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2900 - Site Mitigation Program
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PR0548753
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Entry Properties
Last modified
3/2/2026 11:33:41 AM
Creation date
3/2/2026 11:15:39 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0548753
PE
2959 - DTSC LEAD AGENCY SITE
FACILITY_ID
FA0027916
FACILITY_NAME
BOBSON CLEANERS, INC.
STREET_NUMBER
600
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
22314117
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
600 N MAIN ST MANTECA 95336
Tags
EHD - Public
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Cleanup in Vulnerable Communities'Initiative Final Project Reference:Bobson Cleaners <br /> Discovery and Enforcement Discovery Project Number:60688620-5.1 <br /> Investigation Work Plan <br /> tested. If no valid detectable concentrations of target compounds are reported for the given samples,then a <br /> decision will be made that the Site is adequately characterized with respect to the compounds tested and no <br /> further sampling will be required as part of this DI. If target constituents are detected in the samples tested, <br /> depending on the data it may be necessary to perform additional sampling until the Site is completely <br /> characterized. Once the site is adequately characterized,the data will be compiled for use in calculating <br /> screening risks to human health and the environment. Once the site is adequately characterized,the data will <br /> be compiled for use in calculating screening risks to human health. The results of the risk evaluation will be used <br /> to request a determination from DTSC. <br /> • Specify Limits on Decision Error: The results of the analytical testing will be subject to data evaluation <br /> following the procedures for data review specified in Section 4.3 below. Data will be determined to be valid if the <br /> specified limits on precision, accuracy, representativeness, comparability, completeness, and sensitivity are <br /> achieved.The results of any detected target constituents will be considered in evaluating the need for additional <br /> sampling of soil gas, soil, or groundwater, and assessing the necessity for reducing any risks posed by the <br /> potential contamination.AECOM will review the signed data package from the laboratory and will be responsible <br /> for the quality of the data. <br /> • Develop the Plan for Obtaining Data:The field-sampling program has been designed to provide the type and <br /> quantity of data needed to satisfy each of the aforementioned objectives. Due to the absence of previous site <br /> investigations(i.e. site characterization and sampling)to the Site there is a possibility of constituent hot spots <br /> being inaccessible for sampling at this time.Areas of high concentration onsite may not be identified without <br /> additional access and investigation of the Site. The DI Work Plan provides the specifications for the data <br /> collection activities, including the numbers of samples, respective locations, and sampling techniques.The <br /> quality of the data will be assessed through the procedures further described herein. <br /> 4.2 Specific Data Quality Objectives <br /> Specific DQOs for the data quality indicators (DQIs)of precision, accuracy, representativeness, completeness, <br /> comparability, and method detection limits have been selected. These DQIs and their corresponding DQOs are <br /> discussed in turn below. <br /> 4.2.1 Precision <br /> Precision measures the reproducibility of repetitive measurements. It is strictly defined as the degree of mutual <br /> agreement among independent measurements as the result of repeated application of the sample process under <br /> similar conditions. <br /> Analytical precision is a measurement of the variability associated with duplicate or replicate analyses of the same <br /> sample in the laboratory and is determined by analysis of laboratory quality control samples, such as duplicate control <br /> samples, matrix spike duplicates(MSD), or sample duplicates. If the recoveries of analytes in the specified control <br /> samples are comparable within established control limits, then precision is within limits. <br /> Total precision is a measurement of the variability associated with the entire sampling and analytical process. It is <br /> determined by analysis of duplicate or replicate field samples, and measures variability introduced by both the <br /> laboratory and field operations. Field duplicate samples are analyzed to assess field and analytical precision. <br /> Duplicate results are assessed using the relative percent difference(RPD)between duplicate measurements. If the <br /> RPD for laboratory quality control samples exceeds 30 percent, data will be qualified. If the RPD between primary <br /> and duplicate field samples exceeds 50 percent, data will be qualified. The RPD will be calculated as follows: <br /> %RPD =200(X2—X1)/(X2+Xt), <br /> where Xi is the larger of the two observed values and X2 is the smaller of the two observed values. <br /> 4.2.2 Accuracy <br /> Accuracy is a statistical measurement of correctness and includes components of random error(variability due to <br /> imprecision)and systematic error. It reflects the total error associated with a measurement.A measurement is <br /> accurate when the value reported does not differ from the true value or known concentration of the spike or standard. <br /> Prepared for: Department of Toxic Substances Control AECOM <br /> 24 <br />
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