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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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Last modified
3/16/2020 11:36:44 PM
Creation date
3/16/2020 2:10:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0541875
PE
2960
FACILITY_ID
FA0024017
FACILITY_NAME
CHEVRON SITE 306415
STREET_NUMBER
437
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95202
APN
1392417
CURRENT_STATUS
01
SITE_LOCATION
437 E MINER AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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JRN-39-1996 13:01 PLJCaCB — SP BRY PLANNING 5102853928 P.02 <br /> .: <br /> CALIFORNIA REGIONAL WA QUALITY CONTROL BOARD '°, 4 <br /> SAN FRANCISCO BAY REGION `I <br /> 2101 wE3STER STREET,Sude 500 <br /> OAKLAND,CA 94612 <br /> Tel: (510)226-1255 <br /> FAX: (510)296.1330 <br /> 395: (5101286-0404 <br /> act sheet <br /> Questlons and Answers <br /> an the <br /> "Interim Guidance on Low-Rise Petroleum Hydracarban Cl anups" <br /> roacamber <br /> ranee Livermore National iaborator/ (1f1LJ 15suetl its wn'n maximum depth to water less man so feet and no drinking <br /> ecommendations to Improve the Cleanup P,ocess for California's water wells screened in the shallow groundwater zone within 250 <br /> abng Underground Fu.l Tanks° (October 16, 19951. in response feet of Ne leak) we recommend that active remediation be replaced <br /> this report, State 'A'ater Resources ConUcl Board fxecu0ve vviih monitoring to determine if the fuel leak plume is stable. <br /> Director Walt Pettit issued an interim Quidance tetter dated Obviously Qood judgment is required in alt o!these decisions. <br /> 8, 1995, which discussed me regulatory implications of However, <br /> that report"judgment should now include knowledge provided by <br /> the conclusions and recommendations of to LNL report the <br /> From the December 8, 1995, tatter. This Fart Sheet is intended to further amplify the guidance contained <br /> in me State Board letter for fuel cleanup sites within the San <br /> "In the interim and in light of the findings and recommendations in Francisco Bay Region through the form of"Answers" to frequently <br /> Me LLVL report, we believe clealup oversight agencias should asked questions regarding implementation of the net,petroleum <br /> proceed aggressively to close lot"risk soil Only cases. For cases cleanup intehm guidance. <br /> affecting low nsk groundwater (for instance, shallow groundwater <br /> Qwhat is considered a "source"when completing source expected to come in contact with the groundwater, it is <br /> removal? unlikely that it is a significant source of pullution. <br /> A Lcaking tanks and appurtenant structures must be removed low risk groundwater sites"? <br /> or repaired. Free product or soil which contains sufficient Q What i8 meant b3' " <br /> mobile constituents (leachate,vapors, or gravity flow)to A An example of a low risk groundwater site is described in <br /> degradc groundwater quality above water quality objectives the State Board letter as a site with maximum depth to <br /> or provide a significant threat to human health or the groundwater less than 50 feet and no drinking water wells <br /> environment should be considered a source. screened in the shallow groundwater zone within 250 feet of <br /> the leak. In addition, there should be no surface water or <br /> Gasoline or diesel free product fits this definition at other sensitive habitat that may be adversely impacted by <br /> virtually all sites. Oil and grease, degraded crude oil, and the release. <br /> degraded diesel may not be soluble enough to be <br /> considered a significant source and often do not degrade Thcse criteria arc not hard and fast rules. They are meant <br /> water quality or present a significant risk to human health to recognize that shallow groundwater is rarely used as a <br /> or the environment, drinking water source, that biodegradation in most cases <br /> will stabilize a plume within Z50 feet of the leak. and that. <br /> Many factors need to be considered when delermining if a the plume will likely remediate itself duc to natural <br /> given petroleum release con3titate5 a source. biodegradation. However, if the plume is not stable, <br /> prefercutial pathways exist at the situ, or sensitive receptors <br /> Depth of the affected soil below ground surface are near the end of the plume,then the site should not be <br /> • Depth to groundwater below ground surface considered law risk. <br /> Soil type and physical properties <br /> Presence of preferential pathways (is. old wells, utility Q How do we determine if there is a significant risk to human <br /> trenches, ctc.) health at a site? <br /> Type of pettolevm released A The American Society of Testing and 24aterials (AS-1'rf) <br /> Infiltration rate standard for Risk Based Corrective: Action, ASTM E-1739- <br /> Spatial distribution of petroleum concentrations 95, (RBCA)provides look up tables for various exposure <br /> Total mass of petroleum released pathways that contains conservative screening levels (when <br /> 'fronds in monitoring data modified for California's benzene standard)for comparison <br /> Chemical and physical properties of any residual with values existing at the site. 'the standard also contains <br /> hydrocarbons a methodology for determining site specific levels that arc <br /> protective, of public health and the environment. The <br /> Good judgment must be used when weighing these and SWRCB/RWQCB is now offering two day classui for all <br /> other factors- For old releases, the absence of current interested parties in risk-basud decision making at soil and <br /> groundwater degradation often is a good indication that groundwater impacted sites. Please contact the CIC <br /> residual concentrations present in the soil are not a source <br /> of pollution. In general, if impacted soil is not in contact or <br /> ... ,.�....w,�no. Much of this information nes <br />
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