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Is the southern crab Halicarcinus planatus (Fabricius, 1775) the next invader of Antarctica?

The potential for biological colonization of Antarctic shores is an increasingly important topic in the context of anthropogenic warming. Successful Antarctic invasions to date have been recorded exclusively from terrestrial habitats. While non‐native marine species such as crabs, mussels and tunica...

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Published in:Global change biology 2021-08, Vol.27 (15), p.3487-3504
Main Authors: López‐Farrán, Zambra, Guillaumot, Charlène, Vargas‐Chacoff, Luis, Paschke, Kurt, Dulière, Valérie, Danis, Bruno, Poulin, Elie, Saucède, Thomas, Waters, Jonathan, Gérard, Karin
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cited_by cdi_FETCH-LOGICAL-c4224-fcea2616d6de8382a97fa7d4da1536e98ecdf2b2018cc447fa94e976c6a4a4fa3
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creator López‐Farrán, Zambra
Guillaumot, Charlène
Vargas‐Chacoff, Luis
Paschke, Kurt
Dulière, Valérie
Danis, Bruno
Poulin, Elie
Saucède, Thomas
Waters, Jonathan
Gérard, Karin
description The potential for biological colonization of Antarctic shores is an increasingly important topic in the context of anthropogenic warming. Successful Antarctic invasions to date have been recorded exclusively from terrestrial habitats. While non‐native marine species such as crabs, mussels and tunicates have already been reported from Antarctic coasts, none have as yet established there. Among the potential marine invaders of Antarctic shallow waters is Halicarcinus planatus (Fabricius, 1775), a crab with a circum‐Subantarctic distribution and substantial larval dispersal capacity. An ovigerous female of this species was found in shallow waters of Deception Island, South Shetland Islands in 2010. A combination of physiological experiments and ecological modelling was used to assess the potential niche of H. planatus and estimate its future southward boundaries under climate change scenarios. We show that H. planatus has a minimum thermal limit of 1°C, and that its current distribution (assessed by sampling and niche modelling) is physiologically restricted to the Subantarctic region. While this species is presently unable to survive in Antarctica, future warming under both ‘strong mitigation’ and ‘no mitigation’ greenhouse gas emission scenarios will favour its niche expansion to the Western Antarctic Peninsula (WAP) by 2100. Future human activity also has potential to increase the probability of anthropogenic translocation of this species into Antarctic ecosystems. No decapod is currently established in the shallow Antarctic coastal waters. Halicarcinus planatus (Brachyura, Hymenosomatidae) has been observed once in the Shetland Islands in 2010. Here, the thermotolerance of this crab is evaluated and demonstrated that H. planatus can not persist in Antarctica under the present extreme conditions; however, following IPCC climate prediction (RCP 8.5), in 2100, this species may find a suitable habitat in the Antarctic Peninsula. (a) Survival rate of H. planatus from cold to polar temperatures during 90 days. Probability, from 0 (yellow) to 1 (red), associated with H. planatus geographic distribution around the Antarctic Peninsula: under present conditions (b) and IPCC RCP 8.5 climate scenario (c).
doi_str_mv 10.1111/gcb.15674
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Successful Antarctic invasions to date have been recorded exclusively from terrestrial habitats. While non‐native marine species such as crabs, mussels and tunicates have already been reported from Antarctic coasts, none have as yet established there. Among the potential marine invaders of Antarctic shallow waters is Halicarcinus planatus (Fabricius, 1775), a crab with a circum‐Subantarctic distribution and substantial larval dispersal capacity. An ovigerous female of this species was found in shallow waters of Deception Island, South Shetland Islands in 2010. A combination of physiological experiments and ecological modelling was used to assess the potential niche of H. planatus and estimate its future southward boundaries under climate change scenarios. We show that H. planatus has a minimum thermal limit of 1°C, and that its current distribution (assessed by sampling and niche modelling) is physiologically restricted to the Subantarctic region. While this species is presently unable to survive in Antarctica, future warming under both ‘strong mitigation’ and ‘no mitigation’ greenhouse gas emission scenarios will favour its niche expansion to the Western Antarctic Peninsula (WAP) by 2100. Future human activity also has potential to increase the probability of anthropogenic translocation of this species into Antarctic ecosystems. No decapod is currently established in the shallow Antarctic coastal waters. Halicarcinus planatus (Brachyura, Hymenosomatidae) has been observed once in the Shetland Islands in 2010. Here, the thermotolerance of this crab is evaluated and demonstrated that H. planatus can not persist in Antarctica under the present extreme conditions; however, following IPCC climate prediction (RCP 8.5), in 2100, this species may find a suitable habitat in the Antarctic Peninsula. (a) Survival rate of H. planatus from cold to polar temperatures during 90 days. 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subjects Anthropogenic factors
Aquatic habitats
Biodiversity
Biodiversity and Ecology
Climate change
Colonization
Crustaceans
Current distribution
Dispersal
Distribution
Ecological models
Environmental Sciences
establishment
Greenhouse effect
Greenhouse gases
Halicarcinus planatus
Human influences
Indigenous species
Introduced species
Invasive species
Life Sciences
Marine crustaceans
Marine invertebrates
Mathematical models
Mitigation
Modelling
Mussels
niche modelling
Niches
non‐native species
Probability theory
reptant crab
Shallow water
Shellfish
Shores
Southern Ocean
Survival
thermotolerance
Translocation
title Is the southern crab Halicarcinus planatus (Fabricius, 1775) the next invader of Antarctica?
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