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2023-10-03_REVISION - M1977344 (22)
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2023-10-03_REVISION - M1977344 (22)
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Last modified
10/5/2023 8:56:09 AM
Creation date
10/4/2023 10:41:27 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977344
IBM Index Class Name
Revision
Doc Date
10/3/2023
Doc Name Note
App 4.5 Red Creek Quarry Baseline Water Information
Doc Name
Request For Amendment To Permit
From
Holcim (US) Inc.
To
DRMS
Type & Sequence
AM2
Email Name
TC1
MAC
Media Type
D
Archive
No
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Red Creek Quarry Baseline Water Investigation Section 4 <br /> <br /> <br />4-6 <br />DRAFT for review purposes only. Use of contents on this sheet is subject to the limitations specified at the end of this document. <br />4.5 Quality Assurance/Quality Control and Data Validation <br />A pre-defined number of samples were collected as part of the QA/QC program described in the <br />Quality Assurance Project Plan (QAPP) (BC 2023a, Appendix 3.6). Field QC included duplicates, <br />equipment blanks, and matrix spike (MS)/matrix spike duplicate (MSD) sample collection. Laboratory <br />QC included method blank, laboratory control sample (LCS), LCS duplicate (LCSD), MS/MSD, <br />surrogate spikes, and internal standards. <br />4.5.1 Duplicates <br />Duplicates were collected so that the parent and duplicate sample containers were filled <br />consecutively (e.g., parent bottle was filled then the duplicate bottle was filled immediately <br />afterward). This process was conducted until all sample bottles for the complete list of analytes were <br />filled. Surface and groundwater duplicate samples were collected at a frequency of one per sampling <br />event for each water source. Duplicate samples were submitted to the laboratory “blind” meaning <br />the sample identification number used on the duplicate samples and the time of the duplicate <br />sample collection were not included in the documentation provided to the laboratory. <br />4.5.2 Equipment Blanks <br />The only non-dedicated sampling equipment was the water level meter which was cleaned with <br />distilled water and Liquinox between each well. Equipment blanks were collected by pouring <br />laboratory-provided deionized or commercially available distilled water over the water level probe <br />and into the sample containers (Photo 4-6). The equipment blank samples were field filtered, <br />preserved, and handled and transported in the same manner as the other samples in accordance <br />with the QAPP. Equipment blanks were collected at a frequency of one per sampling event. <br /> <br />Photo 4-6. Example of collecting the equipment blank
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