NSW Bitou Bush Threat Abatement Plan - Department of ...
NSW Bitou Bush Threat Abatement Plan - Department of ...
NSW Bitou Bush Threat Abatement Plan - Department of ...
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50<br />
<strong>Threat</strong> <strong>Abatement</strong> <strong>Plan</strong> - Invasion <strong>of</strong> native plant communities by Chrysanthemoides monilifera<br />
The staged approach must:<br />
< be planned before any control is undertaken, with all stages clearly marked and the<br />
timing <strong>of</strong> each stage determined, preferably incorporated into a site-specific<br />
management plan (see below)<br />
< only control areas for which there are resources available to undertake the subsequent<br />
stages, including most importantly the follow-up treatment <strong>of</strong> seedlings. Irrespective <strong>of</strong><br />
the initial control measure implemented, follow-up treatments are required to control<br />
recruitment (as described by Vranjic 2000).<br />
7.4.1 Littoral rainforest - an example <strong>of</strong> a staged approach<br />
<strong>Bitou</strong> bush poses a serious threat to littoral rainforest. It threatens littoral rainforests in two main<br />
ways. First, it invades the margins, where it competes with or suppresses the species that protect<br />
the rainforest. The exposed margins are then subject to further degradation particularly on the<br />
seaward fringes, which are exposed to salt spray and desiccating winds. Second, bitou bush<br />
establishes in canopy gaps where it suppresses regrowth and reduces recruitment <strong>of</strong> native plants.<br />
Canopy gaps can occur naturally or through the competitive effect <strong>of</strong> bitou bush at the margins.<br />
Long-term monitoring <strong>of</strong> bitou bush-infested littoral rainforests shows that where small gaps in<br />
the canopy occur, lantana and native species may replace bitou bush. However, in larger gaps and<br />
on the margins, bitou bush remains the dominant species (Hunter pers. comm.).<br />
The staged approach is necessary in the control <strong>of</strong> bitou bush invasion <strong>of</strong> margins to ensure that it<br />
does not result in exposure <strong>of</strong> the littoral rainforest following the removal <strong>of</strong> bitou bush from<br />
where it replaces the forest’s protective vegetation. Thus stage 1 would involve a staggered<br />
removal <strong>of</strong> bitou bush from the forest edge, especially on the seaward side <strong>of</strong> littoral rainforests,<br />
to maintain the forest’s protective buffer from wind and salt spray. For the control <strong>of</strong> bitou bush in<br />
canopy gaps, stage 1 would involve the systematic removal <strong>of</strong> all plants from within the canopy,<br />
especially in forest gaps, while stage 2 would involve the removal <strong>of</strong> bitou bush from the forest<br />
margins, and stage 3 removal from the surrounding habitat.<br />
7.5 Site-specific management<br />
Best practice management guidelines (Vranjic 2000) and the <strong>NSW</strong> bitou bush strategy (NPWS<br />
2001a) both emphasise the importance <strong>of</strong> site-specific strategies or management plans for the<br />
control <strong>of</strong> bitou bush. Previously there has been no framework for developing such strategies, but<br />
rather information was presented on a series <strong>of</strong> bitou bush densities and invaded habitats along<br />
with a range <strong>of</strong> control options (see Vranjic 2000).<br />
The use <strong>of</strong> site-specific management strategies should not result in broader management<br />
objectives being compromised. To avoid this occurring and still ensure effective site management,<br />
a framework has been developed for compiling site-specific management strategies/plans (see<br />
below) as well as a pr<strong>of</strong>orma for preparing a site-specific management plan (see Appendix 9).<br />
7.5.1 A framework for site-specific management plans<br />
While the development <strong>of</strong> site-specific management plans is dependent on local factors and<br />
conditions, each plan [for the purposes <strong>of</strong> this TAP] must be based on a core set <strong>of</strong> attributes.<br />
These form a framework for the development <strong>of</strong> site-specific management plans for the control <strong>of</strong>