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Okaloosa County BOCC — December 6, 2016 — Gap Creek QAPP — reading text
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above) for preparation of equipment blanks. To
collect the equipment blank, the laboratory deionized water will be poured through the
Nalgene sampler and into a pre-cleaned laboratory provided bottle. The equipment blank
will be shipped along with the field samples to the laboratory.
Equipment blanks will also be collected from the dipper if used for grab sampling after
the dipper has been decontaminated.
3.3 Laboratory Control Sample
The LCS is a clean-matrix QC sample that is spiked with a known amount of target
compounds. The LCS is carried through the analytical process with the field samples. Its
purpose is to monitor the effectiveness and efficiency of the analytical process at
recovering target compounds.
3.4 Corrective actions in the event of QC problems
If QC results indicate problems with the data, corrective action will be taken, which can
include any of the below processes:
Retrieving missing information
Re-calibrating the measurement system
Re-analyzing samples (within holding time requirements)
Collecting additional samples
Qualifying results.
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4 Data Management Procedures
4.1 Sample Collection Records
The recording and reporting of results of these monitoring events shall be in accordance
with the specifications in Attachment J, Quality Assurance Requirements, of the
Agreement, in Section 4.
4.2 Laboratory Data
The data package from the laboratory will include a case narrative discussing any
problems with the analyses, corrective actions taken, changes to the referenced method,
and an explanation of data qualifiers. QC results associated with the data will also be
included in the lab data package.
The laboratory will provide all QC sample results and raw data in addition to the field
sample results. This data package will be submitted in electronic format for review.
All QC data will be included in the data report. Any errors with quality control will be
noted in the data package. If the results do not fall within established control limits, the
measurement system should be re-calibrated. The following minimum qualifications will
be made, as necessary, by the laboratory:
U = Analyte is not detected
J = Analyte concentration less than the QL listed in Table 2 but above the DL.
The J-qualifier may also address additional QC deficiencies which will be
described in the laboratory case narrative.
4.3 Data Verification and Validation
4.3.1 Data Verification
All analytical data generated during this study will be reviewed by the Laboratory Quality
Assurance Manager (QAM). The QAM will ensure that:
Data are consistent, correct, and complete, with no errors or omissions
Results from the lab and field QC samples accompany the results
Established criteria for QC results are met
Data qualifiers are properly assigned where necessary
Data specified in the Sampling Process Design were obtained
Measurement procedures used to generate the data are those specified in this
QAPP
4.3.2 Data Validation
Data will be validated by HDR for the PARCCS parameters. Data will be qualified during
data validation when PARCCS parameter MQOs as specified in Section 2.4 are not met.
Data will be validated according to the USEPA Functional Guidelines (August 2014), and
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final qualifiers will be R (rejected), J (estimated), U (not detected) and UJ (not detected,
with an estimated reporting limit).
Also, 100 percent of the data in the data tables that will be uploaded into STORET will be
checked for accuracy against the data reported in the data package.
4.4 Data Upload
As per grant requirements, monitoring results will be uploaded to the USEPA STORET
database or the successor database to STORET by HDR. Data will be maintained by
HDR in an electronic and hard copy form for a period of no less then three years
following the final report. Data will be flagged following laboratory and HDR QC
evaluations.
4.5 Data Quality Assessment
If MQOs have not been met for data, HDR will determine if data is still usable. If data are
found to be inadequate to meet study objectives, corrective action may be taken
including, but not limited to:
Notifying the laboratory to re-analyze samples (if within the holding time
requirements)
Re-collecting samples
Altering the sample collection method
Altering the measurement method
4.6 Audits and Reports
The laboratories, in order to obtain their certifications with the Florida Department of
Health, have been audited and accredited that they are technically competent and able
to generate data of known and documented quality. It is therefore not anticipated that the
labs will need to be further audited, nor will they need to analyze additional quality control
check samples (QCCS) as indicated in Addendum 1, Quality Control Requirements for
Laboratories Performing Chemical Analyses, of the Agreement.
4.7 Field Monitoring Report
Monitoring results will be uploaded to the USEPA STORET database or the successor
database to STORET. Through the STEPL program, an estimate reduction load for
sediment, (TSS as estimated through the PLOAD model) will be reported.
The following deliverables will be provided to gauge the effectiveness of the BMP
Four quarterly reports of the sampling results
Analysis of collected data with a Draft and Final Project Report
Records of data uploaded to the EPA STORET database.
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5 References
State of Florida, DEP Agreement No. G0326, State of Florida Grant Agreement Pursuant
to Environmental Protection Agency Grant Awards.
United States Environmental Protection Agency (USEPA), EPA Requirements for Quality
Assurance Project Plans, EPA QA/R-5, EPA/240B-01/003 (March 2001).
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