Swiss-Army Sentinels: Building a Case for the Bottlenose Dolphin (Tursiops truncatus) as a Tool to Study Plastic Pollution
IAAAM 2023
Miranda K. Dziobak1*+; Randall S. Wells2; Ed F. Wirth3; Emily C. Pisarski3; Brian C. Balmer4; Elizabeth B. McCabe2; Christina N. Toms2; John E. Weinstein5; Bonnie M. Ertel1,6; Tita Curtin7; Eric Conger8; Leslie B. Hart7
1Department of Environmental Health Sciences, University of South Carolina, Columbia, SC, USA; 2Chicago Zoological Society’s Sarasota Dolphin Research Program, c/o Mote Marine Laboratory, Sarasota, FL, USA; 3National Oceanic and Atmospheric Administration, National Ocean Service, National Centers for Coastal Ocean Science, Charleston, SC, USA; 4Dolphin Relief and Research, Clancy, MT, USA; 5Department of Biology, The Citadel, Charleston, SC, USA; 6CSS Inc., (Under Contract to NOAA/NOS/NCCOS), Charleston, SC, USA; 7Department of Health and Human Performance, College of Charleston, Charleston, SC, USA; 8Department of Biology, College of Charleston, Charleston, SC, USA

Abstract

Plastics are concerning to environmental health given their ubiquity and potential for adverse impacts to wildlife.1 Globally, 60% of the 380 million tons produced annually ends up in landfills or the natural environment.2 Coastal ‘hotspots’ of microplastics (particles <5 mm diameter) occur in urbanized areas near industrial and commercial activities, especially in estuarine habitats.3 The public health consequences of this pollution are significant considering the proportion of the world’s population living near the coast.

Sarasota Bay, located on the central west coast of Florida, is an urban watershed with residential, industrial, and commercial centers. Bottlenose dolphins in this area have been studied since 1970, including recent investigations of plastic and plasticizer (i.e., phthalate) exposure. As long-lived apex predators, resident dolphins (i.e., those that remain in the localized Sarasota Bay region for the majority of their lives) are sensitive gauges of environmental disturbances.4 This study used a sentinel species approach to better understand exposure risks for dolphins from plastics and endocrine-disrupting plasticizers in the marine environment.

Plastic exposure in Sarasota dolphins was presumed based on detection of a plasticizer (di2(ethylhexyl) phthalate [DEHP]) metabolite, methyl (2-ethylhexyl) phthalate (MEHP), or ingested particles suspected to be plastic. MEHP concentrations were quantified using liquid chromatography with tandem mass-spectrometry for urine collected during 2010–2019. Using a dissection microscope, ingested particles were quantified and visually characterized from dolphin gastric samples collected in 2019 and prey fish muscle collected in 2022. Plastic particles were confirmed using Fourier-transform Infrared spectroscopy.

MEHP was detected in 55% of dolphins sampled (n=51), with no significant sex- or age-related differences in concentrations (p>0.05).5 While detectable metabolites did not vary demographically, there was evidence of spatial influence. Ranging patterns differed between exposed and unexposed dolphins; dolphins with detectable MEHP were concentrated in the southern portion of the bay where land-use is primarily industrial and residential.6 Concentrations of MEHP were higher in Sarasota dolphins (p<0.05) compared to humans, suggesting the potential for endocrine disruption.7,8 In fact, free thyroxine was positively correlated with MEHP in adult dolphins (females p=0.04; males p=0.02) indicating potential impacts to thyroid homeostasis.9

While the source of DEHP exposure is uncertain, evidence points to a plastic origin. Of the 92 particles observed in gastric samples (n=7), 62% were suspected to be plastic, and at least one suspected plastic particle was observed in every dolphin. All suspected plastics were less than 5 mm in diameter (i.e., microplastics), and several polymers were identified (e.g., PVC zinc, polyethylene, polyamide).10 Additionally, fibers were prevalent in prey fish muscle, supporting trophic transfer, via consumption, as an exposure pathway. Our findings suggest dolphins can serve as a model to study the geographic scope and severity plastic pollution, as well as warn of potential seafood safety risks for human consumption.

