The dingo (Canis familiaris or Canis familiaris dingo or Canis lupus dingo or Canis dingo) is a type of feral dog native to Australia. Its taxonomic status is debated. The first British colonists to arrive established a settlement at Port Jackson in 1788 and recorded dingoes living there with indigenous Australians. Although the dingo exists in the wild, it associates with humans but has not been selectively bred as have other domesticated animals. It is a medium-sized canid that possesses a lean, hardy body adapted for speed, agility and stamina. The dingo's three main coat colours are described as being either light ginger (or tan), black and tan, or creamy white. The head is the widest part of the dingo, is wedge-shaped, and large in proportion to the body. The dingo skull differs to that of the domestic dog by its larger palatal width, longer rostrum, shorter skull height, and wider sagittal crest. One can regard the dingo as an ecotype or an ecospecies which has adapted to Australia's unique environment. It is listed as a "Vulnerable species" on the IUCN Red List due to declining numbers caused by hybridization with the domestic dog.
Temporal range: Holocene (3,450 years BP – Recent)
|A male dingo|
|Subspecies:||C. l. dingo|
|Canis lupus dingo
|Distribution of dingoes and hybrids|
Genetic studies indicate that the dingo is closely related to the New Guinea singing dog, that their lineage split early from the lineage that led to today's domestic dog, and that their lineage can be traced back through the Indonesian Archipelago to Asia. In the archaeological record, the earliest known dingo skeletal remains in Australia (from the Mandurah Caves on the Nullabor Plain, south-eastern Western Australia) date to 3,450 years before present (YBP), which led to the widely-held belief that dingoes arrived with seafarers to Australia 5,000 YBP. The comparison of these early fossils with modern dingoes indicates that dingo morphology has not changed over the past 3,500 years. This suggests that there has been no artificial selection over this period and that the dingo represents an early form of dog from 4,000–5,000 years ago. They have lived, bred, and undergone natural selection in the wild, isolated from other canids until the arrival of European settlers, resulting in a unique canid. Accordingly, some scientists argue that the dingo should be recognised as a distinct taxon that should be classified under its original Latin name, Canis dingo. A recent genetic study shows that the lineage of those dingoes found today in the northwestern part of the Australian continent split from the lineage of the New Guinea singing dog and southeastern dingo 8,300 YBP, followed by a split between the New Guinea singing dog lineage from the southeastern dingo lineage 7,800 YBP. The study proposes that there were two dingo migrations when sea levels were lower and Australia and New Guinea formed one landmass named Sahul that existed until 6,500–8,000 years ago. The dingo is recognised as a native animal under the laws of all Australian jurisdictions.
The dingo's distribution covers a variety of habitats, including the temperate regions of eastern Australia, the alpine moorlands of the eastern highlands, the arid hot deserts of Central Australia, and the tropical forests and wetlands of Northern Australia. Dingos prey on mammals up to the size of the large red kangaroo, in addition to birds, reptiles, fish, crabs, frogs, insects and seeds. The dingo's competitors include the native quoll, the introduced European red fox and the feral cat. A dingo pack usually consists of a mated pair, their offspring from the current year and sometimes offspring from the previous year.
Livestock farming commenced expanding across Australia from the early 19th century, which led to conflict between the dingo and graziers. Sheep, and to a lesser extent cattle, are an easy target for dingoes. The pastoralists and the government bodies that support their industry have shot, trapped, and poisoned dingoes or destroyed dingo pups in their dens. After two centuries of persecution, the dingo or dingo–dog hybrids can still be found across most of the continent. The dingo plays a prominent role in the dreamtime stories of indigenous Australians; however, it rarely appears depicted in their cave paintings when compared with the extinct thylacine.
The name "dingo" comes from the Dharug language used by the Indigenous Australians of the Sydney area. The first British colonists to arrive in Australia in 1788 established a settlement at Port Jackson and noted "dingoes" living with indigenous Australians. The name was first recorded in 1789 by Watkin Tench in his Narrative of the Expedition to Botany Bay:
The only domestic animal they have is the dog, which in their language is called Dingo, and a good deal resembles the fox dog of England. These animals are equally shy of us, and attached to the natives. One of them is now in the possession of the Governor, and tolerably well reconciled to his new master.
The variants include "tin-go" for a bitch, "din-go" for a dog, and "wo-ri-gal" for a big dog. The dingo has been given different names in the Indigenous Australian languages, including "boolomo", "dwer-da", "joogoong", "kal", "kurpany", "maliki", "mirigung", "noggum", "papa-inura", and "wantibirri". Some authors propose that there was a difference between camp dingoes and wild dingoes as they had different names among indigenous tribes. The people of the Yarralin, Northern Territory region frequently call those dingoes that live with them walaku, and those that live in the wilderness ngurakin. They also use the name walaku to refer to both dingoes and dogs. The colonial settlers of New South Wales wrote using the name dingo only for camp dogs. It is proposed that in New South Wales the camp dingoes only became wild after the collapse of aboriginal society.
Dogs associated with natives were first recorded by Jan Carstenszoon in the Cape York Peninsula area in 1623. In 1699, Captain William Dampier visited the coast of what is now Western Australia and recorded that "...my men saw two or three beasts like hungry wolves, lean like so many skeletons, being nothing but skin and bones...".
In 1768, James Cook took command of a scientific voyage of discovery from Britain to New Holland, which was the name for Australia at that time. In 1770, his ship HMS Endeavour arrived in Botany Bay, which is now part of Sydney. The mission collected specimens and made notes for taking back to Britain. On return to Britain, Joseph Banks commissioned George Stubbs to produce paintings based on his observations, one of which was the "Portrait of a Large Dog from New Holland" completed in 1772. In 1788, the First Fleet arrived in Botany Bay under the command of Australia's first colonial governor, Arthur Phillip, who made a brief description and an illustration in his journal of the "Dog of New South Wales". In 1793, the "Dog of New South Wales" was classified by Friedrich Meyer as Canis dingo, based on the illustration. Johann Friedrich Blumenbach gathered together a collection from the Cook voyage and in 1799 he classified the "New Holland dog" as Canis familiaris dingo. In 1947, a proposal was made to change this classification after it was discovered that the "New Holland dog" Canis antarticus Kerr, 1792 had been specified a year earlier in a little-known work. Both Kerr and Meyer had based their classifications on the illustration of the "Dog of New South Wales", and therefore there is no reference type specimen that these were based on.
In 1957, the International Commission on Zoological Nomenclature (ICZN) was asked to suppress the name Canis antarticus on the grounds that Canis dingo was the common name that has been used for over 150 years. The ICZN ruled that Canis antarticus Kerr, 1792 be suppressed and that Canis dingo Meyer, 1793 was the name to be used for the dingo in its Opinion 451. This name was then entered on the ICZN's Official Lists and Indexes of Names in Zoology. A name entered onto the Official List of the ICZN is the available name, which is "a scientific name applied to an animal taxon", although this is not prescriptive about whether or not the epithet be used as at species or at subspecific level, or even dropped if the name is considered a synonym of another species on taxonomic grounds.
In 2003, the ICZN ruled in its Opinion 2027 that the "name of a wild species...is not invalid by virtue of being predated by the name based on a domestic form." Additionally, the ICZN placed the taxon Canis lupus as a conserved name on the official list under this opinion. The reason for doing this was that "The majority of wild progenitors and their domestic derivatives share the same name, but in the 17 cases considered....the wild and domestic forms have been separately named and this has created confusion. This Opinion meant that the name of the domestic dog (Canis familiaris) did not take precedence over the name of the wolf (Canis lupus) at a time when researchers were exploring the relationship between these two taxa.
Taxonomy classifies organisms together that have common characteristics. Nomenclature does not determine the rank to be accorded to any assemblage of animals, only its official name. Therefore, zoologists are free to propose what group of animals with similar characteristics that a taxon might belong to. In the third edition of Mammal Species of the World published in 2005, the mammalogist W. Christopher Wozencraft listed under the wolf Canis lupus what he proposed to be two subspecies: "familiaris Linneaus, 1758 [domestic dog]" and "dingo Meyer, 1793 [domestic dog]",[a] with the comment "Includes the domestic dog as a subspecies, with the dingo provisionally separate – artificial variants created by domestication and selective breeding. Although this may stretch the subspecies concept, it retains the correct allocation of synonyms."
This classification by Wozencraft is hotly debated by zoologists. Mathew Crowther, Stephen Jackson and Colin Groves disagree with Wozencraft and argue that based on ICZN Opinion 2027, the implication is that a domestic animal cannot be a subspecies. Crowther, Juliet Clutton-Brock and others argue that because the dingo differs from wolves by behaviour, morphology, and that the dingo and dog do not fall genetically within any extant wolf clade, that the dingo should be considered the distinct taxon Canis dingo. Jackson and Groves regard the dog Canis familiaris as a taxonomic synonym for the wolf Canis lupus with them both equally ranked at the species level. They also disagree with Crowther, based on the overlap between dogs and dingoes in their morphology, in their ability to easily hybridize with each other, and that they show the signs of domestication by both having a cranium of smaller capacity than their progenitor, the wolf. Given that Canis familiaris Linnaeus, 1758 has priority over Canis dingo Meyer, 1793, they regard the dingo as a junior taxonomic synonym for the dog Canis familiaris (i.e. the dog and the dingo are two names for the same taxon Canis familiaris). Gheorghe Benga and others support the dingo as a subspecies of the dog, thus Canis familiaris dingo with the domestic dog being the subspecies Canis familiaris familiaris.
Although the dingo exists in the wild, it associates with humans but has not been selectively bred similarly to other domesticated animals. Therefore, its status as being a domestic animal is not clear. Whether the dingo was a wild or domesticated species was not clarified from Meyer's original description, which translated from the German language ambiguously reads:
It is not known if it is the only dog species in New South Wales, and if it can also still be found in the wild state; however, so far it appears to have lost little of its wild condition; moreover, no divergent varieties have been discovered.
In 2014, whole genome sequencing indicated that the dog is not a descendant of the extant gray wolf, the ancestor of the dog had gone extinct, and the dingo fell within the dog clade. In 2015, the Taxonomy of Australian Mammals considered the Dingo as Canis familiaris. In 2017, a review of the latest scientific information proposed that the Dingo and New Guinea singing dog are types of domestic dog Canis familiaris Linnaeus 1758. In late 2017, the Australian Government's Australian Faunal Directory listed the Dingo under Canis familiaris Linnaeus 1758.
Whole genome sequencing has been used to survey "...the supposedly ancient, semi-domestic dog breeds, the Basenji and dingo." In 2016, a study based on whole genome sequences indicated that the dog is a genetically divergent subspecies of the gray wolf and was derived from a now-extinct ghost population of Late Pleistocene wolves, the dog and the dingo were not separate species, and in accordance with previous studies that the dingo and the Basenji are considered to be basal members of the domestic dog clade. "The term basal refers to a lineage that diverges early in the history of the group...and lies on a branch that originates near the common ancestor of the group." The study found evidence for gene flow of 0.3% mitochondrial DNA into the dingo lineage from the Qinghai population of the Tibetan wolf. The Australian National Kennel Council recognizes a dingo breed standard within its Hounds group.
The archaeological record shows that the earliest dingo skeletal remains in Australia date to 3,450 years before present (YBP) from the Mandurah Caves on the Nullabor Plain, south-eastern Western Australia; 3,320 YBP from Woombah Midden near Woombah, New South Wales; and 3,170 YBP from Fromme's Landing on the Murray River near Mannum, South Australia. Dingo bone fragments were found in a rock shelter located at Mount Burr, South Australia in a layer that was originally dated 7,000-8,500 YBP. Excavations later indicated that the levels had been disturbed, and the dingo remains "probably moved to an earlier level." The earliest dingo remains in the Torres Straits date to 2,100 YBP. In New Guinea, the earliest dog bones date to 2,500–2,300 YBP from Caution Bay near Port Moresby but no ancient New Guinea Singing Dog remains have been found. These early Australian dingo fossils led to the widely-held belief that dingoes first arrived in Australia 5,000 YBP with seafarers. Based on a comparison with these early fossils, dingo morphology has not changed over the past 3,500 years. This suggests that there has been no artificial selection over this period and that the dingo represents an early form of dog from 4,000-5,000 years ago. They have lived, bred, and undergone natural selection in the wild, isolated from other canids until the arrival of European settlers, resulting in a unique canid. Therefore, it is argued by some scientists that the dingo should be recognised as the distinct taxon Canis dingo.
At the end of the Last glacial maximum and the rise in sea levels, Tasmania became separated from the Australian mainland 12,000 YBP, and New Guinea 6,500–8,500 YBP by the inundation of the Sahul Shelf. No remains have been uncovered in Tasmania, therefore the Dingo is estimated to have arrived in Australia between 3,500-12,000 YBP. To reach Australia through the Malay Archipelago even at the lowest sea level of the Last Glacial Maximum, a journey of at least 50 km (30 mi) over open sea between ancient Sunda and Sahul was necessary, indicating that the dingo arrived to Sahul by boat.
A haplotype (haploid genotype) is a group of genes in an organism that are inherited together from a single parent. All dingo sequences studied exhibit mDNA haplotype A29, which falls within the Clade A haplogroup that represents 70% of domestic dogs. The evidence suggests that the haplotype was introduced from East Asia or southeast Asia through the islands of the Malay archipelago and into Australia. Haplotype A29 was one of several domestic dog mDNA haplotypes brought into the Malay Archipelago but only A29 reached mainland Australia. The mDNA haplotype A29, or a haplotype one mutation step away, was found in all of the Australian dingoes and New Guinea Singing Dogs so far studied, indicating descent from a common female ancestor.
