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2900 - Site Mitigation Program
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PR0506824
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Last modified
4/7/2020 3:26:58 PM
Creation date
4/7/2020 2:23:05 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
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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1997 Annual Report 5 - 10 February 1998 <br /> Sharpe Facility <br /> 8) The Annual Report acknowledges the North and South Balloon discharge exceeded the NPDES <br /> pH discharge limits and the Central Area discharge also exceeded the pH discharge limits. <br /> These excursions are violations of Sharpe's permit. In 1996 Sharpe conducted a Scale Study to <br /> address extraction and treatment system scale problems. This study recommended adding pH <br /> control to the outlet of the air stripping towers for each of the three plants to control scale <br /> formation. To date, Sharpe has not implemented the recommendation from the Scale Study <br /> Report. The revised Annual Report must provide specific actions, with a time schedule for <br /> implementation, to achieve compliance. <br /> 9) Current designations of the monitoring well aquifer zones are incorrect and may lead to <br /> inaccurate interpretations of contaminant movement. It appears appropriate to re-designate wells <br /> for more accurate interpretation of future data. For example MW521C does not actually extend <br /> into the C zone sand nor does MW445C as seen in cross section B and D (Figures 2.5-3 and 2.5- <br /> 5). A footnote could indicate the previous designation for correlation of past data. <br /> 10) Page 3-2 in Section 3.2.8, the statement"MW 421C is located at the downgradient edge of the C <br /> zone" is incorrect. This well is at the upgradient edge of the C zone. <br /> 11) Page 4-4, Section 4.2.2.6 States that"Surface scrape soil samples collected in the North Balloon <br /> in February 1997 did not indicate any results greater than the action levels specified in the OU 2 <br /> ROD for lead and chromium". This statement is incorrect and should be modified. <br /> 12) In the 1Q97, 209 results of VOC analysis by SW8020 were rejected by Radian based on the <br /> lack of QA for the data, and in 3Q97, 239 sample results were rejected. Samples collected <br /> during all four quarters for total petroleum hydrocarbons contained a contaminant in the blank <br /> resulting in 27 sample results as being qualified as non-detect. Finally, forty results in the 3Q97 <br /> analyzed for pesticides/PCBs by Method SW8081 were qualified, and therefore are less reliable <br /> because the samples were analyzed at the incorrect dilution factor. These seem to be excessively <br /> poor QA/QC results. What actions is Sharpe taking to improve data collection to avoid these <br /> problems in the future? <br /> 13) Concentrations of diesel are noted in MW 421A and MW470A in both 1996 and 1997 Annual <br /> Reports. These impacts were caused by underground storage tanks and a response action has <br /> been described in the UST Program Work Plan, submitted October 6, 1997. These actions <br /> should be referenced in the Annual Report in response to the diesel degradation. <br /> Page 5-5, Section 5.4.2.4 notes that petroleum hydrocarbons are also detected in the Central <br /> Area effluent. Is there a correlation with the petroleum contamination found in the groundwater <br /> at MW 421A and MW470A noted above? <br /> 14) The last two sentences in Section ES 1.14 contradict each other. Please clarify and correct. <br /> 15) The following comments pertain specifically to the Proposed Groundwater Monitoring Plan. <br />
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