Clemson University TigerPrints All Dissertations Dissertations 5-2017 Toxicity of Microplastics to Aquatic Organisms Sarah Au Clemson University, [email protected] Follow this and additional works at:https://tigerprints.clemson.edu/all_dissertations Recommended Citation Au, Sarah, "Toxicity of Microplastics to Aquatic Organisms" (2017).All Dissertations. 1877. https://tigerprints.clemson.edu/all_dissertations/1877 This Dissertation is brought to you for free and open access by the Dissertations at TigerPrints. It has been accepted for inclusion in All Dissertations by an authorized administrator of TigerPrints. For more information, please [email protected]. TOXICITY OF MICROPLASTICS TO AQUATIC ORGANISMS A Dissertation Presented to the Graduate School of Clemson University In Partial Fulfillment of the Requirements for the Degree Doctor of Philosophy Environmental Toxicology by Sarah Au May 2017 Accepted by: Dr. Cindy M. Lee, Committee Chair The late Dr. Stephen J. Klaine Dr. Peter H. Adler Dr. William S. Baldwin Dr. Peter van den Hurk Dr. John E. Weinstein ABSTRACT Plastic is used in products that span from cutlery to the main components in automobiles, and airplanes. Both municipal solid waste streams and marine debris are comprised of largely plastic products, and as annual global plastic production and use is unlikely to decrease, the presence of plastic in the environment will likely increase. Microplastics (MPs) are plastic fragments that have at least one dimension that is less than 5 mm, and have been found throughout water bodies around the world. MPs are in the same size fraction as most sediment particles and microorganisms, allowing them to be easily ingested by a variety of organisms. The potential for MPs to alter the bioavailability of contaminants, and whether MPs and adsorbed contaminants can undergo trophic transfer, have been investigated in very few studies. Fluoranthene (FLU) is one of the US Environmental Protection Agency’s 16 priority polycyclic aromatic hydrocarbons; and its hydrophobic nature allows it to sorb easily to sediment and organic matter, which suggests FLU will sorb to the hydrophobic surfaces of most MPs. While most studies conducted have focused on acute MP exposures to marine organisms, little is known regarding the toxicological chronic effects of MP exposures. Recent studies have demonstrated that MP concentrations in freshwater water bodies are comparable to those found in the ocean; even less information is available regarding MP toxicity to freshwater organisms. The first objective of my research was to characterize the physical toxicity of MPs to aquatic invertebrates and fish. After establishing a baseline for acute MP toxicity, the second objective focused on the determination of whether fluoranthene that is adsorbed to ii MP surfaces is bioavailable to aquatic invertebrates and fish. Finally, the third objective evaluated whether MPs and the adsorbed fluoranthene can undergo trophic transfer between prey and predatory organisms in both freshwater and marine ecosystems. My results demonstrated that acute exposures to polyethylene spherical MP do result in mortality at environmentally relevant concentrations. Specifically, 10- and 7- day LC s of approximately 4.6 x 104 and 7.9 x 104 MPs/mL for spherical polyethylene 50 MPs were quantified for amphipods and copepods, respectively. No mortality was observed for either fathead minnows or mummichogs at MP exposures used during these bioassays. Interestingly, polypropylene MP fibers were more toxic to exposed amphipods than the polyethylene MP spheres, where mortality was observed at concentrations as low as > 22.5 MPs/mL. When polyethylene spherical MPs are contaminated with FLU, acute exposures can result in an increase in FLU bioavailability to both fish and invertebrates. Chronic polyethylene spherical MP exposures resulted in significant growth reductions in both Hyalellla azteca and Amphiascus tenuiremis, and decreased reproduction in exposed H. azteca. In comparison to polyethylene spherical MPs, fibrous polypropylene MP exposures to H. azteca resulted in significantly greater mortality and reductions in both growth and reproduction. Exposure to FLU- contaminated MPs resulted in an increase in FLU bioavailability to invertebrates and fish, where more than 90% of the invertebrate FLU body burdens were due to MP exposure. Finally, my results demonstrated that FLU that was adsorbed to MP surfaces can undergo trophic transfer using both freshwater and marine invertebrates and fish. Approximately 1.5 mg fluoranthene was bioavailable to fathead minnows and mummichogs that had iii ingested amphipods, and copepods that had been pre-exposed to fluoranthene- contaminated MPs, respectively. Hybrid striped bass that has consumed fathead minnows that were pre-exposed to fluoranthene-contaminated MPs resulted in an average bile concentration of approximately 1.3 mg fluoranthene. MPs represent another route of exposure for ubiquitous persistent organic pollutants in the environment for lower and higher trophic level organisms. My research provided a platform on which the acute and chronic toxicological effects due to MP exposures of freshwater and marine invertebrates and fish can be compared because similar methods were used in all the bioassays. Generating data that resulted from the use of similar exposure methods allows the scientific community to make cross-species comparisons that are difficult to determine with the currently available microplastic toxicity data. My results demonstrate that microplastics can have both acute and chronic toxicological effects on aquatic organisms, and that the presence of microplastics in the environment needs to be taken into consideration when evaluating the exposure to environmental contaminants. iv DEDICATION I dedicate my dissertation to my family and friends. v ACKNOWLEDGMENTS I cannot express how thankful I am to have had the opportunity to study under my PhD adviser, Dr. Stephen J. Klaine. It is easy to say that he