In 2011, a study of the dingo male lineage using Y chromosome DNA (yDNA) as a genetic marker was undertaken for 338 Australian dingoes, New Guinea Singing Dogs, and village dogs from the Malay Archipelago. The Bali dogs support the arrival of their ancestors with the Austronesian expansion and the arrival of other domesticates 3-4,500 YBP. The data confirms that dingoes carry the unique yDNA haplogroup (H60) and it has been derived from yDNA haplogroup H5. Haplogroup H5 was not found in the village dogs from the Malay Archipelago but it is common in Taiwan. One H5 specimen from Taiwan clustered with one H60 from Australia with the indication of a common male ancestor 4-5,000 YBP and coincides with the expansion of the Daic people of Southern China. The conclusion is that there were 2 expansions of two types of dogs. Southern China produced the first ancient regional breeds 8,000 years ago. These were then dominated and replaced by a later explosive expansion of genetically diverse dogs that had been bred in South East Asia. If so, the dingo and the New Guinea Singing Dog, that pre-date the dogs of the Malay Archipelago, would reflect the last vestiges of the earlier ancient breeds.
The existence of a genetic subdivision within the dingo population has been proposed over two decades but has not been investigated. In 2016, a study compared DNA sequences using the entire mDNA genome (16,000 base pairs in length), and 13 DNA loci of the cell nucleus, taken from dingoes and New Guinea singing dogs. The study of their maternal mDNA provided evidence that they form a monophyletic clade (indicating that they all carried the same mutation inherited from a single female ancestor in the past). Dogs from China, Bali and Kalimantan did not fall within this clade. There are two distinct populations of dingoes in Australia based on both mitochondrial and nuclear evidence. The dingoes found today in the northwestern part of the Australian continent are estimated to have diverged 8,300 YBP, followed by a divergence of the New Guinea singing dog from the southeastern dingoes 7,800 YBP. As the New Guinea singing dog is closely related to the southeastern dingoes, these divergences are thought to have occurred somewhere in Sahul (a landmass which once included Australia, New Guinea and some surrounding islands) that existed until 6,500-8,000 years ago. The New Guinea singing dog then became a distinct but closely related lineage. The Fraser Island dingoes were unique because they cluster with the southeastern dingoes but exhibit many alleles (gene expressions) similar to the New Guinea singing dog, in addition to showing signs of admixture with the northwestern dingoes. These dates suggest that dingoes spread from Papua New Guinea to Australia over the land bridge at least twice. The lack of fossil evidence from northern Australia and Papua New Guinea could be explained by their tropical climate and acidic soil, as there are generally few fossils found in these regions. In 2017, a study of dingoes across a wider area found that the New Guinea singing dog female lineage is more closely related to the southeastern dingoes, and its male lineage is more closely related to dingoes found across the rest of the continent, indicating that the dingo lineage has a complex history.
The dingo and New Guinea singing dog lineage can be traced back through the Malay Archipelago to Asia. Therefore, the dingo is not a "wild dog" but a domesticated dog that has gone feral. Human-dog relationships are fluid, and a classification of being either completely "wild" or completely "domesticated" becomes difficult. They have adapted to surviving without human assistance and are the only known dog population to have maintained a long-term independence from humans.
The dingo is a medium-sized canid with a lean, hardy body that is designed for speed, agility and stamina. The head is the widest part of the body, is wedge-shaped and large in proportion to the body. The skull is more like that of the golden jackal than it is to the wolf or coyote. Compared with the skull of the dog, the dingo possesses a longer muzzle, longer carnassial teeth, longer and more slender canine teeth, a larger auditory bullae, a flatter cranium with a larger sagittal crest and larger nuchal lines. In 2014, a study was conducted on pre-20th century dingo specimens that are unlikely to have been influenced by later hybridisation. The dingo skull was found to differ relative to the domestic dog by its larger palatal width, longer rostrum, shorter skull height, and wider sagittal crest. Based on a comparison with the remains of a dingo found at Fromme's Landing, the dingo's skull and skeleton have not changed over the past 3,000 years.
Captive dingoes are longer and heavier than wild dingoes as they have access to better food and veterinary care. The average wild dingo male weighs 15.8 kg (35 lb) and the female 14.1 kg (31 lb), compared with the captive male 18.9 kg (42 lb) and the female 16.2 kg (36 lb). The average wild dingo male length is 125 cm (49 in) and the female 122 cm (48 in), compared with the captive male 136 cm (54 in) and the female 133 cm (52 in). The average wild dingo male stands at the shoulder height of 59 cm (23 in) and the female 56 cm (22 in), compared with the captive male 56 cm (22 in) and the female 53 cm (21 in). Dingoes rarely carry excess fat and the wild ones display exposed ribs. Dingoes from northern and northwestern Australia are often larger than those found in central and southern Australia.
The dingo's three main coat colours are described as being either light ginger (or tan), black and tan, or creamy white. The ginger colour ranges from a deep rust to a pale cream and can be found in 74% of dingoes. There is often small white markings on the tip of the tail, the feet, and the chest but there are no large white patches. Some do not exhibit white tips. The black and tan dingoes possess a black coat with a tan muzzle, chest, belly, legs and feet and can be found in 12% of dingoes. Solid white can be found in 2% of dingoes and solid black 1%. Coat colours with sable, ticking, or brindle indicates some hybridisation and can be found in 12% of dingoes. There are only 3 genes that affect coat colour in the dingo compared with 9 genes in the domestic dog. The ginger colour is dominant and carries the other three main colours - black, tan and white. White dingoes breed true, and black and tan dingoes breed true; when these cross the result is a sandy colour. The coat is not oily, nor does not have a dog-like odour. The dingo has a single coat in the tropical north of Australia and a double thick coat in the cold mountains of the south, the undercoat being a wolf-grey colour.
The dingo's tail is flatish, tapering after mid-length and does not curve over the back but is carried low. The ears are erect and occur high on the skull. The eyes are triangular (or almond) shaped and are hazel to dark in colour with dark rims. When walking, the dingo's rear foot steps in line with the front foot, and these do not possess dewclaws. Dingoes in the wild live between 3–5 years with few living past 7–8 years. Some have been recorded living up to 10 years. In captivity dingoes live between 12–14 years of age. The dingo is similar to the New Guinea singing dog in morphology apart from the dingo's greater height at the withers.
Hybrids, distribution and habitatEdit
The wolf-like canids are a group of large carnivores that are genetically closely related because their chromosomes number 78, therefore they can potentially interbreed to produce fertile hybrids. In the Australian wild there exists dingoes, feral dogs, and the crossings of these two which produces dingo-dog hybrids. Most studies looking at the distribution of dingoes focus on the distribution of dingo-dog hybrids instead.
Dingoes occurred throughout mainland Australia before European settlement. Dingoes are not found in the fossil record of Tasmania, therefore they arrived in Australia after Tasmania had separated from the mainland due to rising sea levels. The introduction of agriculture reduced dingo distribution, and by the early 1900s large barrier fences, including the Dingo Fence, excluded them from the sheep grazing areas. Land clearance, poisoning, and trapping caused the extinction of the dingo and hybrids from most of their former range in southern Queensland, New South Wales, Victoria and South Australia. Today, they are absent from most of New South Wales, Victoria, the south-eastern third of South Australia, and the south-western tip of Western Australia. They are sparse in eastern half of Western Australia and the adjoining areas of the Northern Territory and South Australia. They are regarded as common across the remainder of the continent.
The dingo could be considered an ecotype or an ecospecies which has adapted to Australia's unique environment. The dingo's present distribution covers a variety of habitats, including the temperate regions of eastern Australia, the alpine moorlands of the eastern highlands,the arid hot deserts of Central Australia, and the tropical forests and wetlands of Northern Australia. The occupation of, and adaption to, these habitats may have been assisted by their relationship with indigenous Australians.
A twenty-year study of the dingo's diet was conducted across Australia by the federal and state governments. These examined a total of 13,000 stomach contents and fecal samples. For the fecal samples, it was possible to determine the matching tracks of foxes and feral cats and not include these samples in the study, but it was impossible to distinguish between the tracks left by dingoes from those of dingo hybrids or feral dogs. The study found that these canines prey on 177 species represented by 72.3% mammals (71 species), 18.8% birds (53 species), 3.3% vegetation (seeds), 1.8% reptiles (23 species), and 3.8% insects, fish, crabs, and frogs (28 species). The relative proportions of prey is much the same across Australia, apart from more birds being eaten in the north and south-east coastal regions, and more lizards in Central Australia. Some 80% of the diet consisted of 10 species: red kangaroo, swamp wallaby, cattle, dusky rat, magpie goose, common brushtail possum, long-haired rat, agile wallaby, European rabbit, and the common wombat. Of the mammals eaten, 20% could be regarded as large.
However, the relative proportions of the size of prey mammals varied across regions. In the tropical coast region of the Northern Territory, agile wallabies, dusky rats and magpie geese formed 80% of the diet. In Central Australia, the rabbit has become a substitute for native mammals, and during droughts cattle carcasses provide most of the diet. On the Barkly Tableland, there are no rabbits nor does any native species dominate the diet, except for long-haired rats that form plagues every 9 years. In the Fortescue River region, the large red kangaroo and euro dominate the diet as there are few smaller mammals in this area. On the Nullarbor Plain, rabbits and red kangaroos dominate the diet, and twice as much rabbit eaten as red kangaroo. In the temperate mountains of eastern Australia, swamp wallaby and red-necked wallaby dominate the diet on the lower slopes and wombat on the higher slopes. Possums are commonly eaten here when found on the ground. In coastal regions dingoes patrol the beaches for washed-up fish, seals, penguins and other birds.
Dingoes drink approximately one litre of water each day in the summer and half a litre in winter. In arid regions during the winter, dingoes may live from the liquid in the bodies of their prey, as long as the number of prey is sufficient. In arid Central Australia, weaned pups draw most of their water from their food. There, regurgitation of water by the females for the pups was observed. During lactation, captive females have no higher need of water than usual, since they consume the urine and feces of the pups and therefore recycle the water and keep the den clean. Tracked dingoes in the Strzelecki Desert regularly visited water-points every 3–5 days, with two dingoes surviving 22 days without water during both winter and summer.
Dingoes, dingo hybrids and feral dogs usually attack from the rear as they pursue their prey. They kill their prey by biting the throat, which damages the trachea and the major blood vessels of the neck. The size of the hunting pack is determined by the type of prey targeted, with large packs formed to help hunt large prey. Large prey can include kangaroos, cattle, water buffalo and wild horses. Dingoes will assess and target prey based on the prey's ability to inflict damage on dingoes. Large kangaroos are the most commonly killed prey. The main tactic is to sight the kangaroo, bail it up, then kill it. Dingoes typically hunt large kangaroos by having lead dingoes chase the quarry toward the paths of their packmates, which are skilled at cutting corners in chases. The kangaroo becomes exhausted and is then killed. This same tactic is used by wolves, African hunting dogs, and hyenas. Another tactic shared with African hunting dogs is a relay pursuit until the prey is exhausted. A pack of dingoes is three times as likely to bring down a kangaroo than an individual because the killing is done by those following the lead chaser, which has also become exhausted. There are two patterns of the final stage of the attack. An adult or juvenile kangaroo is nipped at the hamstrings of the hind legs to slow it before an attack to the throat. A small adult female or juvenile is bitten on the neck or back by dingoes running beside them. In one area of Central Australia, dingoes hunt kangaroos by chasing them into a wire fence where they become temporarily immobilised. The largest male red kangaroos tend to ignore dingoes, even when the dingoes are hunting the younger males and females. A large eastern grey kangaroo successfully fought off an attack by a single dingo which lasted for over an hour. Wallabies are hunted in a similar manner to kangaroos, the difference being that a single dingo will hunt using scent rather than sight and the hunt may last for several hours.
Dingo packs may attack young cattle and buffalo but never healthy, grown adults. They focus on the sick or injured young. The tactics include harassing a mother with young, panic a herd to separate the adults from the young, or watch a herd and look for any unusual behaviour that might then be exploited. One 1992 study in the Fortescue River region observed that cattle will defend their calves by circling around the calves or aggressively charging dingoes. In one study of 26 approaches, 24 were by more than one dingo and only 4 resulted in calves being killed. Dingoes often revisited carcasses. They did not touch fresh cattle carcasses until these were largely skin and bone, and even when these were plentiful they still preferred to hunt kangaroo. Out of 68 chases of sheep, 26 sheep were seriously injured but only 8 were killed. The dingoes could outrun the sheep and the sheep were defenceless. However, the dingoes in general appeared not to be motivated to kill sheep, and in many cases just loped alongside the sheep before veering off to chase another sheep. For those that did kill and consume sheep, there was still a large quantity of kangaroo in their diet, indicating once again a preference for kangaroo.
Lone dingoes can run down a rabbit, but are more successful by targeting kittens near rabbit warrens. Dingoes will take young nestlings or young birds, in addition to birds that are moulting and therefore cannot fly. In the coastal wetlands of northern Australia, dingoes depend on magpie geese for a large part of their diet and a lone dingo will sometimes distract these while a white breasted sea eagle makes a kill which is too heavy for it to carry off, with the dingo then driving the sea eagle away. They will also scavenge on prey dropped from the nesting platforms of sea eagles. Lone dingoes may hunt small rodents and grasshoppers in grass by using their sense of smell and hearing, then pouncing on them with their forepaws.
Dingoes and their hybrids co-exist with the native Quoll. They also co-occur in the same territory as the introduced European red fox and feral cat, but little is known about the relationships between these three. Dingoes and their hybrids will drive off foxes from sources of water and occasionally eat feral cats. Dingoes can be killed by buffalo and cattle goring and kicking them, from snake bite, and predation on their pups by wedge-tailed eagles.
