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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL (2)
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0527444
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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL (2)
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Last modified
4/10/2020 4:45:36 PM
Creation date
4/10/2020 4:19:11 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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SJGOV\sballwahn
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EHD - Public
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I Y � <br /> is attached. However, the decision logic for a sample of units is more complicated than for <br /> single residential units, and should be fully grasped before a sample is selected. <br /> How to Sample <br /> The recommended method for testing in a residential unit at this time is the K shell <br /> reading from a portable XRF instrument. Substrate corrections are to be made where <br /> necessary. Standard reference material paint films developed by NIST for usage with XRFs <br /> are to be used to demonstrate that XRF instruments are in control. XRF results are in units <br /> of milligrams per square centimeter. <br /> An average of three readings is recommended. Each reading should be approximately <br /> 15 seconds with a new source. Appropriate adjustments in reading time should be made for <br /> source age. <br /> Where portable XRF is not feasible due to a surface being narrow or curved, where <br /> greater accuracy is desired, or where comparison to the percent by weight standard is desired, <br /> paint samples can be collected and sent for to a laboratory for analysis. The paint samples <br /> should be collected from a one square inch area. Care should be taken to collect all the paint <br /> in the area, and to minimize the inclusion of substrate material. Lead in paint samples <br /> collected in this way can be reported in both milligrams per square centimeter and percent by <br /> weight. If a surface is so deteriorated that XRF is not feasible• and a paint sample cannot be <br /> collect from a square inch, then a strip of peeling paint is to be collected. Lead from such a <br /> sample can only be reported in percent by weight units. <br /> How to Analyze Paint Samples <br /> Paint chip samples should be analyzed by a laboratory recognized by EPA's National <br /> Lead Laboratory Accreditation Program. Paint samples should be no more than 500 milligrams <br /> in weight. If the paint samples received by the laboratory are larger than 500 milligrams, the <br /> laboratory should homogenize and subsample the paint samples to select a subsample of <br /> approximately 500 milligrams for the analysis. Results reported by the laboratory must make <br /> the appropriate adjustment for the subsampling. <br /> Conclusions <br /> For single houses and units, conclusions are reached as follows. XRF results are to be <br /> corrected for substrate effects where necessary. Corrected XRF results are divided into three <br /> categories: positive, inconclusive, and negative. Reading averages of 1.6 mg/cm2 or more are <br /> classified as positive; reading averages or 0.4 mg/cm' or less are classified as negative. All <br /> other reading averages are classified as inconclusive. K-shell XRF results in the positive <br /> category indicate lead is present at or above 1.0 mg/cmZ. K-shell XRF results in the negative <br /> category indicate lead is not present at or above 1.0 mg/cm2. The probability of false positives <br /> is currently estimated to be at least less than 10%, and less than 5% in most cases. The <br /> 5 <br />
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