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Strategic management of Aleppo Pines on Lower Eyre

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8 A STRATEGIC APPROACH<br />

8.1 Criteria for <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine c<strong>on</strong>trol<br />

<str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine sites are identified for local eradicati<strong>on</strong> if:<br />

1. The site poses a high infestati<strong>on</strong> risk to native vegetati<strong>on</strong> such as high quality roadside<br />

remnants, threatened vegetati<strong>on</strong> communities, threatened flora sites, Heritage Agreements,<br />

nati<strong>on</strong>al parks and reserves, and<br />

2. The site is more than 5 kilometres from the EPYTBC breeding area, and<br />

3. There are no records <str<strong>on</strong>g>of</str<strong>on</strong>g> EPYTBC feeding at the site within the last 10 years, or<br />

4. The site was 100% burnt during the January 2005 bushfire.<br />

Depending <strong>on</strong> site characteristics, the c<strong>on</strong>trol priority high, medium or low was assigned (see<br />

Map 4 and Appendix 3). Site characteristic notes rati<strong>on</strong>alise the assignment <str<strong>on</strong>g>of</str<strong>on</strong>g> high, medium or<br />

low prioritisati<strong>on</strong> and are shown in Appendix 3.<br />

In the case <str<strong>on</strong>g>of</str<strong>on</strong>g> criteri<strong>on</strong> number two, shading in Map 4 identifies the 5 kilometre buffer around the<br />

currently known EPYTBC breeding area. The EPYTBC breeding area has been identified through<br />

the analysis and mapping <str<strong>on</strong>g>of</str<strong>on</strong>g> l<strong>on</strong>g-term data collected during nest m<strong>on</strong>itoring as part <str<strong>on</strong>g>of</str<strong>on</strong>g> the jointly<br />

funded Department for Envir<strong>on</strong>ment and Heritage and <strong>Eyre</strong> Peninsula Natural Resources<br />

Management Board EPYTBC Recovery Project. More informati<strong>on</strong> <strong>on</strong> EPYTBC breeding habitat is<br />

provided in van Weenen and Cooper (2000).<br />

8.2 Criteria for <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine retenti<strong>on</strong> and <str<strong>on</strong>g>management</str<strong>on</strong>g><br />

Pine sites are recommended for retenti<strong>on</strong> and <str<strong>on</strong>g>management</str<strong>on</strong>g> if:<br />

1. The site occurs in or within 5 kilometres <str<strong>on</strong>g>of</str<strong>on</strong>g> the EPYTBC breeding area, or<br />

2. EPYTBC have been recorded feeding at the site within the last 10 years AND the site poses a<br />

minimum infestati<strong>on</strong> risk to native vegetati<strong>on</strong> such as high quality roadside remnants,<br />

threatened vegetati<strong>on</strong> communities, threatened flora sites, Heritage Agreements, nati<strong>on</strong>al<br />

parks and reserves, or<br />

3. The site is <strong>on</strong> private land and poses a minimum infestati<strong>on</strong> risk to biodiversity values.<br />

In the case <str<strong>on</strong>g>of</str<strong>on</strong>g> criteri<strong>on</strong> number two, there are a minimal number <str<strong>on</strong>g>of</str<strong>on</strong>g> sites (less than 10%) where<br />

<str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> <str<strong>on</strong>g>Pines</str<strong>on</strong>g> are recommended for retenti<strong>on</strong> and the site poses a risk to other biodiversity values.<br />

The majority <str<strong>on</strong>g>of</str<strong>on</strong>g> these occur <strong>on</strong> SA Water land (Uley Basin) and are recommended for priority<br />

<str<strong>on</strong>g>management</str<strong>on</strong>g> (i.e. removal <str<strong>on</strong>g>of</str<strong>on</strong>g> emergent seedlings) in agreement with SA Water.<br />

In the case <str<strong>on</strong>g>of</str<strong>on</strong>g> criteri<strong>on</strong> number three, infestati<strong>on</strong> risk to biodiversity values is c<strong>on</strong>sidered to be<br />

minimal where a site occurs in the middle <str<strong>on</strong>g>of</str<strong>on</strong>g> a cropped or grazed paddock (e.g. shelter belt or<br />

isolated paddock trees) at least 100 metres from remnant vegetati<strong>on</strong> or roadside reserves<br />

c<strong>on</strong>taining native vegetati<strong>on</strong>. <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine seeds are wind dispersed and can carry for<br />

c<strong>on</strong>siderable distances <strong>on</strong> prevailing winds, however the majority <str<strong>on</strong>g>of</str<strong>on</strong>g> seeds fall to within 40-<br />

50 metres <str<strong>on</strong>g>of</str<strong>on</strong>g> the parent tree (Bulman 1992).<br />

22 <str<strong>on</strong>g>Strategic</str<strong>on</strong>g> <str<strong>on</strong>g>management</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> <str<strong>on</strong>g>Pines</str<strong>on</strong>g> <strong>on</strong> <strong>Lower</strong> <strong>Eyre</strong> Peninsula to maximise biodiversity c<strong>on</strong>servati<strong>on</strong> outcomes

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