Like all domestic dogs, dingoes tend towards phonetic communication. However, in contrast to domestic dogs, dingoes howl and whimper more, and bark less. Eight sound classes with 19 sound types have been identified.
Compared to most domestic dogs, the bark of a dingo is short and monosyllabic, and is rarely used. Barking was observed to make up only 5% of vocalisations. Dog barking has always been distinct from wolf barking. Australian dingoes bark mainly in swooshing noises or in a mixture of atonal and tonal sounds. In addition, barking is almost exclusively used for giving warnings. Warn-barking in a homotypical sequence and a kind of "warn-howling" in a heterotypical sequence have also been observed. The bark-howling starts with several barks and then fades into a rising and ebbing howl and is probably (similar to coughing) used to warn the puppies and members of the pack. Additionally, dingoes emit a sort of "wailing" sound, which they mostly use when approaching a wateringhole, probably to warn already present dingoes.
According to the present state of knowledge, it is not possible to get Australian dingoes to bark more frequently by putting them in contact with other domestic dogs. However, German zoologist Alfred Brehm reported a dingo that learned the more "typical" form of barking and how to use it, while its brother did not. Whether dingoes bark or bark-howl less frequently in general is not certain.
Dingoes have three basic forms of howling (moans, bark-howls and snuffs) with at least 10 variations. Usually, three kinds of howls are distinguished: long and persistent, rising and ebbing, and short and abrupt.
Observations have shown that each kind of howling has several variations, though their purpose is unknown. The frequency of howling varies with the season and time of day, and is also influenced by breeding, migration, lactation, social stability and dispersal behaviour. Howling can be more frequent in times of food shortage, because the dogs become more widely distributed within their home range.
Additionally, howling seems to have a group function, and is sometimes an expression of joy (for example, greeting-howls). Overall howling was observed less frequently in dingoes than among grey wolves. It may happen that one dog will begin to howl, and several or all other dogs will howl back and bark from time to time. In the wilderness, dingoes howl over long distances to attract other members of the pack, to find other dogs, or to keep intruders at bay. Dingoes howl in chorus with significant pitches, and with increasing number of pack-members, the variability of pitches also increases. Therefore, it is suspected that dingoes can measure the size of a pack without visual contact. Moreover, it has been proposed that their highly variable chorus howls may generate a confounding effect in the receivers by making pack size appear larger.
Other forms of communicationEdit
Growling, making up approximately 65% of the vocalisations, is used in an agonistic context for dominance, and as a defensive sound. Similar to many domestic dogs, a reactive usage of defensive growling is only rarely observed. Growling very often occurs in combination with other sounds, and has been observed almost exclusively in swooshing noises (similar to barking).
During observations in Germany, dingoes were heard to produce a sound that observers have called Schrappen. It was only observed in an agonistic context, mostly as a defence against obtrusive pups or for defending resources. It was described as a bite intention, during which the receiver is never touched or hurt. Only a clashing of the teeth could be heard.
Aside from vocal communication, dingoes communicate, like all domestic dogs, via scent marking specific objects (for example, Spinifex) or places (such as waters, trails and hunting grounds) using chemical signals from their urine, feces and scent glands. Males scent-mark more frequently than females, especially during the mating season. They also scent-rub, whereby a dog rolls its neck, shoulders, or back on something that is usually associated with food or the scent markings of other dogs.
Unlike wolves, dingoes can react to social cues and gestures from humans.
Dingoes tend to be nocturnal in warmer regions, but less so in cooler areas. Their main period of activity is around dusk and dawn. The periods of activity are short (often less than one hour) with short times of resting. Dingoes have two kinds of movement: a searching movement (apparently associated with hunting) and an exploratory movement (probably for contact and communication with other dogs). According to studies in Queensland, the wild dogs (dingo hybrids) there, move freely at night through urban areas and cross streets and seem to get along quite well.
The dingo's social behaviour is about as flexible as that of a coyote or gray wolf, which is perhaps one of the reasons it was initially believed that the dingo was descended from the Indian wolf. While young males are often solitary and nomadic in nature, breeding adults will often form a settled pack. However, in areas of the dingo's habitat with a widely spaced population, breeding pairs remain together, apart from others. Dingo distributions are a single dingo, 73%, two dingoes, 16%, three dingoes, 5%, four dingoes, 3% and packs of five to seven dingoes, 3%. A dingo pack usually consists of a mated pair, their offspring from the current year and sometimes offspring from the previous year.
Where conditions are favourable among dingo packs, the pack is stable with a distinct territory and little overlap between neighbors. The size of packs often appears to correspond to the size of prey that appears in the pack's territory. Desert areas have smaller groups of dingoes with a more loose territorial behaviour and sharing of the water sites. It has been noted that the average monthly pack size was between three and twelve members.
Similar to other canids, a dingo pack largely consists of a mated pair, their current year's offspring, and occasionally a previous year's offspring. There are dominance hierarchies both between and within males and females, with males usually being more dominant than females. However, a few exceptions have been noted in captive packs. During travel, while eating prey, or when approaching a water source for the first time, the breeding male will be seen as the leader, or alpha. Subordinate dingoes will approach a more dominant dog in a slightly crouched posture, ears flat and tail down, to ensure peace in the pack. Establishment of artificial packs in captive dingoes have failed.
Dingoes breed once annually, depending on the estrus cycle of the females which, according to most sources, only come in heat once per year. Dingo females can come in heat twice per year, but can only be pregnant once a year, with the second time only seeming to be pregnant.
Males are virile throughout the year in most regions, but have a lower sperm production during the summer in most cases. During studies on dingoes from the Eastern Highlands and Central Australia in captivity, no specific breeding cycle could be observed. All were potent throughout the year. The breeding was only regulated by the heat of the females. A rise in testosterone was observed in the males during the breeding season, but this was attributed to the heat of the females and copulation. In contrast to the captive dingoes, captured dingo males from Central Australia did show evidence of a male breeding cycle. Those dingoes showed no interest in females in heat (this time other domestic dogs) outside of the mating season (January to July) and did not breed with them.
The mating season usually occurs in Australia between March and May (according to other sources between April and June). During this time, dingoes may actively defend their territories using vocalisations, dominance behaviour, growling and barking.
Most females in the wild start breeding at the age of two years. Within packs, the alpha female tends to go into heat before subordinates and actively suppresses mating attempts by other females. Males become sexually mature between the ages of one and three years. The precise start of breeding varies depending on age, social status, geographic range and seasonal conditions. Among dingoes in captivity, the pre-estrus was observed to last 10–12 days. However, it is suspected that the pre-estrus may last as long as 60 days in the wild.
In general, the only dingoes in a pack that successfully breed are the alpha pair, and the other pack members help with raising the pups. Subordinates are actively prevented from breeding by the alpha pair and some subordinate females have a false pregnancy. Low-ranking or solitary dingoes can successfully breed if the pack structure breaks up.
The gestation period lasts for 61–69 days and the size of the litter can range from one to 10 (usually five) pups, with the number of males born tending to be higher than that of females. Pups of subordinate females usually get killed by the alpha female, which causes the population increase to be low even in good times. This behaviour possibly developed as an adaptation to the fluctuating environmental conditions in Australia. Pups are usually born between May and August (the winter period), but in tropical regions, breeding can occur at any time of the year.
At the age of three weeks, the pups leave the den for the first time, and leave it completely at eight weeks. In Australia, dens are mostly underground. There are reports of dens in abandoned rabbit burrows, rock formations, under boulders in dry creeks, under large spinifex, in hollow logs, in augmented burrows of monitor lizards and wombat burrows. The pups usually stray around the den within a radius of 3 km (2 mi), and are accompanied by older dogs during longer travels. The transition to consuming solid food is normally accompanied by all members of the pack during the age of 9 to 12 weeks. Apart from their own experiences, pups also learn through observation. Young dingoes usually become independent at the age of three to six months or they disperse at the age of 10 months when the next mating season starts.
Dingoes usually remain in one area and do not undergo seasonal migrations. However, during times of famine, even in normally "safe" areas, dingoes travel into pastoral areas, where intensive, human-induced control measures are undertaken. It was noted in Western Australia in the 1970s that young dogs can travel for long distances when necessary. About 10% of the dogs captured—all younger than 12 months—were later recaptured far away from their first location. Among these, 10% of the travelled distance for males was 21.7 km (13.5 mi) and for females 11 km (7 mi). Therefore, travelling dingoes had lower chances of survival in foreign territories, and it was apparently unlikely that they would survive long migrations through occupied territories. The rarity of long migration routes seemed to confirm this. During investigations in the Nullarbor Plain, even longer migration routes were recorded. The longest recorded migration route of a radio-collared dingo was about 24–32 km (15–20 mi).
Attacks on humansEdit
Although dingoes are large enough to be dangerous, they generally avoid conflict with humans. Apart from the well-known case in which an infant was taken from a campsite (see below), there have been numerous confirmed dingo attacks, often involving people feeding wild dingoes, particularly on Fraser Island, a special center of dingo-related tourism (see main article). Most dingo attacks are minor in nature, but some can be major, and a few can be fatal. Many Australian national parks have signs advising visitors not to feed wildlife, partly because this practice is not healthy for the animals, and partly because it may encourage undesirable behaviour, such as snatching or biting by dingoes, kangaroos, goannas and some birds.
Some researchers propose that the dingo caused the extinction of the thylacine, the Tasmanian devil and the Tasmanian nativehen from mainland Australia because of the correlation in space and time with the dingo's arrival. Recent studies have questioned this proposal, suggesting that climate change and increasing human populations may have been the cause. Dingoes do not seem to have had the same ecological impact that the red fox had in later times. This might be connected to the dingo's way of hunting and the size of their favoured prey, as well as to the low number of dingoes in the time before European colonisation.
The assumption that dingoes and thylacines were competitors for the same prey stems from their external similarities; the thylacine had a stronger and more efficient bite, but was probably dependent on relatively small prey, while the dingo's stronger skull and neck would have allowed it to bring down bigger prey. The dingo was probably a superior hunter, as it hunted cooperatively in packs and could better defend resources, while the thylacine was probably more solitary. Also, wild dingo populations might have had demographic support from conspecific living with humans.
The extinction of the thylacine on the continent around 2,000 years ago has also been linked to changes in climate and land use by the Aborigines. It is plausible to name the dingo as the cause of the extinction, but significant morphological differences between the two suggest that the ecological overlapping of both species might be exaggerated. The dingo has the dentition of a generalist, while the thylacine had the dentition of a specialist carnivore without any signs of consumption of carrion or bones. It is also argued that the thylacine was a flexible predator that should have withstood the competition by the dingo, but was instead wiped out due to human persecution.
This theory does not explain how the Tasmanian devil and the dingo coexisted on the same continent until about 430 years ago, when the dingo supposedly caused the Tasmanian devil's demise. The group dynamics of dingoes should have successfully kept devils away from carrion, and since dingoes are able to break bones, little would have been left for the devils to scavenge. Additionally, devils are successful hunters of small- to medium-sized prey, so there should have been an overlapping of the species in this area, too. Furthermore, the arguments that the dingo caused the extinction of the thylacine, the devil and the hen are in direct conflict with each other. If the dingo were really so similar to the thylacine and the Tasmanian devil in its ecological role and suppressed both, then coexisting with both for such an extended time is strange. Although this is a possible result of the dingo's introduction, critics regard the evidence for this as insubstantial.
In 2017, a genetic study found that the population of the northwestern dingoes had commenced expanding since 4,000—6,000 years ago. This was proposed to be due to either their first arrival in Australia or due to the commencement of the extinction of the Tasmanian tiger with the dingo expanding into the Tasmanian tiger's former range.
The dingo is regarded as part of the native Australian fauna by many environmentalists and biologists, as these dogs existed on the continent before the arrival of the Europeans and a mutual adaptation of the dingoes and their surrounding ecosystems had occurred.
Much of the present place of wild dogs in the Australian ecosystem, especially in the urban areas, remains unknown. Although the ecological role of dingoes in Northern and Central Australia is well understood, the same does not apply to the role of wild dogs in the east of the continent. In contrast to some claims, dingoes are assumed to have a positive impact on biodiversity in areas where feral foxes are present.
Dingoes are regarded as apex predators and possibly perform an ecological key function. It is likely (with increasing evidence from scientific research) that they control the diversity of the ecosystem by limiting the number of prey and keeping the competition in check. Wild dogs hunt feral livestock such as goats and pigs, as well as native prey and introduced animals. The low number of feral goats in Northern Australia is possibly caused by the presence of the dingoes, but whether they control the goats' numbers or not is still disputable. Studies from 1995 in the northern wet forests of Australia found the dingoes there did not reduce the number of feral pigs, but their predation only affects the pig population together with the presence of water buffaloes (which hinder the pigs' access to food).
Observations concerning the mutual impact of dingoes and red fox and cat populations suggest dingoes limit the access of foxes and cats to certain resources. As a result, it is assumed that a disappearance of the dingoes may cause an increase of red fox and feral cat numbers and, therefore, a higher pressure on native animals. These studies found the presence of dingoes is one of the factors that keep fox numbers in an area low, and therefore reduces pressure on native animals, which then do not disappear from the area. The countrywide numbers of red foxes are especially high where dingo numbers are low, but other factors might responsible for this, depending on the area. Evidence was found for a competition between wild dogs and red foxes in the Blue Mountains of New South Wales, since there were many overlaps in the spectrum of preferred prey, but there was only evidence for local competition, not on a grand scale.
