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. 2024 May;86(4):363-374.
doi: 10.1007/s00244-024-01067-9. Epub 2024 May 18.

Mercury Concentrations in Feathers of Albatrosses and Large Petrels at South Georgia: Contemporary Patterns and Comparisons with Past Decades

Affiliations

Mercury Concentrations in Feathers of Albatrosses and Large Petrels at South Georgia: Contemporary Patterns and Comparisons with Past Decades

William F Mills et al. Arch Environ Contam Toxicol. 2024 May.

Abstract

Mercury (Hg) is an environmental contaminant that can negatively impact the health of humans and wildlife. Albatrosses and large petrels show some of the highest levels of Hg contamination among birds, with potential repercussions for reproduction and survival. Here, body feather total Hg (THg) concentrations were determined in breeding adults of five species of albatrosses and large petrels in the foraging guild at South Georgia during the mid-2010s. We tested the effects of species, sex and trophic ecology (inferred from stable isotopes) on THg concentrations and compared our results with published values from past decades. Feather THg concentrations differed significantly among species (range: 1.9-49.6 µg g-1 dw), and were highest in wandering albatrosses Diomedea exulans, intermediate in black-browed albatrosses Thalassarche melanophris and northern giant petrels Macronectes halli, and lowest in southern giant petrels M. giganteus and white-chinned petrels Procellaria aequinoctialis. Females were more contaminated than males in all species, potentially due to differences in distributions and diet composition. Across species, THg concentrations were not correlated with feather δ13C or δ15N values, implying that species effects (e.g., breeding and moulting frequencies) may be more important than trophic effects in explaining feather THg concentrations in this foraging guild. Within species, the only significant correlation was between THg and δ13C in wandering albatrosses, which could reflect higher Hg exposure in subtropical waters. Comparisons with THg concentrations from past studies, which reflect contamination from 10 to > 60 years ago, revealed considerable annual variation and some evidence for increases over time for wandering and black-browed albatrosses since before 1950 and from the late 1980s, respectively.

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Conflict of interest statement

The authors declare no competing interests.

Figures

Fig. 1
Fig. 1
Boxplots of total Hg concentrations (µg g−1 dw) in body feathers of albatrosses and petrels sampled at Bird Island, South Georgia. Species abbreviations are as follows: BBA = black-browed albatross Thalassarche melanophris; NGP = northern giant petrel Macronectes halli; SGP = southern giant petrel M. giganteus; WA = wandering albatross Diomedea exulans; WCP = white-chinned petrel Procellaria aequinoctialis. Samples were collected from southern giant petrels in the 2011/2012 breeding season and from all other species in 2014/2015. Species sharing superscript letters are not significantly different according to post-hoc Tukey’s HSD tests. Boxplots show medians (horizontal lines), interquartile range (IQR; boxes), the lowest and highest values within 1.5 × IQR (whiskers) and outliers (black points)
Fig. 2
Fig. 2
Mean (± SDs) and individual carbon (δ13C) and nitrogen (δ.15N) stable isotope values (‰) of body feathers of albatrosses and petrels sampled at Bird Island, South Georgia. Species abbreviations are: BBA = black-browed albatross Thalassarche melanophris; NGP = northern giant petrel Macronectes halli; SGP = southern giant petrel M. giganteus; WA = wandering albatross Diomedea exulans; WCP = white-chinned petrel Procellaria aequinoctialis. Samples were collected from southern giant petrels in the 2011/2012 breeding season and from all other species in 2014/2015. Grey vertical shaded areas and text reflect the approximate locations of biogeographic boundary zones (Phillips et al. 2009)
Fig. 3
Fig. 3
Boxplots of (a) carbon (δ13C) and (b) nitrogen (δ15N) stable isotope values (‰) in body feathers of albatrosses and large petrels sampled at Bird Island, South Georgia. Species abbreviations are: BBA = black-browed albatross Thalassarche melanophris; NGP = northern giant petrel Macronectes halli; SGP = southern giant petrel M. giganteus; WA = wandering albatross Diomedea exulans; WCP = white-chinned petrel Procellaria aequinoctialis. Samples were collected from southern giant petrels in the 2011/2012 breeding season and from all other species in 2014/2015. Species sharing superscript letters are not significantly different according to post-hoc Dunn’s tests. Boxplots show medians (horizontal lines), interquartile range (IQR; boxes), the lowest and highest values within 1.5 × IQR (whiskers) and outliers (black points)
Fig. 4
Fig. 4
Relationships between body feather total Hg (THg) concentrations (µg g−1 dw) and (a) δ13C and (b) δ15N values (‰) of body feathers of albatrosses and large petrels; and (c) relationships between feather THg concentrations and δ13C values of wandering albatross Diomedea exulans sampled at Bird Island, South Georgia. Species abbreviations are: BBA = black-browed albatross Thalassarche melanophris; NGP = northern giant petrel Macronectes halli; SGP = southern giant petrel M. giganteus; WA = wandering albatross; WCP = white-chinned petrel Procellaria aequinoctialis

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References

    1. Albert C, Renedo M, Bustamante P, Fort J. Using blood and feathers to investigate large-scale Hg contamination in Arctic seabirds: a review. Environ Res. 2019;177:108588. doi: 10.1016/j.envres.2019.108588. - DOI - PubMed
    1. Anderson ORJ, Phillips RA, McDonald RA, Shore RF, McGill RAR, Bearhop S. Influence of trophic position and foraging range on mercury levels within a seabird community. Mar Ecol Prog Ser. 2009;375:277–288. doi: 10.3354/meps07784. - DOI
    1. Appelquist H, Asbirk S, Drabæk I. Mercury monitoring: mercury stability in bird feathers. Mar Pollut Bull. 1984;15:22–24. doi: 10.1016/0025-326X(84)90419-3. - DOI
    1. Arcos JM, Ruiz X, Bearhop S, Furness RW. Mercury levels in seabirds and their fish prey at the Ebro Delta (NW Mediterranean): the role of trawler discards as a source of contamination. Mar Ecol Prog Ser. 2002;232:281–290. doi: 10.3354/meps232281. - DOI
    1. Barrett RT, Camphuysen K, Anker-Nilssen T, Chardine JW, Furness RW, Garthe S, Hüppop O, Leopold MF, Montevecchi WA, Veit RR. Diet studies of seabirds: a review and recommendations. ICES J Mar Sci. 2007;64:1675–1691. doi: 10.1093/icesjms/fsm152. - DOI