Feral goats (Capra hircus) were shot from a helicopter on four sites i
n central-western Queensland. These sites centred on Idalia National P
ark (660 km(2)) and three nearby properties: Lissoy (360 km(2)), Mt Ca
lder (260 km(2)) and Ravensbourne (320 km(2)), the order reflecting in
creasing goat density. On Idalia, 134 goats were shot in 8 h of flying
time. On Lissoy, 28 goats were shot in 3 h, 1038 goats were shot on M
t Calder in 15 h, while 2307 goats were shot on Ravensbourne in 21 h.
The reduction was monitored by aerial surveys using fixed-wing aircraf
t. No goats were recorded on either Idalia or Lissoy immediately follo
wing shooting and substantial reductions in goat numbers were achieved
on Mt Calder (75%) and Ravensbourne (49%). Surveys conducted six mont
hs after this reduction indicated population increases on all sites fo
llowing shooting. This was particularly marked on Ravensbourne, where
goat numbers had increased by 31% despite further substantial removals
by commercial mustering. These population increases were largely the
result of immigration. The cooperation of landowners over a large area
is therefore essential for effective control of goats. The per capita
cost of shooting goats from a helicopter was essentially constant dow
n to a threshold density of <1 goat km(-2), below which the cost incre
ased substantially. The accuracy of fixed-wing aerial surveys was impr
oved by using double-counting and these corrected estimates compared f
avourably with index-manipulation-index estimates. Estimates of densit
ies ii goat km(-2) were imprecise and at these densities goats were di
fficult to detect. The extent of vegetation cover did not affect the s
ightability of goats, whereas group size was positively correlated wit
h the sightability of goats. To estimate true density, correction fact
ors of 1-2 were applied to goat group sizes using survey parameters of
100 m strip width, a survey height of 76 m and a speed of 187 km h(-1
).