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SITE INFORMATION AND CORRESPONDENCE
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
11/1/2018 10:03:55 PM
Creation date
11/1/2018 11:57:45 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0009012
PE
2960
FACILITY_ID
FA0004532
FACILITY_NAME
FRMR KEARNEY-KPF FACILITY
STREET_NUMBER
1624
Direction
E
STREET_NAME
ALPINE
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
11708006-09
CURRENT_STATUS
01
SITE_LOCATION
1624 E ALPINE AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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Kearney-KPF 2 13 September 1990 <br /> Modified Closure Plan <br /> Page 10. The Letter of Closure Certification and Closure Certification Report <br /> are tentatively scheduled for submittal on 20 November 1990. Once <br /> these documents are reviewed and accepted, the site will no longer <br /> be regulated by the Toxic Pits Cleanup Act (TPCA) because Kearney- <br /> KPF will have closed the surface impoundments and has previously <br /> completed their Hydrogeologic Assessment Report (HAR) . <br /> APPENDIX B <br /> REPORT OF PRELIMINARY GEOTECHNICAL INVESTIGATION DESIGN FOR SITE CLOSURE - <br /> KEARNEY-KPF BORROW / INFILTRATION BASIN SITE <br /> Page 1. The infiltration basin was sited at the southwest corner of the <br /> western field. Portions of the basin are located over the cuttings <br /> and drilling mud disposal areas. The basin site appears to have <br /> been selected because of the lower topography in this portion of the <br /> field. <br /> However, previously this portion of the western field had been <br /> selected by Hargis for disposal of wastes generated during the <br /> remedial investigation (RI) . It is anticipated that Hargis will <br /> want to dispose of additional wastes from Phase II of the RI . The <br /> Regional Board had previously discussed with Hargis that the <br /> infiltration basin was not to be located over the landfarmed wastes. <br /> Because of the conflict in the use of this portion of the western <br /> field, the landfarmed wastes must 1) be removed and disposed at a <br /> permitted facility; 2) be removed and landfarmed in another portion <br /> of the western field; or 3) be excavated and placed in the <br /> foundation layer of the cover, or lower, and not within the upper <br /> foot of the cover. Additionally, the disposal of the wastes which <br /> were to be landfarmed was based on the analytical results for the <br /> contaminants of concern; namely heavy metals and volatile organic <br /> constituents (VOCs) . The cuttings or drilling muds were not <br /> analyzed for pH, electrical conductivity (EC) or total dissolved <br /> solids (TOS) . These wastes should also be analyzed for these <br /> constituents prior to burial in the ponds or use in the pond cover, <br /> to determine if these constituents pose a threat to water quality. <br /> Page 1. Figure 1 (Demolition and Select Sand Blanket Locations) depicts a <br /> soil disposal area. If this soil disposal area is intended to be <br /> representative of the drilling mud disposal area, it is drawn <br /> incorrectly. The drilling mud disposal area is clearly <br /> distinguishable in the field due to the different properties of the <br /> drilling mud compared to the native soils. Monitor well B-4 is not <br /> encompassed by the drilling mud disposal area and this area does not <br /> extend to the north of the diagonal access road. <br /> Page 1 . Five representative test pits were excavated in the western field to <br /> determine the engineering properties of the native soils. Based on <br />
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