Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2021 Jan 6;16(1):e0243570.
doi: 10.1371/journal.pone.0243570. eCollection 2021.

An assessment of temporal, spatial and taxonomic trends in harmful algal toxin exposure in stranded marine mammals from the U.S. New England coast

Affiliations

An assessment of temporal, spatial and taxonomic trends in harmful algal toxin exposure in stranded marine mammals from the U.S. New England coast

Spencer E Fire et al. PLoS One. .

Abstract

Despite a long-documented history of severe harmful algal blooms (HABs) in New England coastal waters, corresponding HAB-associated marine mammal mortality events in this region are far less frequent or severe relative to other regions where HABs are common. This long-term survey of the HAB toxins saxitoxin (STX) and domoic acid (DA) demonstrates significant and widespread exposure of these toxins in New England marine mammals, across multiple geographic, temporal and taxonomic groups. Overall, 19% of the 458 animals tested positive for one or more toxins, with 15% and 7% testing positive for STX and DA, respectively. 74% of the 23 different species analyzed demonstrated evidence of toxin exposure. STX was most prevalent in Maine coastal waters, most frequently detected in common dolphins (Delphinus delphis), and most often detected during July and October. DA was most prevalent in animals sampled in offshore locations and in bycaught animals, and most frequently detected in mysticetes, with humpback whales (Megaptera novaeangliae) testing positive at the highest rates. Feces and urine appeared to be the sample matrices most useful for determining the presence of toxins in an exposed animal, with feces samples having the highest concentrations of STX or DA. No relationship was found between the bloom season of toxin-producing phytoplankton and toxin detection rates, however STX was more likely to be present in July and October. No relationship between marine mammal dietary preference and frequency of toxin detection was observed. These findings are an important part of a framework for assessing future marine mammal morbidity and mortality events, as well as monitoring ecosystem health using marine mammals as sentinel organisms for predicting coastal ocean changes.

PubMed Disclaimer

Conflict of interest statement

DE is affiliated with Integrated Statistics. ZW is affiliated with CCS Corporation. There are no patents, products in development or marketed products to declare. This does not alter our adherence to PLOS ONE policies on sharing data and materials.

Figures

Fig 1
Fig 1. Animal collection/sampling locations and detections of saxitoxin (presence/absence in at least one sample).
Fig 2
Fig 2. Animal collection/sampling locations and detections of domoic acid (presence/absence in at least one sample).
Fig 3
Fig 3. Correspondence analysis ordination for sub-region comparisons.
Positive values for dimension 1 correlate with larger proportion of positive domoic acid samples and negative values correlate with larger proportion of negative domoic acid samples. Positive values for dimension 2 correlate with larger proportion of positive saxitoxin samples and negative values correlate with larger proportion of negative saxitoxin samples. MA = Massachusetts, ME = Maine, NH = New Hampshire, OB = offshore/bycatch.
Fig 4
Fig 4. Correspondence analysis ordination for taxonomic group comparisons.
Positive values for dimension 1 correlate with larger proportion of positive domoic acid samples and negative values correlate with larger proportion of negative domoic acidsamples. Positive values for dimension 2 correlate with larger proportion of positive saxitoxin samples and negative values correlate with larger proportion of negative saxitoxin samples.
Fig 5
Fig 5. Correspondence analysis ordination for species comparisons.
Positive values for dimension 1 correlate with larger proportion of positive domoic acid samples and negative values correlate with larger proportion of negative domoic acid samples. Positive values for dimension 2 correlated with larger proportion of positive saxitoxin samples and negative values correlate with larger proportion of negative saxitoxin samples.
Fig 6
Fig 6. Frequency of animals testing positive for saxitoxin, domoic acid or either toxin, by month.
Fig 7
Fig 7. Correspondence analysis ordination for frequency comparisons by month of sampling.
Positive values for dimension 1 correlate with larger proportion of positive saxitoxin samples and negative values correlate with larger proportion of negative saxitoxin samples. Positive values for dimension 2 correlated with larger proportion of positive domoic acid samples and negative values correlate with larger proportion of negative domoic acid samples.
Fig 8
Fig 8. Animals testing positive for saxitoxin, domoic acid, or either toxin, by year.
Fig 9
Fig 9. Domoic acid and saxitoxin fecal concentrations (ng/g) detected in this study vs. previously reported values in Pacific U.S. marine mammals.
Box lines correspond to 25%, 50% and 75% quartiles, whisker lines correspond to 1.5 times the interquartile range, circle markers represent outliers beyond 1.5 times the interquartile range.

References

    1. Broadwater MH, Van Dolah FM, Fire SE. Vulnerabilities of marine mammals to harmful algal blooms In: Shumway SE, Burkholder JM, Morton SL, editors. Harmful Algal Blooms. Chichester, UK: John Wiley & Sons, Ltd; 2018. pp. 191–222.
    1. Fire SE, Van Dolah FM. Marine Biotoxins; Emergence of harmful algal blooms as health threats to marine wildlife New Directions in Conservation Medicine: Applied Cases of Ecological Health Oxford University Press, New York: 2012; 374.
    1. Landsberg JH. The effects of harmful algal blooms on aquatic organisms. Rev Fish Sci. 2002;10: 113–390.
    1. Scholin CA, Gulland F, Doucette GJ, Benson S, Busman M, Chavez FP, et al. Mortality of sea lions along the central California coast linked to a toxic diatom bloom. Nature. 2000;403: 80–84. 10.1038/47481 - DOI - PubMed
    1. Litz JA, Baran MA, Bowen-Stevens SR, Carmichael RH, Colegrove KM, Garrison LP, et al. Review of historical unusual mortality events (UMEs) in the Gulf of Mexico (1990–2009): Providing context for the multi-year northern Gulf of Mexico cetacean UME declared in 2010. Dis Aquat Organ. 2014;112: 161–175. 10.3354/dao02807 - DOI - PubMed

Publication types

LinkOut - more resources