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New wire-netting fences like this one are rarely constructed because of the cost. The fence is 1.8 metres high with the bottom half constructed with rabbit-proof netting and the top with lighter, marsupial-proof netting. A 25 centimetre flap of rabbit-proof netting is either buried or laid flat on the ground to prevent wild dogs, rabbits and macropods from digging under the fence (Source: P. Fleming).

New wire-netting fences like this one are rarely constructed because of the cost. The fence is 1.8 metres high with the bottom half constructed with rabbit-proof netting and the top with lighter, marsupial-proof netting. A 25 centimetre flap of rabbit-proof netting is either buried or laid flat on the ground to prevent wild dogs, rabbits and macropods from digging under the fence (Source: P. Fleming).

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Managing the Impacts of Dingoes and Other Wild Dogs is the first book to provide a comprehensive review of the history and biology of wild dogs in Australia, the damage they cause, and community attitudes to their management. Australia's wild dogs include dingoes, introduced around 4000 years ago, feral domestic dogs and hybrids between the two. Th...

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... The dingo (Canis dingo [33,34] or Canis familiaris [35,36]-its taxonomy is disputed [37][38][39]), Australia's largest terrestrial carnivore, is one species warranting further investigation into its ecological role. Dingoes have long been controlled due to conflicts with livestock producers [40,41] and are known to prey upon a range of threatened species [42][43][44][45][46][47]. In some cases, they have also compromised conservation efforts [10,48]. ...
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... The foraging behaviours and interactions between these predators are of great ecological and economic significance due to their heavily debated impacts on vulnerable native mammal populations and farming practices (Moseby et al. 2012;Cooke and Soriguer 2017). The dingo is Australia's largest terrestrial predator and has coexisted with extant native prey species since its arrival on the continent ~ 5000 years ago (Fleming et al. 2001;Savolainen et al. 2004). Since European colonization in 1788, dingoes have been exterminated from much of the mainland Australia because they attack livestock (Fleming et al. 2001;Philip 2021). ...
... The dingo is Australia's largest terrestrial predator and has coexisted with extant native prey species since its arrival on the continent ~ 5000 years ago (Fleming et al. 2001;Savolainen et al. 2004). Since European colonization in 1788, dingoes have been exterminated from much of the mainland Australia because they attack livestock (Fleming et al. 2001;Philip 2021). Along with numerous other placental mammals, Europeans introduced the red fox; an efficient mesopredator considered a significant threat to the long-term survival of many endemic Australian mammals, especially small, desert-dwelling mammals weighing between 50 and 5500 g (Letnic and Dickman 2006;McKenzie et al. 2007)). ...
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... Dingoes are estimated to cost the livestock industry AUD89 million/year in lost productivity; foxes come in second at AUD28 million/year (McLeod 2016). The main methods used in Australia to prevent predation of livestock are lethal control of predators (by trapping, shooting, and poisoning) and exclusion fencing (Fleming et al. 2001;Allen and Fleming 2004;Smith et al. 2021). Various non-lethal methods for predator control are available; among these, LGDs are relatively popular (van Bommel and Johnson 2014) but still not widespread. ...
... Non-lethal control is often labour intensive (van Bommel and Johnson 2014), but lethal control must also be intensive, well-coordinated and applied over large areas on a continuing basis to achieve an effective long-term reduction in predator numbers (Ballard et al. 2020); otherwise, local reductions in predator abundance are quickly reversed by immigration (Saunders et al. 1995;Allen and Gonzalez 1998;Corbett 2001). In addition, there is concern about the impact of lethal control on nontarget animals (Fleming et al. 2001;Glen and Dickman 2003;Glen et al. 2007) and on dingo populations. Dingoes perform an important ecological function as Australia's top predator, and reducing their numbers could negatively affect biodiversity (Johnson et al. 2007;Letnic et al. 2011Letnic et al. , 2012. ...
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... The dingo is Australia's largest terrestrial predator. While sheep production is incompatible with dingoes (Thomson 1984;Allen & Sparkes 2001;Fleming et al. 2001), the effect of dingoes on cattle enterprises is more complex (Allen 2015;Prowse et al. 2015). The widespread control of dingoes has been synonymous with the spread of sheep grazing throughout agricultural and pastoral regions of Australia. ...
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... Consequently, intensive effort is spent on suppressing dingo populations in many regions . The most widely used methods to suppress dingo populations are exclusion fencing, poisoning, trapping and shooting (Fleming et al. 2001). Exclusion fences have been particularly effective at reducing dingo populations and work by preventing immigration of dingoes into areas where their populations have been suppressed (Fleming et al. 2001). ...
... The most widely used methods to suppress dingo populations are exclusion fencing, poisoning, trapping and shooting (Fleming et al. 2001). Exclusion fences have been particularly effective at reducing dingo populations and work by preventing immigration of dingoes into areas where their populations have been suppressed (Fleming et al. 2001). The longest of these fences, the dingo barrier fence, is > 5000 km in length (McKnight 1969). ...
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... Where present, dingoes seem to limit the access of foxes to resources (Fleming et al. 2001). Foxes, in turn, may competitively exclude feral cats from other food resources (Robley et al. 2004). ...
