Monitoring microplastics in drinking water: An interlaboratory study to inform effective methods for quantifying and characterizing microplastics
Graphical abstract
Introduction
Microplastics represent a potential threat to human health, with exposure through the air we breathe (Chen et al., 2020; Gasperi et al., 2015), the food we eat (Cox et al., 2019; EFSA Panel on Contaminants in the Food Chain (CONTAM), 2016), and the water we drink (Eerkes-Medrano et al., 2019). While further research is needed to understand biological fate and toxicity of microplastics in humans (Barboza et al., 2018; Carbery et al., 2018; Rist et al., 2018), there is sufficient evidence to impose a precautionary approach for monitoring and mitigation of microplastics in drinking water (Danopoulos et al., 2020; Leslie and Depledge, 2020; Senathirajah et al., 2021).
Drinking water exposure has become a focal point for the State of California, which has a legislative mandate (Senate Bill 1422) to enact routine monitoring, including adoption of standard methods for implementing that requirement (Wyer et al., 2020). Such methods do not currently exist, though there is a growing body of research from which to draw. Microscopy is a useful pre-screening tool for enumerating microplastic particles and is a comparatively quick method with low upfront and equipment costs (Primpke et al., 2020). Fourier-Transform Infrared (FTIR) and Raman spectroscopy are often used to confirm microplastic particle counts by providing chemical confirmation of material type. Several studies have previously demonstrated the capabilities of these methods (Cabernard et al., 2018; Käppler et al., 2016; Xu et al., 2019).
Establishment of standard methods for management application requires several additional steps beyond publishing methods in peer-reviewed journals. Management application requires development of a detailed standard operating procedure with sufficient specificity to ensure repeatability across laboratories. It also requires a multi-laboratory method evaluation study to determine performance characteristics, including demonstration of whether the precision and accuracy of the chosen methods are suitable for the intended purpose. These data serve as a foundation for the development of laboratory accreditation, which define expectations for well-performing laboratories.
There have been several interlaboratory studies assessing microplastic methods performance across laboratories with blind microplastic samples (Cadiou et al., 2020; Isobe et al., 2019; Michida et al., 2019; Müller et al., 2020; Van Mourik et al., 2021). However, none have been conducted using specific prescribed methodologies, which results in high of variability among labs and across methods. In addition, all these studies except for one (Müller et al., 2020) have been limited to particles larger than 50 μm, which is problematic because drinking water is typically filtered to at least this size and monitoring needs to focus on smaller particles that can potentially pass through filters (Na et al., 2021).
Here we present a multi-laboratory validation study using three microplastic measurement methods: stereomicroscopy, Raman spectroscopy, and FTIR spectroscopy. For each, we establish performance characteristics, including accuracy and precision. We also establish the time requirements to implement such methods, necessary for use in required monitoring. The study included laboratories from around the world with a range of experience, and all received samples spiked with diverse particle shapes, densities, colors and sizes, a strict protocol to follow for extraction, particle identification, counting and chemical identification. These results collectively inform recommendations for microplastic analysis in drinking water, for monitoring programs within the State of California and beyond.
Section snippets
Materials and methods
Participants were from 22 laboratories in the United States, Canada, Germany, China, Australia, and Norway. The study benefitted from diversity in institutions, laboratory practice, and experience by including laboratories from different countries. The study was conducted ‘blind’, and participating laboratories did not know any details of the spiked particle content within each sample.
Laboratories were asked to follow a strict protocol (Appendix A.1), in which particles were extracted, then
Results
Twenty-two laboratories submitted results for at least one method. All laboratories submitted results for microscopy and counted particles in size fractions >20 μm. Of the 22 laboratories, 13 did not count particles in the 1–20 μm size fraction. Seventeen laboratories submitted results for their blank sample. For chemical identification, 11 laboratories used FTIR spectroscopy and 9 used Raman spectroscopy.
Discussion
Overall, the methods used in this study are fit for purpose to quantify and characterize microplastics in drinking water for most applications. Below we discuss the variables that affected the recovery and precision of our results and the applicability of this work to the monitoring of microplastics in drinking water.
This study included a SOP for all labs to follow, which is unique to other method evaluation studies (Cadiou et al., 2020; Isobe et al., 2019; Michida et al., 2019; Müller et al.,
Conclusions
Method performance was highly dependent on particle size, with good recovery for particles >50 μm. Both FTIR and Raman spectroscopy were effective at identifying microplastic particles and differentiating from non-plastics but there were performance differences based on particle size. FTIR could accurately identify polymer types for particles in size fractions above 20 μm whereas Raman did so for particles in size fractions above 1 μm. This size issue is of concern for sampling drinking water
Author contributions
Hannah De Frond: Conceptualization, Methodology, Validation, Formal analysis, Data curation, Writing – original draft, Writing – review & editing, Visualization. Leah Thornton Hampton: Methodology, Formal analysis, Data curation, Visualization, Writing – review & editing. Syd Kotar: Validation, Investigation, Resources, Data curation, Writing – review & editing. Kristine Gesulga: Methodology, Validation, Investigation, Writing – review & editing. Cindy Matuch: Data curation, Investigation.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
We thank all participants of the study including: Alfred-Wegener-Institute; Algalita Marine Research and Education; Barnett Technical Services; BASF; California Department of Public Health; California State University (Bakersfield); California State University (Channel Islands); Carollo Engineers Inc., East China Normal University; Eastman Chemical Company; U.S. Environmental Protection Agency; Eurofins (Australia, Norway, US); HORIBA Scientific; Innovations institut für Nanotechnologie und
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