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AP2400573 (4)
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AP2400573 (4)
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Last modified
4/22/2026 2:33:32 PM
Creation date
4/22/2026 1:26:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
AP2400573
PE
2903 - WORKPLAN/REPORT PLAN CHECK - OTHER AGENCY
FACILITY_NAME
CITY OF LATHROP PUBLIC WORKS
STREET_NUMBER
390
STREET_NAME
TOWNE CENTRE
City
LATHROP
CURRENT_STATUS
In Review
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
390 TOWNE CENTRE LATHROP
Tags
EHD - Public
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Appendix D:Quality Assurance and Control Assessment <br /> The 2023 First Semiannual monitoring was performed by FGL Environmental during the period <br /> 1 February 2023 through 4 April 2023; all samples were analyzed by FGL Environmental. The <br /> analytical reports provided by the laboratory will be maintained on file by the Discharger and <br /> are available upon request. <br /> Prescribed Holding Times <br /> Holding time is defined as the maximum time allowed between sample collection and sample <br /> analysis. Results may become questionable when the holding time is exceeded. Holding times <br /> vary between constituents and can range from a few hours to a few months. All samples, with <br /> the exception of the Nitrate as Nitrogen (48 hour hold time, held for 79 hours) in the sample <br /> from KMW-8, were analyzed within the prescribed holding times. <br /> Lab Blanks <br /> Laboratory blanks are analyzed using the same procedures as the environmental samples. The <br /> blanks consist of deionized and distilled (Reagent Grade Type II) water. Analysis of the blanks is <br /> used to detect potential constituent sources contributed by the laboratory. Examples can <br /> include improperly cleaned laboratory equipment, impure reagents, and persistent airborne <br /> constituents in the laboratory environment. <br /> The QA/QC review identifies lab blanks with detections of target analytes and evaluates the <br /> effect of the detections on associated sample results. All lab blank analyses were determined <br /> acceptable by the laboratory. <br /> Field Blanks <br /> Field blanks detect possible constituent sources contributed from sampling methods and <br /> equipment. Examples include, but are not limited to, improperly cleaned sampling equipment, <br /> persistent airborne constituents in the sampling environment, and constituent sources in the <br /> sample containers. Three field blanks were collected during the 2023 First Semiannual sampling <br /> event(one blank in First Quarter 2023 and two blanks in Second Quarter 2023).1 <br /> Concentrations of constituents detected in field blanks are shown in Table D-1. Sodium and <br /> Total Dissolved Solids (TDS) were detected in the field blank collected on 1 February 2023, at <br /> concentrations of 19 milligrams per liter (mg/L) and 40 mg/L, respectively. The field blanks <br /> collected on 24 March 2023 and 4 April 2023 had no detections. <br /> 1 Field blanks were collected by pumping deionized water through the sample pump and a length of <br /> tubing. Sample bottles were filled, preserved, stored, and transported using the same procedures as used <br /> for the well water samples. Field blanks for total coliform analysis were collected by filling a new <br /> disposable bailer with deionized water and then filling the sample bottle from the bailer. In order to <br /> minimize potential contamination between wells,a clean pump is used for each sample. <br />
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