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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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3570
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2900 - Site Mitigation Program
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PR0527444
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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL
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Last modified
4/10/2020 4:53:44 PM
Creation date
4/10/2020 4:05:28 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
ROY'S AUTO - HISTORICAL
RECORD_ID
PR0527444
PE
2950
FACILITY_ID
FA0018586
FACILITY_NAME
FORMER ROY KNOLL TOWING
STREET_NUMBER
3570
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
14339014
CURRENT_STATUS
01
SITE_LOCATION
3570 E MINER AVE
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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While recognizing that urban lead is a significant problem, <br /> this interim directive is not designed to be applied in <br /> addressing the potential threat of lead in urban areas other than <br /> at CERCLA or RCRA Corrective Action sites. Guidance and <br /> regulations to be developed under TSCA Section 403 will provide <br /> an appropriate tool for addressing urban sites of potential <br /> concern. <br /> Generally, where the screening level is exceeded, oSWER <br /> recommends using the IEUBK model during the Remedial <br /> Investigation or the RCRA Facility Investigation for evaluating <br /> potential risks to humans from environmental exposures to lead <br /> under residential scenarios. Site-specific data need to be <br /> collected to determire PRGs or MCSs. At a minimum, this may <br /> involve collecting soil and dust samples in appropriate areas of <br /> the site. Further guidance on data collection or modification of <br /> the non-residential equation can be obtained by contacting the <br /> RTICs or RCRA Regional risk assessors, who in turn may consult <br /> the Lead Technical Review Workgroup. <br /> The type of site-specific data that should be collected will <br /> obviously depend on a number of factors, including the proximity <br /> of residences to the contaminated soil, the presence of site <br /> access controls, and other factors that would influence the <br /> probability of actual human exposure to the soils. At a minimum, <br /> when residences are at or near the site, it is expected that <br /> using the model will generally involve taking soil and dust <br /> samples from appropriate areas of the site. In many cases, it <br /> may not be necessary to Sather certain types of data for input <br /> into the model. For example, when there are no residences <br /> nearby, or where there is otherwise no exposure or very limited <br /> exposure to lead contamination, it may not be necessary to <br /> collect site-specific data (e.g. , dust, water, paint, blood-lead, <br /> etc. ) <br /> In developing a PRG for CERCLA sites or a MCS for RCRA <br /> facilities, EPA recommends that a soil lead concentration be <br /> determined so that a typical child or group of children exposed <br /> to lead at this level would have an estimated risk of no more <br /> than 5% of exceeding a blood lead of 10 Ag/dl. In applying the <br /> IEUBK model for this purpose, appropriate site specific data on <br /> model input parameters, including background exposures to lead, <br /> would be identified. <br /> When the PRG or MCS is exceeded, remedial action is <br /> generally recommended. Such action does not, however, <br /> necessarily involve excavating soil. A range of possible actions <br /> may be considered, as discussed in greater detail under the <br /> Implementation section of this directive: Issues for Both <br /> Programs. <br /> -10- <br />
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