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The Population Ecology of Wild Horses in the Australian Alps

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horses <strong>in</strong> south Kosciuszko and approximately 100 <strong>in</strong> nor<strong>the</strong>rn Kosciuszko. We have no<br />

way <strong>of</strong> know<strong>in</strong>g how accurate <strong>the</strong>se estimates are, but <strong>the</strong>y are much lower than <strong>the</strong><br />

current study and suggest a 3 fold <strong>in</strong>crease <strong>in</strong> <strong>the</strong> population <strong>in</strong> Kosciuszko National<br />

park over 10 years.<br />

<strong>Population</strong> dynamics<br />

<strong>The</strong> options available to managers <strong>of</strong> any wildlife species are<br />

ei<strong>the</strong>r to make <strong>the</strong><br />

population <strong>in</strong>crease, to make it decrease, harvest it for a cont<strong>in</strong>ual yield or leave it alone.<br />

All <strong>of</strong> <strong>the</strong>se options are greatly assisted by an understand<strong>in</strong>g <strong>of</strong> <strong>the</strong> underly<strong>in</strong>g<br />

dynamics <strong>of</strong> <strong>the</strong> population. <strong>Population</strong> dynamics are <strong>the</strong> variations <strong>in</strong> <strong>the</strong> sizes and<br />

densities <strong>of</strong> populations reflect<strong>in</strong>g a change <strong>in</strong> demographic parameters <strong>in</strong>clud<strong>in</strong>g birth<br />

and death rates. Estimation and modell<strong>in</strong>g <strong>of</strong> demographic parameters provides<br />

<strong>in</strong>formation on <strong>the</strong> state <strong>of</strong> <strong>the</strong> population, such as whe<strong>the</strong>r it is likely to be stable,<br />

<strong>in</strong>creas<strong>in</strong>g or decl<strong>in</strong><strong>in</strong>g, and possible causes. <strong>The</strong> aim <strong>of</strong> this section <strong>of</strong> <strong>the</strong> study was to<br />

exam<strong>in</strong>e <strong>the</strong> population dynamics <strong>of</strong> three populations <strong>of</strong> wild horses across <strong>the</strong> <strong>Alps</strong>,<br />

determ<strong>in</strong>e what factors are likely to be limit<strong>in</strong>g <strong>the</strong> populations if any, and assess <strong>the</strong><br />

sensitivity <strong>of</strong> population growth rate to change <strong>in</strong> key demographic parameters (which<br />

can be used to help make decisions on what component <strong>of</strong> <strong>the</strong> population to target if<br />

undertak<strong>in</strong>g control).<br />

Studies on o<strong>the</strong>r wild horses around <strong>the</strong> world give us a good basic understand<strong>in</strong>g <strong>of</strong><br />

typical population dynamics and social organisation <strong>of</strong> wild horses. L<strong>in</strong>klater (2000)<br />

reviewed feral horse populations <strong>in</strong> North America, South America, Europe and<br />

Australasia and found that comparison across different populations showed that horses<br />

had remarkably similar social and spatial organisation and that group sizes (range 1 –<br />

28) and home range size (range 0.8 – 303km 2 ) varied as much between as with<strong>in</strong><br />

populations (L<strong>in</strong>klater 2000). <strong>The</strong> density <strong>of</strong> populations ranged from 0.1 to 35.4 horses<br />

per km 2 , and adult sex ratios varied from 0.03 to 1.85 males per female. Variation <strong>in</strong><br />

densities and sex ratios were <strong>of</strong>ten <strong>the</strong> result <strong>of</strong> management practices such as removal<br />

<strong>of</strong> animals. <strong>The</strong> maximum rate <strong>of</strong> <strong>in</strong>crease observed for any wild horse population to<br />

date is 30% per year (Duncan 1992), however values <strong>of</strong> 21% per year are more common<br />

(Garrott et al. 1991). <strong>Horses</strong> have an annual breed<strong>in</strong>g season with generally 80-90% <strong>of</strong><br />

adult females (over 2 years) produc<strong>in</strong>g one foal each year (Garrott et al. 1991).<br />

Survivorship is high <strong>in</strong> adults with little annual variation and generally lower and more<br />

variable earlier <strong>in</strong> life (Garrott & Taylor 1990).<br />

Variability <strong>in</strong> wild horse population dynamics occurs at different locations due to <strong>the</strong><br />

fact that different limit<strong>in</strong>g factors are operat<strong>in</strong>g on <strong>the</strong> various age and sex classes <strong>of</strong> <strong>the</strong><br />

population. For example, mounta<strong>in</strong> lion predation can drastically reduce juvenile<br />

survival, and food limitation reduces juvenile survival, delays age at first reproduction<br />

and reduces fecundity. Management practices can potentially limit populations by<br />

reduc<strong>in</strong>g fecundity (birth rate) us<strong>in</strong>g fertility control or reduc<strong>in</strong>g survival rates <strong>of</strong> adults<br />

and/or juveniles by cull<strong>in</strong>g.<br />

<strong>The</strong> population dynamics <strong>of</strong> wild horses were studied <strong>in</strong> detail at three sites each spr<strong>in</strong>g<br />

and autumn between spr<strong>in</strong>g 1999 and autumn 2002. <strong>The</strong> sites were Big Boggy near<br />

Mount Kosciuszko <strong>in</strong> central Kosciuszko National Park, Cowombat on <strong>the</strong> border <strong>of</strong><br />

8

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