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EHD Program Facility Records by Street Name
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STOCKTON
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2900 - Site Mitigation Program
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PR0548037
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Entry Properties
Last modified
7/17/2026 11:48:18 AM
Creation date
7/23/2025 2:39:16 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0548037
PE
2950 - ENVIRON ASSESS
FACILITY_ID
FA0027411
FACILITY_NAME
CITY OF LODI PARKS AND RECREATION DEPARTMENT
STREET_NUMBER
125
Direction
N
STREET_NAME
STOCKTON
STREET_TYPE
ST
City
LODI
Zip
95240
APN
043084130
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
125 N STOCKTON ST LODI 95240
Tags
EHD - Public
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HEURESIS PCS December 2015 <br /> BACKGROUND INFORMATION <br /> EVALUATION DATA SOURCE AND DATE: <br /> This sheet is supplemental information to be used in conjunction with Chapter 7 of the HUD Guidelines for the <br /> Evaluation and Control of Lead-Based Paint Hazards in Housing ("HUD Guidelines"). Performance parameters <br /> shown on this sheet are calculated using test results on building components in the HUD archive. Testing was <br /> conducted on 146 test samples in November 2015, with two separate instruments running software version 2.1-2 <br /> in Action Level test mode. The actual source strength of each instrument on the day of testing was approximately <br /> 2.0 mCi; source ages were approximately one year. <br /> OPERATING PARAMETERS <br /> Performance parameters shown in this sheet are applicable only when properly operating the instrument using the <br /> manufacturer's instructions and procedures described in Chapter 7 of the HUD Guidelines. <br /> XRF CALIBRATION CHECK: <br /> The calibration of the XRF instrument should be checked using the paint film nearest 1.0 mg/cm2 in the NIST <br /> Standard Reference Material (SRM) used (e.g., for NIST SRM 2579, use the 1.02 mg/cm2 film). <br /> If the average (rounded to 1 decimal place) of three readings is outside the acceptable calibration check range, <br /> follow the manufacturer's instructions to bring the instrument into control before XRF testing proceeds. <br /> SUBSTRATE CORRECTION VALUE COMPUTATION: <br /> Chapter 7 of the HUD Guidelines provides guidance on correcting XRF results for substrate bias. Supplemental <br /> guidance for using the paint film nearest 1.0 mg/cm2 for substrate correction is provided: <br /> XRF results are corrected for substrate bias by subtracting from each XRF result a correction value determined <br /> separately in each house for single-family housing or in each development for multifamily housing, for each <br /> substrate. The correction value is an average of XRF readings taken over the NIST SRM paint film nearest to 1.0 <br /> mg/cm2 at test locations that have been scraped bare of their paint covering. Compute the correction values as <br /> follows: <br /> Using the same XRF instrument, take three readings on a bare substrate area covered with the NIST <br /> SRM paint film nearest 1 mg/cm2. Repeat this procedure by taking three more readings on a second bare <br /> substrate area of the same substrate covered with the NIST SRM. <br /> Compute the correction value for each substrate type where XRF readings indicate substrate <br /> correction is needed by computing the average of all six readings as shown below. <br /> For each substrate type (the 1.02 mg/cm2 NIST SRM is shown in this example; use the actual lead <br /> loading of the NIST SRM used for substrate correction): <br /> Correction value = 0st+ 2nd + 3rd + 4th + 5th + 6th Reading)/6 - 1.02 mg/cm2 <br /> Repeat this procedure for each substrate requiring substrate correction in the house or housing <br /> development. <br /> EVALUATING THE QUALITY OF XRF TESTING: <br /> Randomly select ten testing combinations for retesting from each house or from two randomly selected units in <br /> multifamily housing. <br /> Conduct XRF re-testing at the ten testing combinations selected for retesting. <br /> Page 2 of 4 <br />
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