26.03.2013 Views

Underpinnings of fire management for biodiversity conservation in ...

Underpinnings of fire management for biodiversity conservation in ...

Underpinnings of fire management for biodiversity conservation in ...

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

66<br />

<strong>of</strong> graz<strong>in</strong>g needs to be determ<strong>in</strong>ed with respect to species which contribute the bulk <strong>of</strong> the fuel (‘fuel<br />

species’; Gill 1999a), and at larger scales than <strong>for</strong> relatively rare species. In simple terms, when the<br />

palatable species have been consumed, animals turn their attention to less and less palatable species,<br />

‘when these m<strong>in</strong>or species had been consumed, sheep were <strong>for</strong>ced to eat the dom<strong>in</strong>ant grasses’<br />

(Leigh and Holgate 1978). The <strong>in</strong>tensity or graz<strong>in</strong>g varies with palatability and may be seen to apply at<br />

a po<strong>in</strong>t scale. In Leigh and Holgate’s example, at first the graz<strong>in</strong>g <strong>in</strong>tensity was relatively high <strong>for</strong> the<br />

m<strong>in</strong>or species, but very low <strong>for</strong> the dom<strong>in</strong>ant species.<br />

Interval between graz<strong>in</strong>g events<br />

At the paddock scale, the <strong>in</strong>terval between graz<strong>in</strong>g events can be measured by the tim<strong>in</strong>g <strong>of</strong><br />

livestock additions and removals each year. The <strong>in</strong>terval may be rated as short term or seasonal,<br />

measured <strong>in</strong> days or months. As with Tscharke (2001) – noted by Lunt (2005) – long-term outcomes<br />

are unavailable as yet. The <strong>in</strong>terval <strong>for</strong> an <strong>in</strong>dividual resprout<strong>in</strong>g plant – considered to be at a po<strong>in</strong>t<br />

– may be measured <strong>in</strong> days, weeks, months or years. As with <strong>in</strong>tensity, <strong>in</strong>terval may be determ<strong>in</strong>ed<br />

differently accord<strong>in</strong>g to the purpose <strong>of</strong> the measurement.<br />

If the dom<strong>in</strong>ant species, a fuel species, <strong>of</strong> a natural sward is the most palatable to domestic stock,<br />

while the lesser ranked species are less palatable, then the periodic removal or reduction <strong>of</strong> the<br />

shoots <strong>of</strong> the dom<strong>in</strong>ant may be beneficial <strong>for</strong> <strong>conservation</strong> and fuel m<strong>in</strong>imisation. This may have been<br />

the case with Themeda pastures <strong>in</strong> Victoria where periodic, high-frequency (short-<strong>in</strong>terval) burn<strong>in</strong>g<br />

favours the expression <strong>of</strong> a variety <strong>of</strong> herb species, while not elim<strong>in</strong>at<strong>in</strong>g the dom<strong>in</strong>ant (Lunt and<br />

Morgan 2002). However, the palatability <strong>of</strong> Themeda to domestic stock, probably under cont<strong>in</strong>uous<br />

graz<strong>in</strong>g, may have led to its demise over wide areas, as surmised by Moore (1962) and supported by<br />

subsequent studies, <strong>in</strong>clud<strong>in</strong>g those <strong>of</strong> Fensham (1998) and Allcock and Hik (2004).<br />

The effects on palatable and non-palatable (fuel) species at po<strong>in</strong>t, patch or paddock scales merge<br />

when large numbers <strong>of</strong> animals are imposed on the vegetation <strong>for</strong> short periods. In this case, the<br />

shoots <strong>of</strong> the more palatable plants are quickly removed. The animals then concentrate on the<br />

less palatable materials and may remove them be<strong>for</strong>e the shoots <strong>of</strong> the palatable plants recover<br />

sufficiently to aga<strong>in</strong> be available <strong>for</strong> graz<strong>in</strong>g. It has been argued that this sort <strong>of</strong> treatment would<br />

have the m<strong>in</strong>imum adverse <strong>conservation</strong> effect and maximum fuel-reduction effect, but the resilience<br />

and relative palatabilities <strong>of</strong> the species present <strong>in</strong> any local area would need to be taken <strong>in</strong>to account.<br />

Furthermore, other potential adverse effects associated with the presence <strong>of</strong> the animals would need<br />

to be considered, <strong>in</strong>clud<strong>in</strong>g the creation <strong>of</strong> areas <strong>of</strong> nutrient concentration (‘camps’), exposure <strong>of</strong> the<br />

soil to erosion, r<strong>in</strong>gbark<strong>in</strong>g <strong>of</strong> trees by rubb<strong>in</strong>g, trampl<strong>in</strong>g effects, foul<strong>in</strong>g <strong>of</strong> water bodies and the<br />

promotion <strong>of</strong> unpalatable or highly resilient exotic species.<br />

Seasonality <strong>of</strong> graz<strong>in</strong>g<br />

‘Poa annua [an exotic grass] was positively affected by past graz<strong>in</strong>g <strong>in</strong> spr<strong>in</strong>g, and negatively affected<br />

by past graz<strong>in</strong>g <strong>in</strong> summer’ (Kirkpatrick et al. 2005).<br />

‘Seasonal effects’ may be seen as an <strong>in</strong>teraction between herbivores <strong>of</strong> various type and the feed<br />

on <strong>of</strong>fer. Different plant species have different palatabilities and accessibilities at different stages<br />

<strong>of</strong> the year and at different times <strong>in</strong> the life cycle. Young succulent shoots <strong>of</strong> grasses have a higher<br />

palatability to many animals than coarse dead stalks. Flower heads or seeds that appear seasonally<br />

can be preferentially selected (as by rabbits <strong>in</strong> subalp<strong>in</strong>e vegetation <strong>of</strong> New South Wales, see Leigh et<br />

al. 1987), a circumstance that may have consequences to plant reproduction <strong>in</strong> the short- and longterm.<br />

Thus if animals are <strong>in</strong>troduced to an area <strong>for</strong> short lengths <strong>of</strong> time at different times <strong>of</strong> the year,<br />

the results could be different <strong>for</strong> different plant species.<br />

Whalley and Lodge (1986) set out to manipulate pasture species’ composition through livestock<br />

graz<strong>in</strong>g <strong>in</strong> order to favour a ‘desirable’ native grass <strong>in</strong> a graz<strong>in</strong>g system – Danthonia l<strong>in</strong>kii. They<br />

succeeded by us<strong>in</strong>g heavy summer and early autumn graz<strong>in</strong>g and then light w<strong>in</strong>ter and spr<strong>in</strong>g<br />

graz<strong>in</strong>g. Sheep were more effective than cattle. The idea was to manipulate the graz<strong>in</strong>g regime to<br />

m<strong>in</strong>imise adverse effects on the desirable Danthonia and maximise adverse effects on an undesirable<br />

native grass, Aristida ramosa.<br />

Fire and adaptive <strong>management</strong> <strong>Underp<strong>in</strong>n<strong>in</strong>gs</strong> <strong>of</strong> <strong>fire</strong> <strong>management</strong> <strong>for</strong> <strong>biodiversity</strong> <strong>conservation</strong> <strong>in</strong> reserves

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!