Abstract

Among killer whale forms, type C is a fish-eating form and is the most common in the Ross Sea. In the austral summer 2015, a study was conducted to evaluate the toxicological hazard these marine mammals face in the Antarctic ecosystem. Seven biopsy samples were collected from adult individuals (five males and two females) in the surroundings of the Italian Research Station Mario Zucchelli, Terra Nova Bay, by remote dart sampling from the pack ice. The accumulation levels of persistent organic pollutants (POPs) such as legacy (DDTs, PCBs, and HCB) and emerging (PBDEs and DP) were measured. Moreover, the protein expression of cytochrome P450 (CYP1A1 and 2B) and the mRNA level variations of the peroxisome proliferator-activated receptors α and γ (PPARα-γ) and the estrogen receptor α (ERα), aryl hydrocarbon receptor (AhR), andCyp1awere evaluated. Twenty PCB congeners, six DDTs, HCB, three HCHs, and fourteen brominated BDEs and DP-syn and anti-isomers were analyzed on freeze-dried blubber biopsy samples by GC-MS. The protein expression was evaluated by Western Blot and the mRNA levels were quantified by quantitative real-time PCR. The average abundance pattern for the contaminants was DDTs > PCBs > HCB > HCHs ≈ PBDEs >> DP. Contaminant levels resulted to be lower when compared to the existing data from the Antarctic type C killer whales from the McMurdo Sound (Ross Sea) and those reported for fish-eating killer whales worldwide. The mRNA levels of the five target genes were successfully quantified, but no statistical correlation was found with POP levels, suggesting that either the low levels of quantified POPs in blubber may not significantly affect the biological responses investigated, or that other stressors could contribute to the alterations of the molecular biomarkers. Although the results showed a lower risk related to contamination compared to more impacted areas, this study provides baseline data for the conservation of this species in an area with high ecological value, recently declared as the largest Marine Protected Area in Antarctica, where pollutants should remain at minimum levels despite increasing multiple stresses existing in the region.

Highlights

  • Killer whales (Orcinus orca) can be found in all marine regions, ranging from the polar areas to the equator (Pitman and Ensor, 2003; Lauriano et al, 2011)

  • The relative abundance of the contaminants analyzed followed the order DDTs > polychlorinated biphenyls (PCBs) > HCB > HCHs ≈ polybrominated diphenyl ethers (PBDEs) >> Dechlorane plus (DP). This pattern of abundance is similar to what has been described for type C killer whale specimens sampled at the Ross Sea in 2005/2006 and reported by Krahn et al (2008)

  • This pattern was similar to that reported for toothfish (Dissostichus mawsoni) from the same area by Corsolini et al (2017), which is relevant since toothfish is assumed to be among the main prey of type C KW foraging in the Ross Sea (Krahn et al, 2008; Lauriano et al, 2020)

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Summary

Introduction

Killer whales (Orcinus orca) can be found in all marine regions, ranging from the polar areas to the equator (Pitman and Ensor, 2003; Lauriano et al, 2011). Differences in habitat, as well as prey preferences, diet specialization, behavior, and group size are elements that make it possible to distinguish five killer whale ecotypes in the Southern Ocean (Pitman et al, 2018). Among these five types A, B (1 and 2), C, and D, the most common ecotype in the Ross Sea is the C form, known as the Ross sea killer whale (RSKW). A recent study from Lauriano et al (2020) revealed RSKW movements and inferred the presence of feeding grounds in the eastern Ross Sea coastal area and a traveling behavior outside the polar front

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