It is also possible that dingoes can live with red foxes and feral cats without reducing their numbers in areas with sufficient food resources (for example, high rabbit numbers) and hiding places. Nearly nothing is known about the relationship of wild dogs and feral cats, except both mostly live in the same areas. Although wild dogs also eat cats, it is not known whether this affects the cat populations. At the moment, the Invasive Animals Cooperative Research Centre is investigating the exact effects of dingoes on the fox and cat populations to determine the benefits of keeping the dog in certain areas of Australia. In many areas, wild dogs live together with the most species of quolls, except for the eastern quoll, which is probably extinct on the mainland, so wild dogs are not regarded as a threat to them.
Additionally, the disappearance of dingoes might increase the prevalence of kangaroo, rabbit and Australian brushturkey numbers. In the areas outside the Dingo Fence, the number of dingoes and emus is lower than in the areas inside. However, the numbers changed depending on the habitat. Since the environment is the same on both sides of the fence, the dingo was assumed to be a strong factor for the regulation of these species.[clarification needed] Therefore, some people demand that dingo numbers should be allowed to increase or dingoes should be reintroduced in areas with low dingo populations to lower the pressure on endangered populations of native species and to reintroduce them in certain areas. In addition, the presence of the Australian brushturkey in Queensland increased significantly after dingo baiting was conducted.
Cultural opinions about the dingo are often based on its perceived "cunning", and the idea that it is an intermediate between civilisation and wildness.
Some of the early European settlers looked on dingoes as domestic dogs, while others thought they were more like wolves. Over the years, dingoes began to attack sheep, and their relationship to the Europeans changed very quickly: they were regarded as devious and cowardly, since they did not fight bravely in the eyes of the Europeans, and vanished into the bush. Dingoes were seen as predators that killed wantonly, rather than out of hunger (similar claims are made today concerning dingo-hybrids). Additionally, they were seen as promiscuous or as devils with a venomous bite or saliva, and so they could be killed unreservedly. Over the years, dingo trappers gained some prestige for their work, especially when they managed to kill hard to catch dingoes. Dingoes were associated with thieves, vagabonds, bushrangers and parliamentary opponents. From the 1960s, politicians began calling their opponents "dingo," meaning they were cowardly and treacherous, and it has become a popular form of attack since then. Today, the word "dingo" still stands for "coward" and "cheat," with verb and adjective forms used, as well.
The dingo plays a prominent role in the dreamtime stories of indigenous Australians, however it is rarely depicted in their cave paintings when compared with the extinct thylacine. One of the tribal elders of the people of the Yarralin, Northern Territory region tells that the dreamtime dingo is the ancestor of both dingoes and humans. The dingoes "are what we would be if we were not what we are."
Similar to how Europeans acquired dingoes, the Aboriginal people of Australia acquired dogs from the immigrants very quickly. This process was so fast that Francis Barrallier (surveyor on early expeditions around the colony at Port Jackson) discovered in 1802 that five dogs of European origin were there before him. One theory holds that other domestic dogs will adopt the role of the "pure" dingo. Introduced animals, such as the water buffalo and the domestic cat, have been adopted into the indigenous Aboriginal culture in the forms of rituals, traditional paintings and dreamtime stories.
Most of the published myths originate from the Western Desert and show a remarkable complexity. In some stories, dingoes are the central characters, while in others, they are only minor ones. One time, it is an ancestor from the dreamtime who created humans and dingoes or gave them their current shape. There are stories about creation, socially acceptable behaviour, and explanations why some things are the way they are. There are myths about shapeshifters (human to dingo or vice versa), "dingo-people," and the creation of certain landscapes or elements of those landscapes, like waterholes or mountains.
Livestock farming commenced expanding across Australia from the early 1800s, which led to conflict between the dingo and graziers. Sheep, and to a lesser extent cattle, are an easy target for dingoes. The pastoralists and the government bodies that support this industry have shot, trapped, and poisoned dingoes or destroyed dingo pups in their dens. After two centuries of persecution, the dingo or dingo–dog hybrids can still be found across most of the continent.
Research on the real extent of the damage and the reason for this problem only started recently. Livestock can die from many causes and, when the carcass is found, it is often difficult to determine with certainty the cause of death. Since the outcome of an attack on livestock depends to a high degree on the behaviour and experience of the predator and the prey, only direct observation is certain to determine whether an attack was by dingoes or another domestic dog. Even the existence of remnants of the prey in the scat of wild dogs do not prove they are pests, since wild dogs also eat carrion. Exact numbers or reliable estimates of the damage caused by wild dogs are, therefore, hard to obtain and are seldom reliable. Even if livestock is not a big part of the dingo's diet, the extent of damage dingoes could potentially cause to the livestock industry could be much larger because of wanton killing.
The significance of dingoes as a pest is based primarily on the predation of sheep and, to a lesser extent, on cattle, and is not connected only to the direct loss of livestock. Harassment of sheep can cause a less optimal use of grassland and miscarriages.
The cattle industry can tolerate low to moderate, and sometimes high, grades[clarification needed] of wild dogs (therefore dingoes are not so easily regarded as pests in these areas). In the case of sheep and goats, a zero-tolerance attitude is common. The biggest threats are dogs that live inside or near the paddock areas. The extent of sheep loss is hard to determine, due to the wide pasture lands in some parts of Australia. The numbers of cattle losses is much more variable and less well-documented. Although the loss of cattle can rise up to 30%, the normal loss rate is about 0–10%.
Therefore, factors such as availability of native prey, as well as the defending behaviour and health of the cattle, play an important role in the number of losses. A study in Central Australia in 2003 confirmed that dingoes only have a low impact on cattle numbers when a sufficient supply of other prey (such as kangaroos and rabbits) is available. In some parts of Australia, it is assumed that the loss of calves can be minimised if horned cattle are used instead of polled. The precise economic impact is not known in this[which?] case, and it is unlikely that the rescue of some calves compensates for the necessary costs of control measures. Calves usually suffer less lethal wounds than sheep due to their size and the protection by the adult cattle, and therefore have a higher chance of surviving an attack. As a result, the evidence of a dog attack may only be discovered after the cattle have been herded back into the enclosure,[clarification needed] and signs such as bitten ears, tails and other wounds are discovered.
The opinions of cattle owners regarding dingoes are more variable than those of sheep owners. Some cattle owners believe that it is better that the weakened mother loses her calf in times of drought so that she does not have to care for her calf, too. Therefore, these owners are more hesitant to kill dingoes. The cattle industry may benefit from the predation of dingoes on rabbits, kangaroos and rats. Furthermore, the mortality rate of calves has many possible causes, and it is difficult to discriminate between them. The only reliable method to document the damage would be to document all pregnant cows, then observe their development and that of their calves. The loss of calves in observed areas where dingoes were controlled was higher than in other areas. Loss of livestock is, therefore, not necessarily caused by the occurrence of dingoes and is independent from wild dogs. One researcher has stated that for cattle stations where dingoes were controlled, kangaroos were abundant, and this affects the availability of grass.
Domestic dogs are the only terrestrial predators in Australia that are big enough to kill fully-grown sheep, and only a few sheep manage to recover from the severe injuries. In the case of lambs, death can have many causes apart from attacks by predators, which are blamed for the deaths because they eat from the carcasses. Although attacks by red foxes are possible, such attacks are more rare than previously thought. The fact that the sheep and goat industry is much more susceptible to damage caused by wild dogs than the cattle industry is mostly due to two factors: the flight behaviour of the sheep and their tendency to flock together in the face of danger, and the hunting methods of wild dogs, along with their efficient way of handling goat and sheep.
Therefore, the damage to the livestock industry does not correlate to the numbers of wild dogs in an area (except that there is no damage where no wild dogs occur).
According to a report from the government of Queensland, wild dogs cost the state about $30 million annually due to livestock losses, the spread of diseases and control measures. Losses for the livestock industry alone were estimated to be as high as $18 million. In Barcaldine, Queensland, up to one-fifth of all sheep are killed by dingoes annually, a situation which has been described as an "epidemic". According to a survey among cattle owners in 1995, performed by the Park and Wildlife Service, owners estimated their annual losses due to wild dogs (depending on the district) to be from 1.6% to 7.1%.
Despite the variety of estimates, there is little doubt that predation by dingoes can cause enormous economic damage, especially in times of drought when natural prey is sparse and the number of dingoes is still relatively high. Furthermore, wild dogs are involved in the spread of echinococcosis among cattle and sheep. An infection with echinococcosis can lead to confiscation of 90% of the intestines[clarification needed], which further leads to a value decrease of the meat and high economical damage.
Among the indigenous Australians, dingoes were also used as hunting aids, living hot water bottles and camp dogs. Their scalps were used as a kind of currency, their teeth were traditionally used for decorative purposes, and their fur for traditional costumes. In some parts of Australia, premiums are paid for dingo fur and scalps. The fur of dingoes generally has only a low value, and export of this fur is forbidden in states where they are protected. There is no widespread commercial catching and killing of dingoes for the purposes of obtaining their fur.
Sometimes "pure" dingoes are important for tourism, when they are used to attract visitors. However, this seems to be common only on Fraser Island, where the dingoes are extensively used as a symbol to enhance the attraction of the island. Tourists are drawn to the experience of personally interacting with dingoes. Pictures of dingoes appear on brochures, many websites and postcards advertising the island. The use of dingo-urine as a repellent against kangaroos and wallabies has been considered, but has not yet been economically implemented.
The dingo is recognised as a native animal under the laws of all Australian jurisdictions. Australia has over five hundred national parks of which all but six are managed by the states and territories. As of 2017, the legal status of the dingo varies between these jurisdictions and in some instances it varies between different regions of a single jurisdiction.
- Australian Government: The Environment Protection and Biodiversity Conservation Act 1999 under section 528 defines a native species as one that was present in Australia before the year 1400. The dingo is protected in all Australian government managed national parks and reserves, World Heritage Areas, and other protected areas.
- Australian Capital Territory: The dingo is listed as a "pest animal" in the Pest Plants and Animals (Pest Animals) Declaration 2016 (No 1) made under the Pest Plants and Animals Act 2005, which calls for a management plan for pest animals. The Nature Conservation Act 2014 protects native animals in national parks and reserves but excludes this protection to "pest animals" declared under the Pest Plants and Animals Act 2005.
- New South Wales: The dingo falls under the definition of "wildlife" under the National Parks and Wildlife Act 1974 however it also becomes "unprotected fauna" under Schedule 11 of the act. The Wild Dog Destruction Act (1921) applies only to the western division of the state and includes the dingo in its definition of "wild dogs". The act requires landowners to destroy any wild dogs on their property and any person owning a dingo or half-bred dingo without a permit faces a fine. In other parts of the state, dingoes can be kept as pets under the Companion Animals Act 1998 as a dingo is defined under this act as a "dog". The dingo has been proposed for listing under the Threatened Species Conservation Act because it is argued that these dogs had established populations before the arrival of Europeans, however no decision has been made.
- Northern Territory: The dingo is a "vertebrate that is indigenous to Australia" and therefore "protected wildlife" under the Territory Parks and Wildlife Conservation Act 2014. A permit is required for all matters dealing with protected wildlife.
- Queensland: The dingo is listed as "least concern wildlife" in the Nature Conservation (Wildlife) Regulation 2006 under the Nature Conservation Act 1992, therefore the dingo is protected in National Parks and conservation areas. The dingo is listed as a "pest" in the Land Protection (Pest and Stock Route Management) Regulation 2003 under the Land Protection (Pest and Stock Route Management) Act 2002, which requires land owners to take reasonable steps to keep their lands free of pests.
- South Australia: The National Parks and Wildlife Act 1972 defines a protected animal as one that is indigenous to Australia but then lists the dingo as an "unprotected species" under Schedule 11. The purpose of the Dog Fence Act 1946 is to prevent wild dogs entering into the pastoral and agricultural areas south of the dog-proof fence. The dingo is listed as a "wild dog" under this act, and landowners are required to maintain the fence and destroy any wild dog within the vicinity of the fence by shooting, trapping or baiting. The dingo is listed as an "unprotected species" in the Natural Resources Management Act 2004, which allows landowners to lay baits "to control animals" on their land just north of the dog fence.
- Tasmania: Tasmania does not have a native dingo population. The dingo is listed as a "restricted animal" in the Nature Conservation Act 2002 and cannot be imported without a permit. Once imported into Tasmania, a dingo is listed as a dog under the Dog Control Act 2000.
- Victoria: The dingo is a "vertebrate taxon" that is "indigenous" to Australia and therefore "wildlife" under the Wildlife Act 1975, which protects wildlife. The act mandates that a permit is required to keep a dingo, and that this dingo must not be cross-bred with a dog. The act allows an order to be made to unprotect dingoes in certain areas of the state. The Order in Council made on the 28 September 2010 includes the far north-west of the state and all of the state north-east of Melbourne. It was made to protect stock on private land. The order allows dingoes to be trapped, shot or baited by any person on private land in these regions, while protecting the dingo on state-owned land.
- Western Australia: Dingoes are considered as "unprotected" native fauna under the Western Australian Wildlife Conservation Act. The dingo is recorded as a "declared pest" on the Western Australian Organism List. This list records those species that have been declared as pests under the Biosecurity and Agriculture Management Act 2007, and these are regarded as pests across all of Western Australia. Landowners must take the prescribed measures to deal with declared pests on their land. The policy of the WA government is to promote eradication of dingoes in the livestock grazing areas but leave them undisturbed in the rest of the state.
