The colonization of Madagascar by Austronesian-speaking people during AD 50–500 represents the most westerly point of the greatest diaspora in prehistory. A range of economically important plants and animals may have accompanied the Austronesians. Domestic chickens (Gallus gallus) are found in Madagascar, but it is unclear how they arrived there. Did they accompany the initial Austronesian-speaking populations that reached Madagascar via the Indian Ocean or were they late arrivals with Arabian and African sea-farers? To address this question, we investigated the mitochondrial DNA control region diversity of modern chickens sampled from around the Indian Ocean rim (Southeast Asia, South Asia, the Arabian Peninsula, East Africa and Madagascar). In contrast to the linguistic and human genetic evidence indicating dual African and Southeast Asian ancestry of the Malagasy people, we find that chickens in Madagascar only share a common ancestor with East Africa, which together are genetically closer to South Asian chickens than to those in Southeast Asia. This suggests that the earliest expansion of Austronesian-speaking people across the Indian Ocean did not successfully introduce chickens to Madagascar. Our results further demonstrate the complexity of the translocation history of introduced domesticates in Madagascar.
Populations on continental islands are often distinguishable from mainland conspecifics with respect to body size, appearance, behaviour or life history, and this is often congruent with genetic patterns. It is commonly assumed that such differences developed following the complete isolation of populations by sea-level rise following the Last Glacial Maximum (LGM). However, population divergence may predate the LGM, or marine dispersal and colonization of islands may have occurred more recently; in both cases, populations may have also diverged despite ongoing gene flow. Here, we test these alternative hypotheses for the divergence between wedge-tailed eagles from mainland Australia (Aquila audax audax) and the threatened Tasmanian subspecies (Aquila audax fleayi), based on variation at 20 microsatellite loci and mtDNA. Coalescent analyses indicate that population divergence appreciably postdates the severance of terrestrial habitat continuity and occurred without any subsequent gene flow. We infer a recent colonization of Tasmania by marine dispersal and cannot discount founder effects as the cause of differences in body size and life history. We call into question the general assumption of post-LGM marine transgression as the initiator of divergence of terrestrial lineages on continental islands and adjacent mainland, and highlight the range of alternative scenarios that should be considered.
Context Conservation of vulnerable and endangered species requires a comprehensive understanding of their distribution and habitat requirements, so as to implement effective management strategies. Visual scat surveys are a common non-invasive method for monitoring populations. However, morphological similarity of scats among sympatric species presents a problem for accurate identification. Visual misidentifications of scats can have major impacts on the accuracy of abundance and distribution surveys of target species, wasting resources and misdirecting management and conservation actions. DNA identification of scats can overcome this issue, while simultaneously providing a rich source of genetic information for population and dietary studies. Aims We developed a simple and reliable method to identify morphologically similar macropod scats from eight sympatric species in north-eastern Australia, using polymerase chain reaction (PCR) and restriction fragment length polymorphism (RFLP) of a portion of the mtDNA ND2 gene. Methods We identified a short (275-bp) polymorphic region of ND2, which is easily amplifiable from degraded DNA, developed a primer set, and identified a set of three restriction endonucleases (AluI, BstNI and HphI) which, in combination, can discriminate among the eight target species. So as to test the effectiveness of this protocol, we collected 914 macropod scats from 53 sites in the north-eastern Australia. Key results In total, 406 of these scats were extracted, with 398 (98%) containing amplifiable macropod DNA. All 398 scats were subsequently identified to species by using our RFLP protocol. Sequencing of a subset of these samples confirmed the accuracy of the test. Species identification of scats by using DNA identified eight species of macropods, five of which were outside their documented distributions, one of which was ~400 km. Conclusions Our PCR–RFLP method is a simple and efficient means to identify macropod scats to species, eliminating the need for sequencing, which is costly, time-consuming and requires additional laboratory equipment. Implications The method allows for rapid and non-invasive assessment of macropod species and is particularly useful for surveying populations across multiple sites.
Management and conservation require a comprehensive understanding of species distributions and habitat requirements. Reliable species occurrence data are critical in the face of climate change and other anthropogenic activity, but are often difficult to obtain, particularly for wide ranging species. This directly affects ecological models of occurrence and habitat suitability and, in turn, conservation and management decisions. We used generalized linear mixed-effects models to identify ecological determinants of occurrence for four macropod species (across a region of tropical northern Australia) using a non-invasive genetic scat approach with and without additional observation records from visual surveys.We show that genetically derived occurrence data, alone, can be used to develop informative ecological models that describe the inter-specific habitat requirements of macropods. Furthermore, we show that genetic scat surveys of macropods are cheaper and less time consuming to conduct, and tend to provide more occurrence records (and less false absences) than visual surveys. We conclude that indirect surveys using molecular approaches have an important role to play in modelling species' occurrence, and developing future management practices and guidelines to aid species conservation.
The distribution of antilopine wallaroo, Macropus antilopinus, is marked by a break in the species’ range between Queensland and the Northern Territory, coinciding with the Carpentarian barrier. Previous work on M. antilopinus revealed limited genetic differentiation between the Northern Territory and Queensland M. antilopinus populations across this barrier. The study also identified a number of divergent lineages in the Northern Territory, but was unable to elucidate any geographic structure. Here, we re‐examine these results to (1) determine phylogeographic patterns across the range of M. antilopinus and (2) infer the biogeographic barriers associated with these patterns. The tropical savannahs of northern Australia: from the Cape York Peninsula in the east, to the Kimberley in the west. We examined phylogeographic patterns in M. antilopinus using a larger number of samples and three mtDNA genes: NADH dehydrogenase subunit 2, cytochrome b, and the control region. Two datasets were generated and analyzed: (1) a subset of samples with all three mtDNA regions concatenated together and (2) all samples for just control region sequences that included samples from the previous study. Analysis included generating phylogenetic trees based on Bayesian analysis and intraspecific median‐joining networks. The contemporary spatial structure of M. antilopinus mtDNA lineages revealed five shallow clades and a sixth, divergent lineage. The genetic differences that we found between Queensland and Northern Territory M. antilopinus samples confirmed the split in the geographic distribution of the species. We also found weak genetic differentiation between Northern Territory samples and those from the Kimberley region of Western Australia, possibly due to the Kimberley Plateau–Arnhem Land barrier. Within the Northern Territory, two clades appear to be parapatric in the west, while another two clades are broadly sympatric across the Northern Territory. MtDNA diversity of M. antilopinus revealed an unexpectedly complex evolutionary history involving multiple sympatric and parapatric mtDNA clades across northern Australia. These phylogeographic patterns highlight the importance of investigating genetic variation across distributions of species and integrating this information into biodiversity conservation.
A set of 15 microsatellite loci was optimised for multilocus genotyping of non-invasively collected samples of Macropus antilopinus (antilopine wallaroo). Primers were combined in three PCR multiplexes in order to increase the quality of genotypes from scat samples and to allow for replication. In a screen of 104 scat samples from two populations in north-eastern Australia, three loci were found to be monomorphic while the remaining 12 loci had 2–10 alleles. Genotype frequencies for all 12 microsatellite loci from the two populations did not differ significantly from Hardy–Weinberg equilibrium, and there was no evidence of linkage disequilibrium. These informative markers are specifically designed for non-invasive samples and will be used to assess population structure and conservation genetics of this species in the future.
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