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Recovery plan for the brush-tailed rock-wallaby - Department of ...

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Approved NSW <strong>Recovery</strong> Plan Brush-<strong>tailed</strong> <strong>rock</strong>-<strong>wallaby</strong><br />

Actions involving on-ground management programs and <strong>the</strong> long-term monitoring <strong>of</strong> sites will<br />

also have economic consequences <strong>for</strong> land managers. However, <strong>the</strong>se programs will involve<br />

activities which are normally required to effectively manage land, such as weed control and feral<br />

animal removal. Costs <strong>for</strong> land managers can be minimised by seeking funding from external<br />

sources and by adopting a cooperative approach to management involving DECC, Catchment<br />

Management Authorities, o<strong>the</strong>r relevant landholders and <strong>the</strong> community.<br />

In addition to areas managed by DECC, additional areas will need to be managed to conserve <strong>the</strong><br />

species outside national parks and reserves.<br />

There are at least three options <strong>for</strong> conserving <strong>the</strong> BTRW on lands that are not managed by<br />

DECC:<br />

1. DECC can negotiate with relevant stakeholders and implement joint conservation<br />

management programs.<br />

2. DECC can acquire land in high priority areas that is o<strong>the</strong>rwise poorly represented in national<br />

parks and reserves.<br />

3. DECC can encourage landowners or leaseholders to enter into voluntary agreements to<br />

conserve <strong>the</strong> BTRW.<br />

These options should be evaluated in terms <strong>of</strong> <strong>the</strong>ir effectiveness in assisting <strong>the</strong> recovery <strong>of</strong> <strong>the</strong><br />

BTRW, and <strong>the</strong>ir economic impact on land managers. Sympa<strong>the</strong>tic management <strong>of</strong> lands<br />

adjacent to BTRW colonies may benefit landowners and land managers by leading to a reduction<br />

in goat and fox numbers. Such a reduction may outweigh potential negative impacts such as<br />

diminished economic returns from <strong>the</strong> conserved area. Landowners entering into conservation<br />

agreements may also benefit from tax relief.<br />

It is considered that <strong>the</strong>re will be o<strong>the</strong>r positive economic consequences from implementing <strong>the</strong><br />

<strong>plan</strong>, including:<br />

• <strong>for</strong> government, overall cost savings by investing in community training and resourcing to<br />

minimise public labour expenditure in feral animal control, and more efficient resource use,<br />

as management <strong>of</strong> <strong>the</strong> species will be more coordinated and strategic<br />

• <strong>for</strong> <strong>the</strong> rural community, reduced predation on, and spread <strong>of</strong> disease to, livestock, and an<br />

improvement in long-term agricultural productivity through better land management<br />

practices <strong>for</strong> wildlife<br />

• <strong>for</strong> landholders negotiating conservation agreements, positive financial outcomes such as tax<br />

relief.<br />

9.4 Scientific and taxonomic value<br />

Macropods comprise almost 40% <strong>of</strong> Australian marsupials and are one <strong>of</strong> <strong>the</strong> continent’s most<br />

successful faunal groups. Rock-wallabies <strong>for</strong>m <strong>the</strong> largest group <strong>of</strong> macropods, representing<br />

31% <strong>of</strong> extant species, and are an internationally recognised model <strong>for</strong> <strong>the</strong> study <strong>of</strong> chromosome<br />

evolution and speciation (Eldridge pers. comm.).<br />

The great variation within <strong>the</strong> <strong>rock</strong>-<strong>wallaby</strong> genus Petrogale has been attributed to <strong>the</strong> highly<br />

discontinuous distribution <strong>of</strong> species populations (Poole 1978, Maynes 1989). In all, 28 different<br />

<strong>rock</strong>-wallabies were described between 1827 and 1992, <strong>of</strong> which 25 were assigned to <strong>the</strong> genus<br />

Petrogale, and three to <strong>the</strong> genus Peradorcas (Briscoe et al 1982). There are currently 16 species<br />

<strong>of</strong> <strong>rock</strong>-<strong>wallaby</strong> in <strong>the</strong> Petrogale genus, with <strong>the</strong> genus Peradorcas now recategorised as<br />

Petrogale (Calaby and Richardson 1988).<br />

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