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Dingo attacks on livestock led to widescale efforts to repel them from areas with intensive agricultural usage, and all states and territories have enacted laws for the control of dingoes. In the early 20th century, fences were erected to keep dingoes away from areas frequented by sheep, and a tendency to routinely eradicate dingoes developed among some livestock owners. Established methods for the control of dingoes in sheep areas entailed the employment of specific workers on every property. The job of these people (who were nicknamed "doggers") was to reduce the number of dingoes by using steel traps, baits, firearms and other methods. The responsibility for the control of wild dogs lay solely in the hands of the landowners. At the same time, the government was forced to control the number of dingoes. As a result, a number of measures for the control of dingoes developed over time. It was also considered that dingoes travel over long distances to reach areas with richer prey populations, and the control methods were often concentrated along "paths" or "trails" and in areas that were far away from sheep areas. All dingoes were regarded as a potential danger and were hunted.
Apart from the introduction of the poison 1080 (extensively used for 40 years and nicknamed "doggone"), the methods and strategies for controlling wild dogs have changed little over time. Information concerning cultural importance to indigenous people and the importance of dingoes and the impact of control measures on other species is also lacking in some areas. Historically, the attitudes and needs of indigenous people were not taken into account when dingoes were controlled. Other factors that might be taken into account are the genetic status (degree of interbreeding) of dingoes in these areas, ownership and land usage, as well as a reduction of killing measures to areas outside of the zones. However, most control measures and the appropriate studies are there to minimise the loss of livestock and not to protect dingoes.
Increasing pressure from environmentalists against the random killing of dingoes, as well as the impact on other animals, demanded that more information needed to be gathered to prove the necessity of control measures and to disprove the claim of unnecessary killings. Today, permanent population control is regarded as necessary to reduce the impact of all wild dogs and to ensure the survival of the "pure" dingo in the wild.
One method that does not have any proven effect is to hang dead dogs along the borders of the property in the belief that this would repel wild dogs.
To keep wild dogs away from certain areas, efforts are taken to make these areas unattractive for them (for example, by getting rid of food waste) and therefore forcing them to move elsewhere. Control through deliberately spreading disease is normally not considered. Such attempts probably would not be successful, because typical dog diseases are already present in the population. Additionally, dogs under human care would also be susceptible. Other biological control methods are not regarded as achievable, since there would be a high risk of decimating dogs under human care.
In the 1920s, the Dingo Fence was erected on the basis of the Wild Dog Act (1921) and, until 1931, thousands of miles of Dingo Fences had been erected in several areas of South Australia. In the year 1946, these efforts were directed to a single goal, and the Dingo Fence was finally completed. The fence connected with other fences in New South Wales and Queensland. The main responsibilities in maintaining the Dingo Fence still lies with the landowners, whose properties border on the fence and receive financial support from the government.
A reward system (local, as well from the government) was active from 1846 to the end of the 20th century, but there is no evidence that – despite the billions of dollars spent – it was ever an efficient control method. Therefore, its importance declined over time.
Dingo scalping commenced in 1912 with the passage of the Wild Dogs Act by the government of South Australia. In an attempt to reduce depredation on livestock, that government offered a bounty for dingo skins, and this program was later repeated in Western Australia and the Northern Territory. One writer argues that this new legislation and economic driver had significant impacts on Aboriginal society in the region.
Strychnine is still used in all parts of Australia.
Baits with the poison 1080 are regarded as the fastest and safest method for dog control, since they are extremely susceptible. Even small amounts of poison per dog are sufficient (0.3 mg per kg). The application of aerial baiting is regulated in the Commonwealth by the Civil Aviation Regulations (1988). The assumption that the tiger quoll might be damaged by the poison led to the dwindling of areas where aerial baiting could be performed. In areas where aerial baiting is no longer possible, it is necessary to put down baits.
The eradication of dingoes due to livestock damage decreased along with the importance of the sheep industry and the usage of strychnine (which beforehand had been used for 100 years) in the 1970s. The number of doggers also decreased and the frequency of government-approved aerial baiting increased. During this period, many farmers in Western Australia switched to the cattle industry, and findings in the area of biology led to a significant change in control measures and techniques in association with reduced costs and increased efficiency. At the same time, the importance of 1080 increased.
Efficiency of measuresEdit
The efficiency of control measures was questioned in the past and is often questioned today, as well as whether they stand in a good cost-benefit ratio. The premium system proved to be susceptible to deception and to be useless on a large scale, and can therefore only be used for getting rid of "problem-dogs". Animal traps are considered inhumane and inefficient on a large scale, due to the limited efficacy of baits. Based on studies, it is assumed that only young dogs that would have died anyway can be captured. Furthermore, wild dogs are capable of learning and sometimes are able to detect and avoid traps quite efficiently. In one case, a dingo bitch followed a dogger and triggered his traps one after another by carefully pushing her paw through the sand that covered the trap.
Poisonous baits can be very effective when they are of good meat quality; however, they do not last long and are occasionally taken by red foxes, quolls, ants and birds. Aerial baiting can nearly eliminate whole dingo populations. Livestock guardian dogs can effectively minimise livestock losses, but are less effective on wide open areas with widely distributed livestock. Furthermore, they can be a danger to the livestock or be killed by control measures themselves when they are not sufficiently supervised by their owners. Fences are reliable in keeping wild dogs from entering certain areas, but they are expensive to build, need permanent maintenance, and only cause the problem to be relocated.
Control measures mostly result in smaller packs and a disruption of pack structure. The measures seem[which?] to be rather detrimental to the livestock industry because the empty territories are taken over by young dogs and the predation then increases. Nonetheless, it is regarded as unlikely that the control measures could completely eradicate the dingo in Central Australia, and the elimination of all wild dogs is not considered a realistic option.
It has been shown that culling a small percentage of immature dingoes on Fraser Island have little significant negative impact on the overall island population, though this is being disputed.
Until 2004, the dingo was categorized as of "least concern" on the Red List of Threatened Species. However, it has since been recategorised as "vulnerable," following the decline in numbers to around 30% of "pure" dingoes, due to crossbreeding with domestic dogs.
Dingoes are reasonably abundant in large parts of Australia, but there is some argument that they are endangered due to interbreeding with other dogs in many parts of their range. Dingoes are not a protected species, but they are regulated under federal law and, thus, their status varies in different states and territories. Dingoes receive varying levels of protection in conservation areas such as national parks and natural reserves in New South Wales, the Northern Territory and Victoria, Arnhem Land and other Aboriginal lands, UNESCO World Heritage Sites, and the whole of the Australian Capital Territory. In some states, dingoes are regarded as declared pests and landowners are allowed to control the local populations. Throughout Australia, all other wild dogs are considered pests.
Fraser Island is a 1,840 square kilometre World Heritage Site located off Australia’s eastern coast. The island is home to a genetically distinct population of dingoes that are free of dog introgression, estimated to number 120. These dingoes are unique because they are closely related to the southeastern dingoes but share a number of genes with the New Guinea singing dog and show some evidence of admixture with the northwestern dingoes. Because of their conservation value, in February 2013, a report on Fraser Island dingo management strategies was released, with options including ending the intimidation of dingoes, tagging practice changes and regular veterinarian checkups, as well as a permanent dingo sanctuary on the island. According to DNA examinations from 2004, the dingoes of Fraser Island are "pure", as opposed to dingo—dog hybrids. However, skull measurements from the mid-1990s had a different result. A 2013 study showed that dingoes living in the Tanami Desert are among the "purest" in Australia.
Groups that have devoted themselves to the conservation of the "pure" dingo by using breeding programs include the Australian Native Dog Conservation Society and the Australian Dingo Conservation Association. Presently, the efforts of the dingo conservation groups are considered to be ineffective because most of their dogs are untested or are known to be hybrids.
Dingo conservation efforts focus primarily on preventing interbreeding between dingoes and other domestic dogs in order to conserve the population of pure dingoes. This is extremely difficult and costly. Conservation efforts are hampered by the fact that it is not known how many pure dingoes still exist in Australia. Steps to conserve the pure dingo can only be effective when the identification of dingoes and other domestic dogs is absolutely reliable, especially in the case of living specimens. Additionally, conservation efforts are in conflict with control measures.
Conservation of pure and survivable dingo populations is promising in remote areas, where contact with humans and other domestic dogs is rare. Under New South Wales state policy in parks, reserves and other areas not used by agriculture, these populations are only to be controlled when they pose a threat to the survival of other native species. The introduction of "dog-free" buffer zones around areas with pure dingoes is regarded as a realistic method to stop interbreeding. This is enforced in the way that all wild dogs can be killed outside of the conservation areas. However, studies from the year 2007 indicate that even an intensive control of core areas is probably not able to stop the process of interbreeding.
According to the Dingo Discovery Sanctuary and Research Centre, many studies are finding a case for the re-introduction of the dingo into previously occupied areas in order to return some balance to badly degraded areas as a result of "unregulated and ignorant farming practices".
Interbreeding with domestic dogsEdit
European domestic dogs first arrived in Australia during the European colonisation. These dogs reverted to the wild (both unintentionally and intentionally), produced feral populations and interbred with the existing dingoes. Hybrids of dingoes and domestic dogs exist today in all wild dog populations of Australia, with their numbers having increased to such a degree that any completely "pure" populations may no longer exist.
Dingo-like domestic dogs and dingo-hybrids can be generally distinguished from "pure" dingoes by their fur colour, since there is a wider range of colours and patterns among them than among dingoes. In addition, the more dog-typical kind of barking exists among the hybrids, and differences in the breeding cycle, certain skull characteristics, and genetic analyses can be used for differentiation. Despite all the characteristics that can be used for distinguishing between dingoes and other domestic dogs, there are two problems that should not be underestimated. First, there is no real clarity regarding at what point a dog is regarded as a "pure" dingo, and, secondly, no distinguishing feature is completely reliable—it is not known which characteristics permanently remain under the conditions of natural selection.
There are two main opinions regarding this process of interbreeding. The first, and likely most common, position states that the "pure" dingo should be preserved via strong controls of the wild dog populations, and only "pure" or "nearly-pure" dingoes should be protected. The second position is relatively new and is of the opinion that people must accept that the dingo has changed and that it is impossible to bring the "pure" dingo back. Conservation of these dogs should therefore be based on where and how they live, as well as their cultural and ecological role, instead of concentrating on precise definitions or concerns about "genetic purity". Both positions are controversially discussed.
Due to this interbreeding, there is a wider range of fur colours, skull shapes and body size in the modern-day wild dog population than in the time before the arrival of the Europeans. Over the course of the last 40 years,[when?] there has been an increase of about 20% in the average wild dog body size. It is currently unknown whether, in the case of the disappearance of "pure" dingoes, remaining hybrids would alter the predation pressure on other animals. It is also unclear what kind of role these hybrids would play in the Australian ecosystems. However, it is unlikely that the dynamics of the various ecosystems will be excessively disturbed by this process.
In 2011, a total of 3,941 samples were included in the first continent-wide DNA study of wild dogs. The study found that 46% were pure dingoes which exhibited no dog alleles (gene expressions). There was evidence of hybridisation in every region sampled. In Central Australia only 13% were hybrids, however in southeastern Australia 99% were hybrids or feral dogs. Pure dingo distribution was 88% in the Northern Territory, intermediate numbers in Western Australia, South Australia and Queensland, and 1% in New South Wales and Victoria. Almost all wild dogs showed some dingo ancestry, with only 3% of dogs showing less than 80% dingo ancestry. This indicates that domestic dogs have a low survival rate in the wild or that most hybridisation is the result of roaming dogs that return to their owners. No populations of feral dogs have been found in Australia.
In 2016, a three dimensional geometric morphometric analysis of the skulls of dingoes, dogs and their hybrids found that dingo-dog hybrids exhibit morphology closer to the dingo than to the parent group dog. Hybridisation did not push the unique Canis dingo cranial morphology towards the wolf phenotype, therefore hybrids cannot be distinguished from dingoes based on cranial measures. The study suggests that the wild dingo morphology is dominant when compared with the recessive dog breed morphology, and concludes that although hybridisation introduces dog DNA into the dingo population, the native cranial morphology remains resistant to change.
As a petEdit
In 1976, the Australian Native Dog Training Society of NSW Ltd. was founded but has now ceased. In 1994, the Australian National Kennel Council recognised a dingo breed standard within its Hounds group. The dingo is not recognised as a dog breed by the Fédération Cynologique Internationale.
In 2017, a study explored whether dingoes and primitive dog breeds might exhibit less desirable traits than the more recently derived breeds through a survey of their owners. The study found that both modern and ancient breeds were easier to train than the dingo, showed less staring behavior, and were less likely to roll in animal dung than the dingo. The "staring at nothing" behavior was thought to be a reaction to high frequency sounds that humans and some domestic dogs cannot hear. Modern breeds showed less fear of strangers, were less likely to escape, and urinated against objects less than the dingo. Dingo behavior was outside the range of typical dog behaviors, which indicates that dingoes behave like true wild canids and are behaviorally distinct from modern domesticated dogs. The study concluded that these behaviors might be undesirable to the humans living with dingoes and therefore these behaviors reflect natural selection pressures rather than human selection. Some writers disagree that the dingo should be considered as a dog breed because they believe "true" dingoes can be tamed but not truly domesticated.
Dingoes can be very tame when they come in frequent contact with humans. Furthermore, some dingoes live with humans (due to practical, as well as emotional reasons). Many indigenous Australians and early European settlers lived alongside dingoes. Indigenous Australians would take dingo pups from the den and tame them until sexual maturity and the dogs would leave. Alfred Brehm reported cases where dingoes were completely tame and, in some cases, behaved exactly like other domestic dogs (one was used for shepherding heavy livestock), as well as specimens that remained wild and shy. He also reported about dingoes that were aggressive and completely uncontrollable, but he was of the opinion that these reports "should not get more attention than they deserve," since the behaviour depends on how the dingo was raised since early puppyhood. He believed that these dogs could become very decent pets.
