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Spatial distribution and range expansion of the Tawny Coster butterfly, Acraea terpsicore (Linnaeus, 1758) (Lepidoptera: Nymphalidae), in South-East Asia and Australia

Identifieur interne : 000120 ( PascalFrancis/Corpus ); précédent : 000119; suivant : 000121

Spatial distribution and range expansion of the Tawny Coster butterfly, Acraea terpsicore (Linnaeus, 1758) (Lepidoptera: Nymphalidae), in South-East Asia and Australia

Auteurs : Michael F. Braby ; Cléo Bertelsmeier ; Chris Sanderson ; Brian M. Thistleton

Source :

RBID : Pascal:15-0016231

Descripteurs français

English descriptors

Abstract

1. Documenting the range size and range boundaries of species, and understanding the factors determining changes in these spatial components, is crucial given current rates of anthropogenic climate change and habitat loss. Here, we document the establishment of the acraeine butterfly. Acraea terpsicore, in South-East Asia (Indonesian islands south of Malay Peninsula, and Timor) and Australia for the first time. We estimate its rate of colonisation and potential for further range expansion in the Indo-Australian region according to bioclimatic niche models. 2. We modelled the potential distribution of the species in the Indo-Australian region under current climatic conditions and in 2050 following climate change. The bioclimatic niche models were based on five different modelling techniques, three global circulation models (GCMs) and two CO2 emission scenarios (SRES), yielding 30 individual models that were combined in a consensus model. 3. Acraea terpsicore became established in Indo-China (Thailand) during the 1980s and since that time it has spread to other parts of South-East Asia. It was first recorded on the Australian mainland in the Northern Territory in April 2012 and within a few months of detection was found to occur at six locations, with an estimated extent of occurrence of 4000 km2. Thus, the range size of A. terpsicore has expanded by approximately 6000 km across the equator (c. 32 degrees latitude) in 28 years, with an average rate of colonisation (from Thailand to Australia) of 200 km year-1(range: 170-230 km year-1). 4. The bioclimatic niche models identified additional regions with favourable climatic conditions, and within Australia it is likely to occupy coastal and sub-coastal savannah woodlands of the entire monsoon tropics, indicating potential for further range expansion. Moreover, the species' potential range is likely to increase with climate change. 5. We hypothesise that habitat modification, particularly rapid deforestation of tropical forest in South-East during the past three decades, is a major factor accounting for the range expansion given the species' habitat preference for disturbed and open degraded areas. Climate change may be a contributing factor but is unlikely the sole determinant given the spatial area involved and rate of spread.

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Pour connaître la documentation sur le format Inist Standard.

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Format Inist (serveur)

