Study Details

Study ID:  MRED0003

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Study Basics

Study IDMRED0003
Study NameAssessing Dioxin in Groundwater, Lower Yakima Valley
EIM Data Entry Review StatusNot Reviewed
Study TypeGeneral environmental study
Study PurposeTo assess dioxin in groundwater in the lower Yakima valley.
Field Collection Date Range11/4/2019 - 4/28/2021
Data First/Last Loaded Date
Data Last Updated Date
Ecology Program or Other Responsible EntityEcy Environmental Assessment Program
Ecology ContactMelanie Redding
Ecology Monitoring Program
Submitting OrganizationWA Department of Ecology
Study QA Planning LevelLEVEL 4: Approved QAPP or SAP.
Study QA Project Plan Description
Study QA Assessment LevelLevel 1: Data neither Verified nor Assessed for Usability
Study Result DescriptionLink to technical memo on Ecology webpage: https://tinyurl.com/2hvre8rh
Study CommentQuality assurance measures are important for credible data. For this study, Ecology used quality assurance and quality control practices for dioxins to figure out the levels of background contamination, limits of detection, and the variability of sample results. The laboratory method to analyze dioxins is very sensitive, and cross-contamination can easily occur. Dioxins are found throughout the world in our environment. They are found mostly in soil, sediment, and food. Very low levels are found in plants, water, and air. Because of this, numerous blank samples were analyzed in order to determine the threshold at which dioxins in well water samples could be distinguished from dioxins already present in the environment and the analytical and sampling processes. Blank samples are ultra-pure water that is free of dioxins and supplied by the laboratory. These blank samples were sent back to the lab along with the other samples. The types of blanks analyzed for this study included laboratory and field blanks. Laboratory blanks consist of pure water samples that are analyzed along with the collected samples. Three types of field blanks were used: travel blanks, transfer blanks, and an equipment blank. Replicates of some types of blanks were used during each 3-day sampling event. Three travel blanks were analyzed during each sampling event (one blank for each day of the three days of sampling). Travel blanks remained in the vehicle the samplers drove to each sampling site, but were never opened. Blank samples help determine where contamination may be occurring during the sampling and analytical process. Dioxins that were present in these unopened bottles, both laboratory and field blanks, are referred to as “noise” or “background” contamination. To fully comprehend the data contained in this study, please also take a look at the dioxin levels found in the travel blanks, transfer blanks, and equipment blanks.
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