According to the Austrian behavioral researcher and author Eberhard Trumler, dingoes are very smart and affectionate. To would-be owners, he recommended the provision of a large escape-proof enclosure and a partner of the opposite sex. During heat, dingoes are harder to manage than other domestic dogs which, combined with their attachment to their owners, can lead to problems, since they want to follow their owners and never miss the opportunity to feed. Dingoes are supposed[who?] to find every weak spot of an enclosure or residence, escape for a while and stray through towns and villages. Their intellectual ability is supposedly[who?] connected to an enormous ability to learn and a lightning perception. Dingoes have a reputation for not handling pressure, but this conflicts with their record as working dogs. They are suitable as shepherd dogs, appearing to see a purpose in it (keeping together a familiar group is in their nature) and, even today, some dingoes are employed as shepherd dogs. In addition, dingoes have strong toileting instincts and can easily be housebroken.
The ownership of dingoes as pets and their breeding is widely criticised. The main criticism is that the activities and the resulting consequences of the dingo conservation groups, "dingo farms" and legislation for legal ownership of dingoes for people in public, is seen to be an additional threat to the survival of the pure dingoes. This fear exists because the majority of these breeding activities effectively expedite the interbreeding of dingoes and other domestic dogs, when the identification of a pure dingo is not absolutely correct respectively when hybrids are sold as "pure" dingoes.[clarification needed]
Supporters of breeding programmes are only mildly optimistic about a successful outcome. Success in the form of a population viable for future re-wilding cannot be easily accomplished. According to David Jenkins,[who?] the breeding and reintroduction of pure dingoes is no easy option and, at the time[when?], there were no studies that seriously dealt with this topic, especially in areas where dingo populations are already present.
An additional threat is that breeders may unconsciously select tamer dingoes by breeding individuals who are easier to manage. Therefore, it may happen that, over the years, the tame populations may become less suitable for living in the wild than their ancestors. In addition, a loss of genetic diversity (thus resulting in a higher susceptibility to diseases) might occur due to a small founding population, and negative changes could occur simply because the dogs were captive-bred. Furthermore, some features that are necessary for survival in the wild might "fade" under the conditions of domestication (for example, hunting techniques) because they are no longer needed.
Dingo pets are likely to escape into the wild.
Problems in classificationEdit
There is no general agreement (scientific or otherwise) regarding what the dingo is, in a biological sense, since it has been called "wolf," "dingo," "dog," and "wild dog". Dingoes have been described by various authors to be wild dogs, the progenitor of domestic dogs, a link between wolf and domestic dog, a primitive canine species, a primitive domestic dog, and a relatively unchanged form of early domestic dog. Some authors do not consider dingoes to be feral but completely wild since they have been living under natural selection for a number of generations. Compared to the European grey wolf, dingoes have an approximately 30% lower relative brain size, reduced facial expressions, reduced impressive behaviour, and generally a permanent fertility in males—features that all known domestic dogs share and are considered to be caused by domestication.
- The addition of [domestic dog] against dingo and familiaris is inferred to mean that these two taxons form the "domestic dog clade" within Canis lupus, as opposed to its wild "wolf clade".
- Greig, K; Walter, R; Matisoo-Smith, L (2016). "21–Dogs and People in South East Asia and the Pacific". In Marc Oxenham, Hallie Buckley. The Routledge Handbook of Bioarchaeology in Southeast Asia and the Pacific Islands. Routledge, Oxford UK. pp. 471–475. ISBN 9781138778184.
- Jackson, Stephen; Groves, Colin (2015). Taxonomy of Australian Mammals. CSIRO Publishing, Clayton, Victoria, Australia. pp. 287–290. ISBN 9781486300136.
- Corbett, L.K. (2008). "Canis lupus ssp. dingo". IUCN Red List of Threatened Species. Version 2012.2. International Union for Conservation of Nature. Retrieved 1 July 2012.
- Fleming et al. 2001, pp. 1–16
- Meyer, F.A.A. (1793). Systematisch-summarische Uebersicht der neuesten zoologischen Entdeckungen in Neuholland und Afrika: nebst zwey andern zoologischen Abhandlungen. Dykischen,Leipzig. pp. 33–35. refer page 34. Quote: "Man weiß nicht, ob er die einzige Hundeart in Neusüdwales ist, und ob er auch noch wild sich vorfindet, indeß scheint er bis jetzt noch wenig von seinem wilden Zustande verloren zu haben; auch hat man noch keine Abarten von ihm entdeckt." Translation: "It is not known if it is the only dog species in New South Wales, and if it can also still be found in the wild state; however, so far it appears to have lost little of its wild condition; moreover, no divergent varieties have been discovered"
- Handbuch der Naturgeschichte. Blumenbach, J.F. 1799. Sechste Auflage. Johann Christian Dieterich, Göttingen. Edition 6. [ref page 100, under Canis, under familiaris, under Dingo. Translation: "Dingo. The New Holland dog. Is similar, especially in the head and shoulders, as a fox.]
- Jackson, Stephen M.; Groves, Colin P.; Fleming, Peter J.S.; Aplin, KEN P.; Eldridge, Mark D.B.; Gonzalez, Antonio; Helgen, Kristofer M. (2017). "The Wayward Dog: Is the Australian native dog or Dingo a distinct species?". Zootaxa. 4317 (2): 201. doi:10.11646/zootaxa.4317.2.1.
- "Species Canis familiaris Linnaeus, 1758 - Common Dog, Dingo, Domestic Dog". Australian Faunal Directory. Australian Government: Dept of Environment & Energy. 15 December 2017. Retrieved 6 May 2018.
- Benga, Gheorghe; Chapman, Bogdan E; Matei, Horea; Cox, Guy C; Romeo, Tony; Mironescu, Eugen; Kuchel, Philip W (2010). "Comparative NMR studies of diffusional water permeability of red blood cells from different species: XVI Dingo (Canis familiaris dingo) and dog (Canis familiaris)". Cell Biology International. 34 (4): 373. doi:10.1042/CBI20090006. PMID 19947930.
- Wozencraft, W.C. (2005). "Order Carnivora". In Wilson, D.E.; Reeder, D.M. Mammal Species of the World: A Taxonomic and Geographic Reference (3rd ed.). Johns Hopkins University Press. pp. 575–577. ISBN 978-0-8018-8221-0. OCLC 62265494. url=https://books.google.com/books?id=JgAMbNSt8ikC&pg=PA576
- "Canis lupus dingo Meyer, 1793". Catalogue of Life 2018 Checklist. Catalogue of Life. May 2018. Retrieved 8 June 2018.
- Smith 2015, pp. xi–24 Chapter 1 - Bradley Smith
- Tench, W. (1789). "11". A Narrative of the Expedition to Botany Bay (PDF). J. Debrett. Note that page numbers are not used in this journal
- Smith 2015, pp. 55–80 Chapter 3 - Bradley Smith & Peter Savolainen
- Purcell 2010, pp. 15–40
- Crowther, M. S.; M. Fillios; N. Colman; M. Letnic (2014). "An updated description of the Australian dingo (Canis dingo Meyer, 1793)". Journal of Zoology. 293 (3): 192–203. doi:10.1111/jzo.12134.
- Smith 2015, pp. 49
- Fan, Zhenxin; Silva, Pedro; Gronau, Ilan; Wang, Shuoguo; Armero, Aitor Serres; Schweizer, Rena M.; Ramirez, Oscar; Pollinger, John; Galaverni, Marco; Ortega Del-Vecchyo, Diego; Du, Lianming; Zhang, Wenping; Zhang, Zhihe; Xing, Jinchuan; Vilà, Carles; Marques-Bonet, Tomas; Godinho, Raquel; Yue, Bisong; Wayne, Robert K. (2016). "Worldwide patterns of genomic variation and admixture in gray wolves". Genome Research. 26 (2): 163–73. doi:10.1101/gr.197517.115. PMID 26680994.
- Koepfli, K.-P.; Pollinger, J.; Godinho, R.; Robinson, J.; Lea, A.; Hendricks, S.; Schweizer, R. M.; Thalmann, O.; Silva, P.; Fan, Z.; Yurchenko, A. A.; Dobrynin, P.; Makunin, A.; Cahill, J. A.; Shapiro, B.; Álvares, F.; Brito, J. C.; Geffen, E.; Leonard, J. A.; Helgen, K. M.; Johnson, W. E.; O’Brien, S. J.; Van Valkenburgh, B.; Wayne, R. K. (2015-08-17). "Genome-wide Evidence Reveals that African and Eurasian Golden Jackals Are Distinct Species". Current Biology. 25 (16): 2158–65. doi:10.1016/j.cub.2015.06.060. PMID 26234211.
- Freedman, Adam H.; Gronau, Ilan; Schweizer, Rena M.; Ortega-Del Vecchyo, Diego; Han, Eunjung; Silva, Pedro M.; Galaverni, Marco; Fan, Zhenxin; Marx, Peter; Lorente-Galdos, Belen; Beale, Holly; Ramirez, Oscar; Hormozdiari, Farhad; Alkan, Can; Vilà, Carles; Squire, Kevin; Geffen, Eli; Kusak, Josip; Boyko, Adam R.; Parker, Heidi G.; Lee, Clarence; Tadigotla, Vasisht; Siepel, Adam; Bustamante, Carlos D.; Harkins, Timothy T.; Nelson, Stanley F.; Ostrander, Elaine A.; Marques-Bonet, Tomas; Wayne, Robert K.; et al. (2014). "Genome Sequencing Highlights the Dynamic Early History of Dogs". PLoS Genetics. 10 (1): e1004016. doi:10.1371/journal.pgen.1004016. PMC . PMID 24453982.
- Cairns, Kylie M.; Wilton, Alan N. (2016). "New insights on the history of canids in Oceania based on mitochondrial and nuclear data". Genetica. 144 (5): 553. doi:10.1007/s10709-016-9924-z. PMID 27640201.
- Clutton-Brock, Juliet (2015). "Chapter 9. Naming the scale of nature". In Alison M Behie and Marc F Oxenham. Taxonomic Tapestries: The Threads of Evolutionary, Behavioural and Conservation Research (PDF). ANU Press, The Australian National University, Canberra, Australia. pp. 171–182.
- Cairns, Kylie M; Brown, Sarah K; Sacks, Benjamin N; Ballard, J. William O (2017). "Conservation implications for dingoes from the maternal and paternal genome: Multiple populations, dog introgression, and demography". Ecology and Evolution. 7 (22): 9787. doi:10.1002/ece3.3487. PMID 29188009.
- Smith 2015, pp. 25–54 Chapter 2 - Bradley Smith
- Corbett 1995, pp. 102–123
- Fleming et al. 2001, pp. 17–42
- Jackson 2003, pp. 381–407
- Smith 2015, pp. 103–130 Chapter 5 - Rob Appleby
- Rose 1992, pp. 47–49
- Gunn, R.G; Whear, R.L; Douglas, L.C (2016). "A Dingo Burial from the Arnhem Land Plateau" (PDF). Australian Archaeology. 71: 11. doi:10.1080/03122417.2010.11689380.First published 2010, online 2016
- Simpson, Jane (14 November 2008). "Sydney Language -mb- ~ -m- and dingo — David Nash". Transient Languages & Cultures. The University of Sydney. Retrieved 6 February 2017.
- Corbett, L. K. (2004). "9–Dingo". In Sillero-Zubiri, Claudio; Hoffmann, Michael; Macdonald, David Whyte. Canids: Foxes, Wolves, Jackals, and Dogs:Status Survey and Conservation Action Plan (PDF). IUCN-The World Conservation Union. pp. 223–230. ISBN 2831707862. Retrieved September 18, 2017.
- Ryan, J. S. (1964). "Plotting an Isogloss-The Location and Types of Aboriginal Names for Native Dog in New South Wales". Oceania. 35 (2): 111. doi:10.1002/j.1834-4461.1964.tb00837.x.
- Rose 1992, pp. 176
- Rose 1992, pp. 104
- Walters, Berenice (1995). The company of dingoes : two decades with our native dog. Bargo, N.S.W. : Australian Native Dog Conservation Society. p. 29. ISBN 0646224263.
- The Voyage of Governor Phillip to Botany Bay with an Account of the Establishment of the Colonies of Port Jackson & Norfolk Island. Mazell, P. & Phillip, A. (1789). J: 274–275. Phillip, A. (Ed.). London:Stockdale.
- ICZN (2017). "The Code online (refer Glossary)". International Code of Zoological Nomenclature online. International Commission on Zoological Nomenclature.
- Ireland, Tom (1947). "THE SCIENTIFIC NAME OF THE DINGO". Proc. Roy. Zool. Soc. N.S.W. (1946/1947): 34.
- Dampier, William (1699). "A voyage to New Holland, Chapter 2: South of the line to Brazil - OF THE INHABITANTS THERE, AND GREAT TIDES, THE VEGETABLES AND ANIMALS, ETC". Project Gutenberg. Retrieved 10 February 2017. "...my men saw two or three beasts like hungry wolves, lean like so many skeletons, being nothing but skin and bones..."
- Hauser-Schäublin, B.; Krüger, G. "Cook-Forster Collection: Pacific cultural heritage". National Museum Australia. National Museum Australia. Retrieved 8 May 2018.
- The animal kingdom Kerr, R. (1792). London: J. Murray & R. Faulder. p136
- Francis Hemming, ed. (1957). "Opinion 451". Opinions and Declarations Rendered by the International Commission on Zoological Nomenclature. 15. Order of the International Trust for Zoological Nomenclature. pp. 331–333.
