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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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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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the ponds. One boring, to be located at the center of each pond, was recommended <br />in our past comments, provided that the GPR survey results are definitive. <br />27. The quartering technique to be used for surface soil samples is not adequately <br />described and may not result in sufficiently uniform duplicate samples. An alternative <br />and preferred method of providing duplicate samples is to homogenize the discrete - <br />depth samples (pg. 4-1, Section 4.1). <br />28. Discrete 15 -in samples should be analyzed instead of the composited samples proposed <br />by SHAD in Section 4.2 (pg. 4-1), because of the potential for false negative results <br />due to dilution, and because of the lower vertical resolution that results from <br />compositing. - <br />The proposed compositing method was used in previous soil sampling by SHAD (ESE, <br />1987b) at locations where high TCE soil gas results indicated that TCE was present <br />in the soil. Discrete samples were analyzed for TCE, while arsenic, selenium and <br />bromacil were analyzed in composited samples. Because TCE, rather than other waste <br />compounds, was targeted in that sampling effort, only if arsenic and bromacil were <br />associated with the disposal of TCE would they be expected to be found. There is <br />some evidence that arsenic levels above background are associated with areas of TCE <br />contamination, but the correlation is not systematic. <br />SHAD proposes to collect three samples from each boring. A preferred procedure for <br />collecting three samples from each boring would be to collect and analyze discrete <br />samples (for example, from the upper 0- to 15 -in of soil (beneath any asphalt or <br />gravel cover), at 45- to 60 -in, at 120- to 135 -in), and to archive additional samples <br />(for example, at 90- to 105 -in and at the bottom of the hole) for possible future <br />analysis. In most cases the initial three samples would provide adequate vertical <br />coverage. If further resolution of non -volatiles were required later, the archived <br />samples could be analyzed. <br />29. Field quality control samples should be included. <br />30. The supplemental soil <br />investigation plan <br />represents an <br />outline of <br />the rationales and <br />methods to be used in <br />the proposed soil <br />investigation <br />but is not <br />sufficiently detailed <br />10 <br />
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