was a great teacher and mentor, but it is a rare gift to be able to say that one’s adviser was also a friend, father- figure, and colleague. The science that I learned from him will carry me through my future career decisions, and the people I have met through him are not just professional acquaintances, but are some of the most amazing friends one could ever have. Professionally and personally, I am a better scientist, and person because of Steve Klaine. Hopefully I am a little better at seeing one tree at a time, and not just the whole forest. My committee members also deserve a round of applause. Everyone has contributed to being a solid support system that I hesitate to think of what the last year would have been like without them. I wholeheartedly thank Dr. Cindy M. Lee for being an amazing mentor and friend. You have been a steadying presence in my life for the past year, and I don’t think I could have finished my dissertation without your help. Thank you for taking the time to correct all my writing errors. This may seem trivial, but I “believe” I am a better writer now. Any future collaborator or correspondent will have you to thank as well. I am grateful that through Sea Grant, and my dissertation work, I was given the opportunity to collect microplastics in Charleston and Georgetown, SC, with Dr. John Weinstein and his students. Getting a different perspective on microplastic sampling techniques made me more aware of the various abiotic and biotic processes that influence contaminant transport and fate in the environment. Thank you for your guidance at my platform presentations. It is always good to have a friendly face around. vi A special thanks to Dr. Peter Adler for opening his lab to me, so that I could develop better methods to image my invertebrates. I believe that our discussions on science as a whole and how my work is influenced by other worldly events has given me a better view on how to connect with individuals that do not have the same research background. Thank you for taking the blinders off occasionally, and giving me a chance to truly reflect on different aspects of my research. I am grateful that Dr. William Baldwin has also opened his lab for me, so that I could explore different methods to better extract fluoranthene from my tissue samples. Thank you for allowing me to use some of the instruments in your lab. Finally, a special thank you to Dr. Peter van den Hurk for being a mentor throughout my five years as a graduate student, and becoming a committee member for me in my last year. Thank you for also opening your lab to me, and helping me with method development. I would like to acknowledge and thank Ron Gossett, Norm Ellis, and John Smink for their assistance with animal culture and maintaining facilities at both the Institute of Environmental Toxicology and Cherry Farm. None of my work could have been accomplished without you because you were always helping us whenever an extra hand was needed. ‘Thank you’ is a phrase that does not quite amount to the gratitude I feel. I would also like to thank all past and present Klaine lab members. The research projects that everyone had are so different, and I believe that I benefitted from having so many types of methods and perspectives on toxicology surrounding me every day. Thank you to Kim Newton, Austin Wray, Lauren Sweet, Anna Lee McLeod, Katherine Johnson- Couch, Erica Linard, Lauren Stoczynski, Jason Coral, and Chad Mansfield for helping vii with fish culture, lab inspection cleanings, and giving me a support system throughout the last five years. A special thanks to Lauren Sweet and Chad Mansfield for helping me count copepods during a few bioassays. I would also like to thank Dr. Tom Chandler and Emily Stewart at the University of South Carolina for providing me with copepods to use in my toxicity bioassays. Thank you, Paul Kenny, for assisting us in the collection of pluff mud and mummichogs at the Belle W. Baruch Institute of Coastal Ecology and Forest Science. There are many experiments that would not have been conducted if you had not helped me on so many occasions. Thank you, Austin Gray, for helping me on countless field collection trips in Charleston and Georgetown, SC. I am so glad that we were able to become both colleagues and friends through these trips and various conference meetings. I would also like to thank Dana Szymkowicz and Kaleigh Sims from Dr. Lisa Bain’s lab for helping me with mummichog collection and embryo fertilization. Thank you, Drs. Lisa Bain and Charlie Rice, for helping me develop methods for various experiments in the last few years, and giving me advice regarding mummichog collection and culture. Establishing the What’s in Our Water Jr. Program would not have been possible without the help of Janine Sutter, Cathleen Reas, Laura Nash, and the numerous mentors from Clemson University that helped make science fun for elementary students. Participating in this program has given me a refreshing outlook on my research and a different platform on which to relate my research to the interests of people in different age groups and personal interests. viii Finally, a huge thank you to my mother, father, brother, and sister. Your patience with my schedule has helped me get through the last few years and I am so glad to finally be back in the Maryland-DC area so that the time between visits are not as long. Thank you to all my friends that are scattered between the two coasts for taking the time to maintain our friendships despite everyone having such crazy schedules. I would also like to thank Jacob for making the multiple trips to South Carolina every year so that we can explore various cities in the south. Thank you for listening to all my problems, and helping me cope with all the stress. A general thank you to everyone I have met during my five years at Clemson University. Your patience, guidance, and friendship though out this whole experience has made this dissertation possible. ix
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