- Official Lists and Indexes of Names in Zoology (PDF). International Commission on Zoological Nomenclature. 2014. p. 225.
- ICZN (2017). "Status of works, names and nomenclatural acts in Official Lists and Indexes" (PDF). International Commission on Zoological Nomenclature. International Commission on Zoological Nomenclature.
- "Opinion 2027". Opinions and Declarations Rendered by the International Commission on Zoological Nomenclature. 60. Order of the International Trust for Zoological Nomenclature. 2003. pp. 81–84.
- Oxenham, M.; Behie, A. (2015). "Chapter 18–The warp and weft: Synthesising our taxonomic tapestry". In Alison M Behie and Marc F Oxenham. Taxonomic Tapestries: The Threads of Evolutionary, Behavioural and Conservation Research (PDF). ANU Press, The Australian National University, Canberra, Australia. p. 375.
- Elledge, Amanda E.; Leung, Luke K.-P.; Allen, LEE R.; Firestone, Karen; Wilton, Alan N. (2006). "Assessing the taxonomic status of dingoes Canis familiaris dingo for conservation". Mammal Review. 36 (2): 142. doi:10.1111/j.1365-2907.2006.00086.x.
- Jones. F. W. (1925). 'The Mammals of South Australia.' Pt. I11 (Government Printer: Adelaide.)
- vonHoldt, Bridgette M.; Driscoll, Carlos A. (2016). "3. Origins of the dog:Genetic insights into dog domestication". In James Serpell. The Domestic Dog: Its Evolution, Behavior and Interactions with People (2 ed.). Cambridge University Press, UK. pp. 22–41. ISBN 978-1-107-02414-4. refer page 31
- Ryan, Lyndall (2012). Tasmanian Aborigines. Allen & Unwin, Sydney. pp. 3–6. ISBN 9781742370682.
- Bourke, R. Michael, ed. (2009). Food and Agriculture in New Guinea. Australian National University E. Press. ISBN 9781921536601.
- Greig, Karen; Boocock, James; Prost, Stefan; Horsburgh, K. Ann; Jacomb, Chris; Walter, Richard; Matisoo-Smith, Elizabeth (2015). "Complete Mitochondrial Genomes of New Zealand's First Dogs". PLoS ONE. 10 (10): e0138536. doi:10.1371/journal.pone.0138536. PMC . PMID 26444283.
- Jane B. Reece, Noel Meyers, Lisa A. Urry, Michael L. Cain, Steven A. Wasserman, Peter V. Minorsky, Robert B. Jackson, Bernard N. Cooke (2015). "26-Phylogeny and the tree of life". Campbell Biology Australian and New Zealand version (10 ed.). Pierson Australia. pp. 561–562. ISBN 9781486007042.
- "Australian Dingo". Australian National Kennel Council. ANKC Pty Ltd. 31 August 2009.
- Milham, Paul; Thompson, Peter (2010). "Relative Antiquity of Human Occupation and Extinct Fauna at Madura Cave, Southeastern Western Australia". Mankind. 10 (3): 175–180. doi:10.1111/j.1835-9310.1976.tb01149.x.Original study was published in Mankind v10 p175-180 in 1976.
- Gollan, K (1984) The Australian Dingo:in the shadow of man. In Vertebrate Geozoography and Evolution in Australasia:Animals in Space and Time (Eds M Archer and G Clayton.) p921-927 Hesperian Press, Perth
- Monash University. "SahulTime". Retrieved 2015-07-22.
- Savolainen, P.; Leitner, T.; Wilton, A. N.; Matisoo-Smith, E.; Lundeberg, J. (2004). "A detailed picture of the origin of the Australian dingo, obtained from the study of mitochondrial DNA". Proceedings of the National Academy of Sciences. 101 (33): 12387–12390. Bibcode:2004PNAS..10112387S. doi:10.1073/pnas.0401814101. PMC . PMID 15299143.
- Cox, C. B.; Moore, Peter D.; Ladle, Richard (2016). Biogeography: An Ecological and Evolutionary Approach. Wiley-Blackwell. p. 106. ISBN 978-1-118-96858-1.
- Editorial Board (2012). Concise Dictionary of Science. New Delhi: V&S Publishers. p. 137. ISBN 978-93-81588-64-2.
- Oskarsson, M. C. R.; Klutsch, C. F. C.; Boonyaprakob, U.; Wilton, A.; Tanabe, Y.; Savolainen, P. (2011). "Mitochondrial DNA data indicate an introduction through Mainland Southeast Asia for Australian dingoes and Polynesian domestic dogs". Proceedings of the Royal Society B: Biological Sciences. 279 (1730): 967–974. doi:10.1098/rspb.2011.1395. PMC . PMID 21900326.
- Pang, J.-F.; Kluetsch, C.; Zou, X.-J.; Zhang, A.-b.; Luo, L.-Y.; Angleby, H.; Ardalan, A.; Ekstrom, C.; Skollermo, A.; Lundeberg, J.; Matsumura, S.; Leitner, T.; Zhang, Y.-P.; Savolainen, P. (2009). "MtDNA Data Indicate a Single Origin for Dogs South of Yangtze River, Less Than 16,300 Years Ago, from Numerous Wolves". Molecular Biology and Evolution. 26 (12): 2849–64. doi:10.1093/molbev/msp195. PMC . PMID 19723671.
- Thalmann, O.; Shapiro, B.; Cui, P.; Schuenemann, V. J.; Sawyer, S. K.; Greenfield, D. L.; Germonpre, M. B.; Sablin, M. V.; Lopez-Giraldez, F.; Domingo-Roura, X.; Napierala, H.; Uerpmann, H.-P.; Loponte, D. M.; Acosta, A. A.; Giemsch, L.; Schmitz, R. W.; Worthington, B.; Buikstra, J. E.; Druzhkova, A.; Graphodatsky, A. S.; Ovodov, N. D.; Wahlberg, N.; Freedman, A. H.; Schweizer, R. M.; Koepfli, K.- P.; Leonard, J. A.; Meyer, M.; Krause, J.; Paabo, S.; et al. (2013). "Complete Mitochondrial Genomes of Ancient Canids Suggest a European Origin of Domestic Dogs". Science. 342 (6160): 871–4. Bibcode:2013Sci...342..871T. doi:10.1126/science.1243650. PMID 24233726.
- Vila, C. (1997). "Multiple and ancient origins of the domestic dog". Science. 276 (5319): 1687–9. doi:10.1126/science.276.5319.1687. PMID 9180076.
- Ardalan, Arman; Oskarsson, Mattias; Natanaelsson, Christian; Wilton, Alan N.; Ahmadian, Afshin; Savolainen, Peter (2012). "Narrow genetic basis for the Australian dingo confirmed through analysis of paternal ancestry". Genetica. 140 (1–3): 65–73. doi:10.1007/s10709-012-9658-5. PMC . PMID 22618967.
- Sacks, B. N.; Brown, S. K.; Stephens, D.; Pedersen, N. C.; Wu, J.-T.; Berry, O. (2013). "Y Chromosome Analysis of Dingoes and Southeast Asian Village Dogs Suggests a Neolithic Continental Expansion from Southeast Asia Followed by Multiple Austronesian Dispersals" (PDF). Molecular Biology and Evolution. 30 (5): 1103–18. doi:10.1093/molbev/mst027. PMID 23408799.
- Corbett 1995, pp. 29–48
- Clutton-Brock, Juliet; Corbet, Gordon B; Hills, Michael (1976). "A review of the family Canidae, with a classification by numerical methods". Bulletin of the British Museum (Natural History). 29: 117. doi:10.5962/bhl.part.6922.
- Cairns, A; Wilton, A.; Ballard, W. (2011). "The Identification of Dingoes in a Background of Hybrids". Advances in Genetics Research. Nova Science Publishers. 6: 309–327.
- Wayne, R. & Ostrander, Elaine A. (1999). "Origin, genetic diversity, and genome structure of the domestic dog". BioEssays. 21 (3): 247–57. doi:10.1002/(SICI)1521-1878(199903)21:3<247::AID-BIES9>3.0.CO;2-Z. PMID 10333734.
- "A Management Program For The Dingo (Canis lupus dingo) in the Northern Territory Of Australia 2006—2011" (PDF). www.Phthiraptera.info. Parks and Wildlife Service of the Northern Territory. Retrieved 28 November 2017.
- Purcell 2010, pp. 7–14
- Corbett 1995, pp. 26
- Corbett 1995, pp. 183–186
- Allen, B. (2012). "Do desert dingoes drink daily? Visitation rates at remote waterpoints in the Strzelecki Desert". Australian Mammalogy. 34 (2): 251. doi:10.1071/AM12012.
- Fleming et al. 2001, pp. 83–110
- Thomson, PC (1992). "The behavioural ecology of dingoes in north-western Australia. III. Hunting and Feeding behaviour, and diet". Wildlife Research. 19 (5): 531–41. doi:10.1071/WR9920531.
- Feddersen-Petersen, Dorit Urd (2008). Ausdrucksverhalten beim Hund (in German). Stuttgart: Franckh-Kosmos Verlags-GmbH & Co. KG. ISBN 978-3-440-09863-9.
- Schassburger, R.M. (1987). "Wolf vocalization: An integrated model of structure, motivation, and ontogeny". In H. Frank. Man and Wolf. Dordrecht, the Netherlands: Dr. W. Junk.
- Corbett, Laurie (2004). "Dingo". In Claudio Sillero-Zubiri; Michael Hoffmann; David W. Macdonald. Canids: Foxes, Wolves, Jackals and Dogs (PDF). International Union for Conservation of Nature and Natural Resources.
- Brehms Tierleben (in German). Leipzig, Wien: Bibliographisches Institut. 1900. pp. 82–85.
- Corbett 1995, pp. 58–79
- Fleming, Peter; Laurie Corbett; Robert Harden; Peter Thomson (2001). Managing the Impacts of Dingoes and Other Wild Dogs. Commonwealth of Australia: Bureau of Rural Sciences.
- Ortolani, A., Corbett, L.K., Feinstein, F.H., and R.P. Coppinger. 2001. "A comparative study of larynx anatomy and howling vocalizations in five canids," poster presented at Canid Biology and Conservation Conference, Oxford University, Oxford, UK.
- Young, Emma (5 March 2010). "Dingoes skilled at Reading Human Gestures". Australian Geographic. Retrieved 13 January 2013.
- Harden, RH (1985). "The Ecology of the Dingo in North-Eastern New South Wales I. Movements and Home Range". Wildlife Research. 12: 25–37. doi:10.1071/WR9850025.
- Thomson, PC (1992). "The behavioural ecology of dingoes in north-western Australia. II. Activity patterns, breeding season and pup rearing". Wildlife Research. 19 (5): 519–29. doi:10.1071/WR9920519.
- "South East Queensland's urban wild dog project". Beefy and the Beast Issue 15. Department of Natural Resources and Water. September 2006. p. 6. Retrieved 8 April 2009.
- Macdonald, David W, ed. (2006). "Other Dogs". The Princeton Encyclopedia of Mammals. Princeton, NJ: Princeton University Press. p. 619.
- Burnie, David; Wilson, Don E, eds. (2001). Animal: The Definitive Visual Guide to the World's Wildlife. New York: DK Publishing. p. 185. ISBN 0-7894-7764-5.
- Jackson, Stephen (2003). Australian Mammals: Biology and Captive Management. Collingwood, Victoria: CSIRO Publishing. ISBN 0-643-06635-7.
- Thomson, PC (1992). "The behavioural ecology of dingoes in north-western Australia. IV. Social and spatial organisation, and movements". Wildlife Research. 19 (5): 543–63. doi:10.1071/WR9920543.
- Macpherson, Calum N. L.; et al., eds. (2000). Dogs, Zoonoses, and Public Health. Wallingford: CABI Publishing. p. 31. ISBN 0-85199-436-9.
- Miklósi, Ádám (2007). Dog Behaviour, Evolution, and Cognition. New York: Oxford University Press. p. 89. ISBN 978-0199545667.
- Trummler, Eberhard; Dietmar Mundo (1984). Das Jahr des Hundes – Ein Jahr im Leben einer Hundefamilie (in German) (1st ed.). Nerdlen: Kynos Verlag. ISBN 3-924008-11-6.
- Jones, E; Stevens, PL (1988). "Reproduction in Wild Canids, Canis-Familiaris, From the Eastern Highlands of Victoria". Wildlife Research. 15 (4): 385–97. doi:10.1071/WR9880385.
- Catling, PC (1979). "Seasonal variation in plasma testosterone and the testis in captive male dingoes, Canis familiaries dingo". Australian Journal of Zoology. 27 (6): 939–44. doi:10.1071/ZO9790939.
- Parks & Wildlife Service. "A Management Program for the Dingo (Canis lupus dingo) in the Northern Territory of Australia, 2006–2011" (PDF). Department of Natural Resources. Archived from the original (PDF) on 2008-09-13. Retrieved 4 May 2009.
- Moffitt, Ian (1984). Der Australische Busch (in German) (5th ed.). Amsterdam: Time-Life Books. ISBN 90-6182-070-0.
- A.W. Hogstrom (1986). "A changing approach to Dingo control in Western Australia – Proceedings of the Twelfth Vertebrate Pest Conference". University of Nebraska. Retrieved 8 May 2009.
- MacDonald, Fiona; AAP (9 September 2013). "Dingoes cleared of mainland extinctions". Australian geographic. Nine MSN. Retrieved 2 March 2014.
