE INFO
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Last modified
7/31/2020 9:27:34 AM
Creation date
7/3/2020 10:34:35 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0504187
PE
4430
FACILITY_ID
FA0006111
FACILITY_NAME
SHARPE ARMY DEPOT
STREET_NUMBER
850
Direction
E
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19802001
CURRENT_STATUS
02
SITE_LOCATION
850 E ROTH RD
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
Scanner
CField
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4430_PR0504187_850 E ROTH_.tif
Tags
EHD - Public
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Assessment (RFA). U.S. EPA does not require such that an RFA report be submitted <br />by SHAD; however, U.S. EPA deems that SHAD must document, in a separate chapter <br />of the Remedial, Investigation Report, the following: <br />a. Results of the Remedial Investigation of those potential SWMUs and AM <br />those were already investigated under Superfund, <br />b. Assessment of results of the SWMUs, potential SWMUS, and AOCs which <br />have not been investigated by SHAD. If SHAD deems that Attachment A <br />is not a complete list, then SHAD should recommend additional areas and <br />notify U.S. EPA of such a recommendation, and <br />C. Rationales for not investigating certain SWMU(s), potential SWMU(s), or <br />AOC(s).. <br />2. The purpose of the list of findings is not stated. Are they intended to be factual <br />statements that support a course of action? Are they provided as support for the <br />recommendations presented in the following section? Are they intended as a <br />comprehensive set of conclusions that may be drawn from the results of the <br />investigation up to now? <br />3. SHAD should not rely on automated data analysis methods such as kriging to define <br />plume extent. These methods do not take into account some of the most significant <br />information related to contaminant distribution, including: hydraulic gradients, <br />stratigraphy, and hydraulic conductivity, all of which control the direction and rate of <br />transport. Also of critical importance are: historical data identifying contaminant <br />source areas and constituents; soil gas data or other direct evidence of contaminant <br />distribution in the vadose zone; and the effects of pumping wells and recharge <br />sources on contaminant transport. <br />The limitations and assumptions in the data analysis should be adequately evaluated, <br />r to ensure that appropriate conclusions are drawn from the data. It is not clear from <br />the discussion of the kriging analysis to what extent the recommendations for <br />proposed wells were influenced by more subjective analysis, although it is stated that <br />subjective analysis was performed. <br />2 <br />
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