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... By contrast, prey animals may reduce their activity when night-time illumination is high (e.g., full moon, reduced cloud cover) to decrease predation risk (e.g., Harmsen et al. 2011;Linley et al. 2020). Healthy adult cattle and buffalo are considered too large for dingoes to kill, but calves and weak adults are vulnerable to predation (Thomson 1992;Corbett 1995b;Fleming et al. 2001). Dingoes also prey on feral pigs of all ages in tropical Australia (Corbett 1995a;Fleming et al. 2001;Brook and Kutt 2011). ...
... Healthy adult cattle and buffalo are considered too large for dingoes to kill, but calves and weak adults are vulnerable to predation (Thomson 1992;Corbett 1995b;Fleming et al. 2001). Dingoes also prey on feral pigs of all ages in tropical Australia (Corbett 1995a;Fleming et al. 2001;Brook and Kutt 2011). ...
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... Similar concerns have been raised in Australia with many dingoes, particularly in southeastern Australia, exhibiting genetic, morphological or phenotypic evidence of domestic dog ancestry (Newsome and Corbett 1985;Daniels and Corbett 2003;Jones 2009;Stephens et al. 2015). There is also widespread concern that feral domestic dogs have established in the wild across Australia (Fleming et al. 2001;NSW Threatened Species Scientific Committee 2009). ...
... Before the 2000s a majority of our knowledge about dingo  dog hybridisation was based on assessment of skull morphology and physical appearance (Newsome et al. 1980;Newsome and Corbett 1985;Jones 1990;Corbett 2001;Fleming et al. 2001). A microsatellite DNA test for assessing the ancestry of dingoes was developed in 1999 (Wilton et al. 1999;Wilton 2001) and has since become widely used by wildlife managers and conservation groups. ...
... The finding that feral dogs have not established populations has implications for the management of wild canids in Australia. Dingoes and stray or roaming domestic dogs can cause serious impacts for livestock graziers (Fleming et al. 2001). Management of feral, stray or roaming domestic dogs should focus on responsible pet ownership including spaying and neutering of pet animals, keeping pet and working dogs under control and confined during the night. ...
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Hybridisation between wild and domestic canids is a global conservation and management issue. In Australia, dingoes are a distinct lineage of wild-living canid with a controversial domestication status. They are mainland Australia’s apex terrestrial predator. There is ongoing concern that the identity of dingoes has been threatened from breeding with domestic dogs, and that feral dogs have established populations in rural Australia. We collate the results of microsatellite DNA testing from 5039 wild canids to explore patterns of domestic dog ancestry in dingoes and observations of feral domestic dogs across the continent. Only 31 feral dogs were detected, challenging the perception that feral dogs are widespread in Australia. First generation dingo × dog hybrids were similarly rare, with only 27 individuals identified. Spatial patterns of genetic ancestry across Australia identified that dingo populations in northern, western and central Australia were largely free from domestic dog introgression. Our findings challenge the perception that dingoes are virtually extinct in the wild and that feral dogs are common. A shift in terminology from wild dog to dingo would better reflect the identity of these wild canids and allow more nuanced debate about the balance between conservation and management of dingoes in Australia.
... Hence, further extended studies in both spatial and temporal scale to capture the population dynamics of this species across the ecosystem of Java are necessary. At least, the indices of abundance of dhole's population in the remaining habitat are needed to monitor the impact management programs or the change of environmental conditions on the population [66]. ...
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The success of conservation and management of endangered species is highly dependent on the manager's understanding on the biology and ecology of the target species. However, most wildlife management and conservation activities in developing countries are not based on scientific data, but more on the political agenda and intuition of managers. As a result, the impact of conservation and management efforts was far from what was expected and sometimes even caused new problems to arise (e.g., the rapid population decline of certain species, introduction of alien invasive species etc.). Wildlife legal status is also important to protect a certain species from exploitation and to ensure the fairness by regulating social conduct and enforcing policy associated with wildlife management and conservation, and, therefore, it has play an important role in achieving management goal. We attempt to review the management and conservation of dholes (Cuon alpinus) at the human-dominated landscape through ecological and legal approach. Our finding showed that an approach which was mostly used along the history of dhole’s management was lethal control due to livestock depredation. This approach has resulted dramatic decline of dhole’s population and explosion of wild ungulates population. In Indonesia, the government regulation to conserve this species is already exists, but lack of implementation due to management limitations. The absence and lack of baseline data for dhole’s conservation are common phenomenon since this species has not listed as a priority species. To ensure the long-term survival of this species, suitable conservation strategy supported by good scientific data and regulations related to dhole’s conservation is absolutely needed. Gathering scientific data related to the dhole’s conservation by the multidisciplinary team will benefit to the management in resolving the problem arises during the management process. The availability of adequate ecological data will also be useful for increasing public understanding in the importance of dhole conservation and attracting public sympathy, thus they become more tolerant to the existence of this species. Keywords: Cuon alpinus, Conservation, Ecology, Java, Legal status, Management.