- Short, J; Kinnear, J.E.; Robley, Alan (2002). "Surplus killing by introduced predators in Australia—evidence for ineffective anti-predator adaptations in native prey species?". Biological Conservation. 103 (3): 283–301. doi:10.1016/S0006-3207(01)00139-2.
- Wroe, S.; Clausen, P.; McHenry, C.; Moreno, K.; Cunningham, E. (2007). "Computer simulation of feeding behaviour in the thylacine and dingo as a novel test for convergence and niche overlap". Proceedings of the Royal Society B. 274 (1627): 2819–28. doi:10.1098/rspb.2007.0906. PMC . PMID 17785272.
- Johnson, C. N.; S. Wroe (2003). "Causes of extinction of vertebrates during the Holocene of mainland Australia: arrival of the dingo, or human impact?" (PDF). The Holocene. 13 (6): 1009–1016. Bibcode:2003Holoc..13..941J. doi:10.1191/0959683603hl682fa.
- "Breeding Lethal Weapons of Mass Destruction Sanctioned". Save Our Snowy. Retrieved 9 May 2009.
- Letnic M,Baker L, Nesbitt B, 2013. "Ecologically functional landscapes and the role of dingoes as trophic regulators in south-eastern Australia and other habitats". Ecological Management and Restoration, Vol 14(2) 1-5.
- Corbett, L (1995). "Does Dingo Predation or Buffalo Competition Regulate Feral Pig Populations in the Australian Wet-Dry Tropics? An Experimental Study". Wildlife Research. 22: 65–74. doi:10.1071/WR9950065.
- Claridge, Andrew W.; Hunt, Rob (2008). "Evaluating the role of the dingo as a trophic regulator in Australian ecosystems". Ecological Management & Restoration. 9 (2): 116. doi:10.1111/j.1442-8903.2008.00402.x.
- Mitchell, Bruce D.; Banks, Peter B. (2005). "Do wild dogs exclude foxes? Evidence for competition from dietary and spatial overlaps". Austral Ecology. 30 (5): 581–91. doi:10.1111/j.1442-9993.2005.01473.x.
- "Scientists probe dingo's ecological role". heraldsun.com.au. 28 January 2013. Retrieved 2 February 2013.
- Pople, A. R.; Grigg, G. C.; Cairns, S. C.; Beard, L. A.; Alexander, P. (2000). "Trends in the numbers of red kangaroos and emus on either side of the South Australian dingo fence: evidence for predator regulation?". Wildlife Research. 27 (3): 269–76. doi:10.1071/WR99030.
- Williams, Brian (5 April 2013). "Stuff the turkeys, dingoes need a break". The Courier-Mail. Retrieved 5 April 2013.
- Trigger, D; Mulcock, J; Gaynor, A; Toussaint, Y (2008). "Ecological restoration, cultural preferences and the negotiation of 'nativeness' in Australia". Geoforum. 39 (3): 1273–83. doi:10.1016/j.geoforum.2007.05.010.
- Parker, Merryl (2007). "The Cunning Dingo" (PDF). Animals & Society Institute. Archived from the original (PDF) on 27 July 2011. Retrieved 9 May 2009.
- Wild 'superdogs' may attack people, farmers warn Shanghai Star. Shanghai Star. 27 June 2002. Archived from the original on 11 June 2011. Retrieved 9 May 2009.
- Williams, Robyn; Corbett, Laurie; Jenkins, David; et al. (23 June 2001). "The Dingo in Australia". The Science Show. Archived from the original on 2002-02-12. Retrieved 8 May 2009.
- Merryl Ann Parker (April 2006). "Bringing the dingo home: discursive representations of the dingo by aboriginal, colonial and contemporary Australians" (PDF). UTAS ePrints. Retrieved 9 May 2009.
- Howard, Peter (22 November 2006). "The beast within – an exploration on Australian constructions of wildlife – PhD thesis, Griffith University, Australia" (PDF). Australian Digital Theses Program. Retrieved 9 May 2009.
- "Western Australian Wild Dog Management Strategy 2005" (PDF). August 2005. Archived from the original (PDF) on 1 September 2008. Retrieved 9 May 2009.
- Allen, L.R.; Fleming, P.J.S. (2004). "Review of Canid Management in Australia for the Protection of Livestock and Wildlife – Potential Application to Coyote Management". Sheep & Goat Research Journal. 19: 97.
- "Dingo expert says it's better for the environment to let them live". Retrieved 9 August 2015.
- Miles, Aden (7 June 2013). "Dingo 'epidemic' on farm". Stuff. Retrieved 11 June 2013.
- "Animals – Dingo Wild Dog (canis lupus familiaris, canis lupus dingo and hybrids)". Northern Territory Government. Archived from the original on 9 March 2009. Retrieved 9 May 2009.
- Lawrance, Kate; Higginbottom, Karen (2002). "Behavioural Responses of Dingoes to Tourist on Fraser Island" (PDF). Sustainable Tourism Cooperative Research Centre. Retrieved 3 May 2009.
- Rachel Nowak (26 June 2008). "At last, a use for dingo urine". New Scientist. Retrieved 9 May 2009.
- Australian Government, Department of the Environment (1 June 2015). "National parks". Australia.gov.au. Australian Government. Retrieved 18 August 2017.
- Government of Western Australia, Department of Primary Industries and Regional Development (1 August 2017). "Wild dogs in Western Australia". www.agric.gov.wa. Government of Western Australia. Retrieved 18 August 2017.
- "Wild dogs/dingo Canis familiaris/Canis familiaris (dingo)" (PDF). Queensland Government. September 2002. Archived from the original (PDF) on 31 May 2009. Retrieved 13 May 2009.
- "Pest of the past, dingo's star in the ascendancy". The Age. Melbourne. 22 July 2007. Retrieved 16 May 2009.
- Edited by Ian Keen. Indigenous participation in Australian economies: Historical and anthropological perspectives. ANU E Press. pp. 91–. ISBN 978-1-921666-86-5. Retrieved 29 March 2012.
- "Ejector research update" (PDF). Beefy and the Beast Issue 11. Department of Natural Resources and Mines. August 2003. Archived from the original (PDF) on 20 February 2010. Retrieved 13 May 2009.
- "Livestock protection collars to be tested in Queensland" (PDF). Beefy and the Beast Issue 12. Department of Natural Resources and Mines. April 2004. Archived from the original (PDF) on 20 February 2010. Retrieved 13 May 2009.
- Allen, L. R.; Sparkes, E. C. (2001). "The Effect of Dingo Control on Sheep and Beef Cattle in Queensland". Journal of Applied Ecology. 38 (1): 76–87. doi:10.1046/j.1365-2664.2001.00569.x. JSTOR 2655734.
- Twigg, Laurie E.; Eldridge, Steve R.; Edwards, Glenn P.; Shakeshaft, Bernie J.; Depreu, Nicki D.; Adams, Neville (2000). "The longevity and efficacy of 1080 meat baits used for dingo control in central Australia". Wildlife Research. 27 (5): 473–81. doi:10.1071/WR99044.
- Benjamin, Allen (April 13, 2015). "Culling is no danger to the future of dingoes on Fraser Island". theconversation.com. Retrieved April 27, 2015.
- O'Neill, Adam J; Cairns, Kylie M; Kaplan, Gisela; Healy, Ernest (2017). "Managing dingoes on Fraser Island: Culling, conflict, and an alternative". Pacific Conservation Biology. 23: 4. doi:10.1071/PC16026.
- "Dingo sanctuary considered for Fraser Island". The New Zealand Herald. 27 February 2013. Retrieved 27 February 2013.
- Newby, Jonica (31 March 2005). "Last Of The Dingoes". ABC. Retrieved 8 May 2009.
- Woodall, PF; Pavlov, P; Twyford, KL (1996). "Dingoes in Queensland, Australia: skull dimensions and the indenity of wild canids". Wildlife Research. 23 (5): 581–7. doi:10.1071/WR9960581.
- Brown, Carmen (4 June 2013). "Tanami dingoes among purest in Australia". ABC Rural. Retrieved 6 June 2013.
- "Predation and Hybridisation by Feral Dogs (Canis lupus familiaris) – proposed key threatening process listing". New South Wales Government. 29 August 2008. Retrieved 13 May 2009.
- Centre, Dingo Discovery Research. "Dingo Discovery Research Centre". www.dingofoundation.org. Retrieved 2018-05-31.
- Corbett 1995, pp. 166
- Catling, PC; Corbett, LK; Newsome, AE (1992). "Reproduction in captive and wild dingoes (Canis familiaris dingo) in temperate and arid environments of Australia". Wildlife Research. 19 (2): 195–209. doi:10.1071/WR9920195.
- Newsome, AE; Corbett, LK; Carpenter, SM (1980). "The Identity of the Dingo I. Morphological Discriminants of Dingo and Dog Skulls". Australian Journal of Zoology. 28 (4): 615–25. doi:10.1071/ZO9800615.
- Wilton, Alan. "Genetic Diversity in the Dingo". dingosanctuary. Archived from the original on 2004-02-19. Retrieved 14 May 2009.
- Brad Purcell; Robert Mulley; Robert Close (2008). "Genetic characterisation of dingoes in the Blue Mountains world heritage area" (PDF). 14th Australasian Vertebrate Pest Conference. Darwin: Invasive Animals CRC. p. 140. Archived from the original (PDF) on 24 April 2009. Retrieved 13 May 2009.
- "A Draft Dingo Management Strategy for Fraser Island". Fraser Island Defenders Organization. Retrieved 14 May 2009.
- Daniels, Mike J.; Corbett, Laurie (2003). "Redefining introgressed protected mammals: when is a wildcat a wild cat and a dingo a wild dog?". Wildlife Research. 30 (3): 213–8. doi:10.1071/WR02045.
- Spencer, Ricky-John; Lapidge, Steven J.; Dall, David; Humphrys, Simon (10–13 June 2008). "Bringing out the Mongrel in Australian Dingoes: The Evolution of Wild Dog Body Size" (PDF). 14th Australasian Vertebrate Pest Conference. Inavisive Animals CRC. p. 149. Archived from the original (PDF) on 2009-01-16. Retrieved 10 April 2009.
- Stephens, D. (2011). "The molecular ecology of Australian wild dogs: hybridization, gene flow and genetic structure at multiple geographic scales". Ph.D. thesis. University of Western Australia.
- Parr, William C. H; Wilson, Laura A. B; Wroe, Stephen; Colman, Nicholas J; Crowther, Mathew S; Letnic, Mike (2016). "Cranial Shape and the Modularity of Hybridization in Dingoes and Dogs; Hybridization Does Not Spell the End for Native Morphology". Evolutionary Biology. 43 (2): 171. doi:10.1007/s11692-016-9371-x.
- Smith, Bradley P.; Browne, Matthew; Serpell, James A. (2017). "Owner-reported behavioural characteristics of dingoes (Canis dingo) living as companion animals: A comparison to 'modern' and 'ancient' dog breeds". Applied Animal Behaviour Science. 187: 77. doi:10.1016/j.applanim.2016.11.010.
- Coppinger, Raymond and Lorna (2001). Dogs: A Startling New Understanding of Canine Origin, Behavior, & Evolution. New York: Scribner. pp. 45, 67. ISBN 0-684-85530-5.
- "Why the dingo should be allowed to have its day". The Canberra Times. 11 April 2009. Retrieved 14 May 2009.[dead link]
- Beeby, Rosslyn (7 February 2007). "Genetic dilution dogs dingoes". The Canberra Times. Archived from the original on 2009-04-15. Retrieved 14 May 2009.
- "Australia's dingo dogs face extinction". USA Today. 7 October 2003. Retrieved 14 May 2009.
- Günther, Janine; Jens Mohr (2007). Das Northern Territory und weiterführende Routen (in German) (1st ed.). Gamehl: 360°. ISBN 978-3-9809763-2-9.
- "Dingo". Department of Primary Industries, now Department of Agriculture, Fisheries and Forestry (Queensland). Archived from the original on 16 May 2009. Retrieved 15 May 2009.
- Boitani, L.; Ciucci, P. (1995). "Comparative social ecology of feral dogs and wolves" (PDF). Firenze University Press. Retrieved 27 August 2017.
- Hemmer, Helmut (1983). Domestikation, Verarmung der Merkwelt (Domestication: the decline of environmental appreciation) (in German). Braunschweig: Friedr. Vieweg & Sohn Verlagsgesellschaft mbH. ISBN 3-528-08504-5.
- Trumler, Eberhard (1982). Ein Hund wird geboren; Der Ratgeber für den Hundefreund (in German). Muenich: R. Piper GmbH & Co. KG. ISBN 3-492-02775-X.
- Zimen, Erik (1988). Der Hund: Abstammung – Verhalten – Mensch und Hund (in German) (1. ed.). München: Bertelsmann. ISBN 3-570-00507-0.
- Corbett, L. (1995). The Dingo in Australia and Asia. J B Books. ISBN 9781876622305.
- Fleming, P.; Corbett, L.; Harden, R.; Thomson, P. (2001). Managing the impacts of dingoes and other wild dogs. Bureau of Rural Sciences, Canberra. ISBN 0642704945.
- Jackson, S. (2003). "12–Dingo". Australian Mammals: Biology and Captive Management. CSIRO Publishing. pp. 381–407. ISBN 0643066357.
- Purcell, B. (2010). Dingo. CSIRO Publishing. ISBN 9780643096936.
- Rose, D. (1992). Dingo Makes Us Human: Life and Land in an Australian Aboriginal Culture. Cambridge University Press. ISBN 0-521-39269-1.
- Smith, Bradley, ed. (2015). The Dingo Debate: Origins, Behaviour and Conservation. CSIRO Publishing, Melbourne, Australia. ISBN 9781486300303.
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