Observations from aerial radio-tracking were used together with analysis of scat and stomach samples to investigate the feeding ecology of dingoes, Canis familiaris dingo, on the lower Fortescue River in Western Australia. Between 1977 and 1984, 1948 records of hunting and feeding were obtained, and 352 scats and 119 stomachs were collected. Dingoes preyed predominantly on kangaroos, Macropus robustus and M. rufus, the most abundant and widely distributed of the larger native mammals in the area. In one site dingoes partially switched to alternative food (smaller prey and cattle carrion) when kangaroo abundance declined. However, they continued to hunt and kill kangaroos even when easyto- obtain cattle carrion was available. The increased utilisation of smaller prey by dingoes coincided with changes in sociality (disintegration of packs and an increased number of solitary dingoes). In a sheepgrazing area, sheep were 'easy' prey and dingoes killed sheep and kangaroos in excess of their needs for food, although kangaroo remained a major component of their diet. Dingoes cooperating in groups were more successful than solitary dingoes in hunting large prey (kangaroos, calves). Cooperative effort was not required for dingoes to catch or kill sheep.

Dingoes, Canis familiaris dingo, were studied on the lower Fortescue River during a period when minimal natural or artificial disturbances occurred. From 1975 to 1978, 34 radio-collared dingoes were tracked and observed from aircraft for 2-36 months (mean 11 months). Tracking yielded 9179 daytime and 2229 night-time locations. In all, 25% of dingoes sighted were alone, 21% were in pairs, and 54% were in groups of three or more. Most dingoes were members of five discrete packs (mean monthly pack size 3-12 members) that occupied long-term essentially non-overlapping territories. Territory size (44.5-113.2km*2) was not correlated with pack size. Between-pack encounters were extremely rare. Members of packs were most often seen in smaller groups of variable size (mean 2.2, range 1-12); the largest observed groups of pack members were associated with feeding and hunting activities involving large prey. Dingoes were most gregarious during the prebreeding season. Lone dingoes (n = 3) displayed no pack affiliations, occupied large ranges that overlapped the mosaic of pack territories, and avoided encounters with packs. Dingoes utilised some habitats more heavily than others, with activity often being centred on riverine areas. The greatest seasonal influence on movement patterns occurred during the nursing period when breeding females were mostly confined to den areas. Implications for the control of dingoes, including the strategy of confining control work to buffer zones, are discussed.

The effectiveness of a baiting campaign against red foxes (Vulpes vulpes) was investigated in a rangeland area near Carnarvon, Western Australia. An area of 3180 km2 was aerially baited with dried meat baits containing 3 mg 1080 poison (5 baits km–2) in August 1995. All 45 radio-collared foxes monitored in the area were killed by baits. More than half the radio-collared foxes died within 3 days of baits being laid; the last surviving radio-collared fox died 44 days after baits were laid. The overall population reduction was estimated to be >95%. Further implications of this high level of bait uptake are discussed in relation to immunocontraceptive control of foxes, as well as for population reduction or vaccination of foxes to control rabies. Reinvasion of the baited area occurred mainly in autumn, when juvenile foxes were dispersing. The relevance of this result is discussed in relation to developing more effective baiting strategies. As part of another experiment, outer sections of the baited area were periodically re-baited as a buffer zone to reduce immigration by foxes into the central baited area; the buffer baiting proved to be very effective in preventing recolonisation of the entire baited area.

This paper reports aspects of a long-term study (1975-84) of the ecology, social organisation and behaviour of dingoes, Canis familiaris dingo, on the lower Fortescue River in Western Australia. In all, 170 dingoes were fitted with radio-collars and tracked from aircraft. Dingoes were sighted during 59% of the 13 618 occasions that they were being radio-tracked during the day. Radio-tracking yielded 31 229 daytime and 3016 night-time locations of radio-collared dingoes. The average duration of radio contact with 146 dingoes was 9 months (range 1-35 months). Dingoes were most active around sunrise and sunset, moderately active during the night, and least active during the heat of the day. Travelling (local meandering and more purposeful movement) was the most commonly witnessed activity. Levels of scent-marking (raised-leg urination and ground-scratching), howling and general activity increased over the 2-3 months prior to the mating period, suggesting that dingoes may have a long pro-oestrus (1-2 months). Whelping took place from mid-May to mid-August (mean date 18 July). The characteristics of natal dens are described. The pattern of activities associated with pup-rearing, including alloparental behaviour, closely followed that of related canids.

Wild canids (wild dogs and European red foxes) cause substantial losses to Australian livestock industries and environmental values. Both species are actively managed as pests to livestock production. Contemporaneously, the dingo proportion of the wild dog population, being considered native, is protected in areas designated for wildlife conservation. Wild dogs particularly affect sheep and goat production because of the behavioural responses of domestic sheep and goats to attack, and the flexible hunting tactics of wild dogs. Predation of calves, although less common, is now more economically important because of recent changes in commodity prices. Although sometimes affecting lambing and kidding rates, foxes cause fewer problems to livestock producers but have substantial impacts on environmental values, affecting the survival of small to medium-sized native fauna and affecting plant biodiversity by spreading weeds. Canid management in Australia relies heavily on the use of compound 1080-poisoned baits that can be applied aerially or by ground. Exclusion fencing, trapping, shooting, livestock-guarding animals and predator calling with shooting are also used. The new Invasive Animals Cooperative Research Centre has 40 partners representing private and public land managers, universities, and training, research and development organisations. One of the major objectives of the new IACRC is to apply a strategic approach in order to reduce the impacts of wild canids on agricultural and environmental values in Australia by 10%. In this paper, the impacts, ecology and management of wild canids in Australia are briefly reviewed and the first cooperative projects that will address IACRC objectives for improving wild dog management are outlined.