Acknowledgements

We are grateful to the staff, collaborators, and volunteers of the Sarasota Dolphin Research Program for ensuring the safe capture, sampling, and release of the dolphins. Additionally, we would like to thank Amanda Moors for assistance with the collection of gastric samples and environmental blanks for this study. Funding for this work was provided by Dolphin Quest Inc., the Department of Health and Human Performance at the College of Charleston, and a grant from the National Institute of Environmental Health Sciences (Award No. R15ES034169). The animal sampling was reviewed and approved by Mote Marine Laboratory’s Institutional Animal Care and Use Committee (IACUC). Samples for this study were collected under Scientific Research Permit No. 20455 from the National Oceanic and Atmospheric Administration’s National Marine Fisheries Service.

*Presenting author
+Student presenter

Literature Cited

1.  Eriksen M, Lebreton LC, Carson HS, Thiel M, Moore CJ, Borerro JC, Galgani F, Ryan PG, Reisser J. 2014. Plastic pollution in the world’s oceans: More than 5 trillion plastic pieces weighing over 250,000 tons afloat at sea. PLoS One. 9(12):e111913. doi:10.1371/journal.pone.0111913.

2.  Geyer R, Jambeck JR, Law KL. 2017. Production, use, and fate of all plastics ever made. Sci. Adv. 3(7):e1700782. doi: 10.1126/sciadv.1700782.

3.  Su L, Sharp SM, Pettigrove VJ, Craig NJ, Nan B, Du F, et al. 2020. Superimposed microplastic pollution in a coastal metropolis. Water Res. 168:115140. doi:10.1016/j.watres.2019.115140.

4.  Wells RS, Rhinehart HL, Hansen LJ, Sweeney JC, Townsend FI, Stone R, et al. 2004. Bottlenose dolphins as marine ecosystem sentinels: developing a health monitoring system. EcoHealth. 1(3):246–254. doi: 10.1007/s10393-004-0094-6.

5.  Dziobak MK, Wells RS, Pisarski EC, Wirth EF, Hart LB. 2021. Demographic assessment of mono (2-ethylhexyl) phthalate (MEHP) and monoethyl phthalate (MEP) concentrations in common bottlenose dolphins (Tursiops truncatus) from Sarasota Bay, FL, USA. GeoHealth 5:e2020GH000348. doi: 10.1029/2020GH000348.

6.  Dziobak MK, Ballmer BC, Wells RS, Pisarski EC, Wirth EF, Hart LB. 2022. Temporal and spatial evaluation of mono(2-ethylhexyl) phthalate (MEHP) detection in common bottlenose dolphins (Tursiops truncatus) from Sarasota Bay, Florida, USA. Oceans. 3:231–249. https://doi.org/10.3390/oceans3030017.

7.  Hart LB, Dziobak MK, Pisarski EC, Wirth EF, Wells RS. 2020. Sentinels of synthetics - a comparison of phthalate exposure between common bottlenose dolphins (Tursiops truncatus) and human reference populations. PLoS One. 15(10):e0240506. doi: 10.1371/journal.pone.0240506.

8.  Meeker JD, Ferguson KK. 2014. Urinary phthalate metabolites are associated with decreased serum testosterone in men, women, and children from NHANES 2011–2012. J Clin Endocrinol Metab. 99(11):4346–4352. https://doi.org/10.1210/jc.2014-2555

9.  Dziobak MK, Wells RS, Pisarski EC, Wirth EF, Hart LB. 2022. A correlational analysis of phthalate exposure and thyroid hormone levels in common bottlenose dolphins (Tursiops truncatus) from Sarasota Bay, Florida (2010–2019). Animals 12:824. https://www.mdpi.com/2076-2615/12/7/824

10.  Hart LB, Dziobak M, Wells RS, Ertel B, Weinstein J. 2022. Microplastics in gastric samples from common bottlenose dolphins (Tursiops truncatus) residing in Sarasota Bay FL (USA). Front Mar Sci. 9:947124. doi: 10.3389/fmars.2022.947124.

 

Speaker Information
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Miranda K. Dziobak
Department of Environmental Health Sciences
University of South Carolina
Columbia, SC, USA


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