NO : PASCAL 15-0016231 INIST
ET : Spatial distribution and range expansion of the Tawny Coster butterfly, Acraea terpsicore (Linnaeus, 1758) (Lepidoptera: Nymphalidae), in South-East Asia and Australia
AU : BRABY (Michael F.); BERTELSMEIER (Cléo); SANDERSON (Chris); THISTLETON (Brian M.)
AF : Department of Land Resource Management/Palmerston, NT/Australie (1 aut.); School of Biological Sciences. The Australian National University/Canberra, ACT/Australie (1 aut.); Ecologie, Systématique & Evolution, UMR CNRS 8079, Université Paris Sud XI/Orsa/France (2 aut.); Environmental Resources Management Australia/Canberra, ACT/Australie (3 aut.); Plant Industries, Department of Primary Industry and Fisheries/Darwin, NT/Australie (4 aut.)
DT : Publication en série; Niveau analytique
SO : Insect conservation and diversity : (Print); ISSN 1752-458X; Royaume-Uni; Da. 2014; Vol. 7; No. 2; Pp. 132-143; Bibl. 2 p.3/4
LA : Anglais
EA : 1. Documenting the range size and range boundaries of species, and understanding the factors determining changes in these spatial components, is crucial given current rates of anthropogenic climate change and habitat loss. Here, we document the establishment of the acraeine butterfly. Acraea terpsicore, in South-East Asia (Indonesian islands south of Malay Peninsula, and Timor) and Australia for the first time. We estimate its rate of colonisation and potential for further range expansion in the Indo-Australian region according to bioclimatic niche models. 2. We modelled the potential distribution of the species in the Indo-Australian region under current climatic conditions and in 2050 following climate change. The bioclimatic niche models were based on five different modelling techniques, three global circulation models (GCMs) and two CO2 emission scenarios (SRES), yielding 30 individual models that were combined in a consensus model. 3. Acraea terpsicore became established in Indo-China (Thailand) during the 1980s and since that time it has spread to other parts of South-East Asia. It was first recorded on the Australian mainland in the Northern Territory in April 2012 and within a few months of detection was found to occur at six locations, with an estimated extent of occurrence of 4000 km2. Thus, the range size of A. terpsicore has expanded by approximately 6000 km across the equator (c. 32 degrees latitude) in 28 years, with an average rate of colonisation (from Thailand to Australia) of 200 km year-1(range: 170-230 km year-1). 4. The bioclimatic niche models identified additional regions with favourable climatic conditions, and within Australia it is likely to occupy coastal and sub-coastal savannah woodlands of the entire monsoon tropics, indicating potential for further range expansion. Moreover, the species' potential range is likely to increase with climate change. 5. We hypothesise that habitat modification, particularly rapid deforestation of tropical forest in South-East during the past three decades, is a major factor accounting for the range expansion given the species' habitat preference for disturbed and open degraded areas. Climate change may be a contributing factor but is unlikely the sole determinant given the spatial area involved and rate of spread.
CC : 002A14D02B; 001E02D10; 002A14A02; 002A14D02A
FD : Répartition spatiale; Aire de distribution; Expansion; Bioclimat; Niche écologique; Modélisation; Biogéographie; Espèce envahissante; Changement climatique; Modèle; Surveillance écologique; Protection environnement; Asie du sud est; Australie; Lepidoptera; Nymphalidae; Invasion biologique
FG : Répartition géographique; Climatologie dynamique; Asie; Océanie; Zone tropicale; Insecta; Arthropoda; Invertebrata
ED : Spatial distribution; Distribution range; Expansion; Bioclimate; Ecological niche; Modeling; Biogeography; Invasive species; Climate change; Models; Environmental monitoring; Environmental protection; South east Asia; Australia; Lepidoptera; Nymphalidae; Biological invasion
EG : Geographic distribution; Dynamical climatology; Asia; Oceania; Tropical zone; Insecta; Arthropoda; Invertebrata
SD : Distribución espacial; Area de distribución; Expansión; Bioclima; Nicho ecológico; Modelización; Biogeografía; Especie invasora; Cambio climático; Modelo; Vigilancia ecológica; Protección medio ambiente; Asia del sureste; Australia; Lepidoptera; Nymphalidae; Invasión biológica
LO : INIST-28199.354000506155260040
ID : 15-0016231

