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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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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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children living in houses with high levels of lead dust from <br /> deteriorated paint) . The presence of various sources of lead <br /> exposure may be very important in both the development of site- <br /> specific risk assessments and in the consideration of alternative <br /> risk management options. <br /> From an assessment perspective, estimating blood lead <br /> _ levels, that might result from exposures at a site, depends on <br /> appropriately integrating expoffures from all relevant media. <br /> Specifically, it is important to consider direct soil exposures <br /> and indoor dust exposures (which can include contributions from <br /> both soil and lead-based paint) on a site-specific basis, as well <br /> as any contributions from drinking water or other local sources <br /> of lead exposure. In using the IEUBK model to estimate blood <br /> lead levels, it is important to note that the risk attributable <br /> to soil lead exposures is dependent upon the existing level of <br /> exposures- from other sources. That is, the amount by which the <br /> total risk would be lowered if all exposures to lead in soil were <br /> removed is not a constant, but varies with the level of existing <br /> non-soil exposures. This is because the model derives a <br /> "distribution" (rather than a simple point estimate) as an output <br /> whose shape and size is quite dependent on the predicted <br /> variability of exposures from each lead source. As a result, <br /> other factors being equal, the risks attributable to soil will <br /> generally be higher in the presence of elevated lead exposures <br /> from other sources. Therefore, in applying the IEUBK model, the <br /> risk attributable to soil lead can be predicted as the difference <br /> between the risk estimated when all sources of lead exposure are <br /> assessed, and th= -isk estimated considering only non-soil <br /> related exposures. This concept is especially important when <br /> evaluating different options for risk reduction at a given site. <br /> From a risk management perspective, achieving a safe <br /> environment for populations at CERCLA and RCRA Corrective Action <br /> sites may require attention to multiple sources of lead, not all <br /> of which may be related to contamination from the source that was <br /> the initial concern at the site. Generally, the goal of the <br /> Agency,. while acting within the constraints of CERCLA and RCRA <br /> legal authorities, is to reduce, to the maximum extent feasible, <br /> the risk of having significantly elevated blood lead levels. On <br /> a site-specific basis this can include remediation approaches <br /> that would lead to reduction of exposure from other sources, such <br /> as lead-based paint, in conjunction with appropriate soil <br /> remediation. Following from the risk assessment discussion in <br /> the previous paragraphs, exposures from lead in soils may have a <br /> lesser impact in producing high blood lead levels if existing <br /> exposures from lead-based paint are reduced. <br /> Abatement vs. Intervention: Remedial measures can be divided <br /> into those that remove the source of contamination (abatement) <br /> and those that leave the contamination in place but block the <br /> -12- <br />
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