Monitoring, mapping and safeguarding Kimberley bilbies Go Back

We estimated that bilbies used 21% of the surveyed 2-ha plots in the Fitzroy catchment project area. If a plot was used by a bilby, there was a 49% chance of finding evidence of that use. This result highlights the importance of repeatedly surveying a site to increase the chance of detecting a bilby if it is in the area. These estimates are comparable to the La Grange area west of our study area which has also been identified as a stronghold. We found bilby occupancy was most strongly influenced by cattle occupancy, with areas with lots of cattle less likely to be occupied by bilbies. Overgrazing and trampling by cattle and other introduced herbivores has been implicated as a factor contributing to the decline of bilbies through the degradation of their habitat. Bilbies were also more likely to be detected in open woodland with a higher fire frequency, probably reflecting greater ease of detection in more open habitats.

Mapping the bilby activity area at the Kurlku (Ngurrara) bilby population. Photo: WA DBCA.

Despite a high occupancy rate of feral cats on the survey plots and on cameras, we did not find an association between feral cat and bilby occupancy, suggesting that bilbies are resilient to some level of feral cat presence. Even so, feral cats were observed commonly stationed at burrows occupied by bilbies. We also found no evidence that occupancy of dingoes influenced bilby occupancy, but interestingly, cat occupancy tended to decrease with increasing dingo occupancy.

A concerning finding of our study was the presence of foxes at the three bilby populations where we estimated abundance. We also observed foxes waiting at burrow entrances, sometimes for extended periods. Foxes have been implicated as primarily responsible for the extirpation of bilbies in the southern portion of their former range across Australia, and a single fox can decimate an entire bilby colony. It is generally thought that foxes do not pose a threat in the more tropical northern climates, as they are less prevalent. However, our study suggests otherwise, at least in the southern section of the Fitzroy catchment which is the northern-most extent of the bilby’s range.

Feral cats were recorded by remote cameras stationed at bilby burrows. Photo: WA DBCA.

Foxes were recorded by remote cameras stationed at bilby burrows. Photo: WA DBCA.

We recorded population sizes of 4, 6 and 13 for the three bilby colonies where abundance surveys were completed. Population monitoring over several years in the Kimberley, Pilbara and central desert regions recorded similar populations of 2 to 15 individual bilbies. Monitoring of three populations in the adjacent La Grange area estimated population sizes of 2, 10 and 44 individuals. Based on our models, broad areas of habitat suitable for bilbies were predicted to occur in the southern half of the Fitzroy catchment. This result is probably not surprising given the complex rocky terrain in the north of the catchment is generally not considered suitable for the species.

Based on data from occupancy, density and habitat suitability, we estimated the bilby population within the Fitzroy catchment at 11,806 ± 6,068 individuals, although this is based on a small number of plots sampled across the area and a density estimate derived from just three populations.

Model of bilby habitat suitability, showing that the southern part of the Fitzroy catchment is likely to have more suitable habitat for bilbies.

The widespread presence of threats to bilbies in our study area highlights the need for appropriate management of these threats. A combination of landscape-scale and local management actions will likely provide the most benefit to bilbies. The management area surrounding bilby populations should be large enough to create habitat complexity and accommodate movement of the population within the managed area.

Feral cats and foxes

Baiting programs, coupled with supplementary trapping and traditional hunting, are likely to be effective for controlling feral cats and foxes in and around bilby populations. For example, annual strategic aerial application of the Eradicat® bait has been shown to be effective for controlling feral cats at the landscape scale but it can also be applied locally. Baiting with Eradicat® is also effective for fox control.

Fire management

Recently burnt areas have been shown to be favoured by feral cats, probably because hunting success is improved. Management of both fire and introduced predators at the same time is likely to achieve the best outcome. Intense and large landscape-scale wildfires destroy large areas of habitat that provide food resources and cover from predation. Bilby populations require smaller, more frequent fires that create a mosaic of different age classes of regrowth, which increase habitat and resource diversity. Localised fire management around bilby populations such as fire breaks and patch mosaic burning are recommended.

Introduced herbivores

Due to the transient behaviour of bilbies, fencing off areas is unlikely to be effective. Removal or reducing the number of feral herbivores and unmanaged livestock, or negotiating the closure of artificial water points in the vicinity of bilby populations, are potential management options. 

Land clearing

The negative effects of land clearing are manifested on local and landscape scales. Careful management to ensure sufficient areas of connected suitable habitat remain to support bilby populations is likely to reduce the impacts of land clearing. Securing land specifically for bilby conservation could also be considered.

Nyikina Mangala completing bilby plots and capturing plot data. Photo: Kyle Raina.

Ngurrara ladies point out a fresh bilby burrow while completing occupancy surveys. Photo: WA DBCA.