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Pascal:15-0016231

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<sub>2</sub>
emission scenarios (SRES), yielding 30 individual models that were combined in a consensus model. 3. Acraea terpsicore became established in Indo-China (Thailand) during the 1980s and since that time it has spread to other parts of South-East Asia. It was first recorded on the Australian mainland in the Northern Territory in April 2012 and within a few months of detection was found to occur at six locations, with an estimated extent of occurrence of 4000 km
<sup>2</sup>
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<sup>-1</sup>
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<NO>PASCAL 15-0016231 INIST</NO>
<ET>Spatial distribution and range expansion of the Tawny Coster butterfly, Acraea terpsicore (Linnaeus, 1758) (Lepidoptera: Nymphalidae), in South-East Asia and Australia</ET>
<AU>BRABY (Michael F.); BERTELSMEIER (Cléo); SANDERSON (Chris); THISTLETON (Brian M.)</AU>
<AF>Department of Land Resource Management/Palmerston, NT/Australie (1 aut.); School of Biological Sciences. The Australian National University/Canberra, ACT/Australie (1 aut.); Ecologie, Systématique & Evolution, UMR CNRS 8079, Université Paris Sud XI/Orsa/France (2 aut.); Environmental Resources Management Australia/Canberra, ACT/Australie (3 aut.); Plant Industries, Department of Primary Industry and Fisheries/Darwin, NT/Australie (4 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Insect conservation and diversity : (Print); ISSN 1752-458X; Royaume-Uni; Da. 2014; Vol. 7; No. 2; Pp. 132-143; Bibl. 2 p.3/4</SO>
<LA>Anglais</LA>
<EA>1. Documenting the range size and range boundaries of species, and understanding the factors determining changes in these spatial components, is crucial given current rates of anthropogenic climate change and habitat loss. Here, we document the establishment of the acraeine butterfly. Acraea terpsicore, in South-East Asia (Indonesian islands south of Malay Peninsula, and Timor) and Australia for the first time. We estimate its rate of colonisation and potential for further range expansion in the Indo-Australian region according to bioclimatic niche models. 2. We modelled the potential distribution of the species in the Indo-Australian region under current climatic conditions and in 2050 following climate change. The bioclimatic niche models were based on five different modelling techniques, three global circulation models (GCMs) and two CO
<sub>2</sub>
emission scenarios (SRES), yielding 30 individual models that were combined in a consensus model. 3. Acraea terpsicore became established in Indo-China (Thailand) during the 1980s and since that time it has spread to other parts of South-East Asia. It was first recorded on the Australian mainland in the Northern Territory in April 2012 and within a few months of detection was found to occur at six locations, with an estimated extent of occurrence of 4000 km
<sup>2</sup>
. Thus, the range size of A. terpsicore has expanded by approximately 6000 km across the equator (c. 32 degrees latitude) in 28 years, with an average rate of colonisation (from Thailand to Australia) of 200 km year
<sup>-1</sup>
(range: 170-230 km year
<sup>-1</sup>
). 4. The bioclimatic niche models identified additional regions with favourable climatic conditions, and within Australia it is likely to occupy coastal and sub-coastal savannah woodlands of the entire monsoon tropics, indicating potential for further range expansion. Moreover, the species' potential range is likely to increase with climate change. 5. We hypothesise that habitat modification, particularly rapid deforestation of tropical forest in South-East during the past three decades, is a major factor accounting for the range expansion given the species' habitat preference for disturbed and open degraded areas. Climate change may be a contributing factor but is unlikely the sole determinant given the spatial area involved and rate of spread.</EA>
<CC>002A14D02B; 001E02D10; 002A14A02; 002A14D02A</CC>
<FD>Répartition spatiale; Aire de distribution; Expansion; Bioclimat; Niche écologique; Modélisation; Biogéographie; Espèce envahissante; Changement climatique; Modèle; Surveillance écologique; Protection environnement; Asie du sud est; Australie; Lepidoptera; Nymphalidae; Invasion biologique</FD>
<FG>Répartition géographique; Climatologie dynamique; Asie; Océanie; Zone tropicale; Insecta; Arthropoda; Invertebrata</FG>
<ED>Spatial distribution; Distribution range; Expansion; Bioclimate; Ecological niche; Modeling; Biogeography; Invasive species; Climate change; Models; Environmental monitoring; Environmental protection; South east Asia; Australia; Lepidoptera; Nymphalidae; Biological invasion</ED>
<EG>Geographic distribution; Dynamical climatology; Asia; Oceania; Tropical zone; Insecta; Arthropoda; Invertebrata</EG>
<SD>Distribución espacial; Area de distribución; Expansión; Bioclima; Nicho ecológico; Modelización; Biogeografía; Especie invasora; Cambio climático; Modelo; Vigilancia ecológica; Protección medio ambiente; Asia del sureste; Australia; Lepidoptera; Nymphalidae; Invasión biológica</SD>
<LO>INIST-28199.354000506155260040</LO>
<ID>15-0016231</ID>
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