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Strategic management of Aleppo Pines on Lower Eyre

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EXECUTIVE SUMMARY<br />

Introducti<strong>on</strong><br />

This report provides a recommended approach to <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine <str<strong>on</strong>g>management</str<strong>on</strong>g> <strong>on</strong> lower <strong>Eyre</strong><br />

Peninsula (EP) to benefit the regi<strong>on</strong>’s biodiversity. <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> <str<strong>on</strong>g>Pines</str<strong>on</strong>g> are both an envir<strong>on</strong>mental weed<br />

(proclaimed under the Natural Resources Management Act 2004) threatening native vegetati<strong>on</strong><br />

and an important food source for the Critically Endangered <strong>Eyre</strong> Peninsula Yellow-tailed Black-<br />

Cockatoo (EPYTBC). This report aims to balance the competing interests in the c<strong>on</strong>trol <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g><br />

<str<strong>on</strong>g>Pines</str<strong>on</strong>g> <strong>on</strong> EP and present <str<strong>on</strong>g>management</str<strong>on</strong>g> recommendati<strong>on</strong>s to achieve maximum biodiversity<br />

benefit.<br />

<str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine site assessments<br />

Two hundred and fifty-three <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine sites were surveyed across lower <strong>Eyre</strong> Peninsula. Over<br />

half (58%) <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine sites were identified for c<strong>on</strong>trol (local eradicati<strong>on</strong>) due to negative<br />

impacts <strong>on</strong> biodiversity values (Table 1). Of these, 38% were identified for high priority eradicati<strong>on</strong><br />

due to their proximity to threatened flora sites and remnant threatened vegetati<strong>on</strong> communities.<br />

Seventeen percent <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine sites surveyed were identified as important EPYTBC feeding sites<br />

and/or occurring in the core breeding area (Koppio Hills) and recommended for retenti<strong>on</strong> and<br />

<str<strong>on</strong>g>management</str<strong>on</strong>g> (Table 1). The assessments <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine sites in this way aims to focus efforts <strong>on</strong><br />

those sites posing the most threat to biodiversity values. The assessment suggests a prioritised focus<br />

for site c<strong>on</strong>trol or <str<strong>on</strong>g>management</str<strong>on</strong>g> rather than an increase or decrease in existing effort by current<br />

stakeholders.<br />

Number <str<strong>on</strong>g>of</str<strong>on</strong>g> sites<br />

% total number <str<strong>on</strong>g>of</str<strong>on</strong>g> sites<br />

Table 1 Number <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine sites in each <str<strong>on</strong>g>management</str<strong>on</strong>g> category<br />

Eradicati<strong>on</strong>:<br />

High priority<br />

Eradicati<strong>on</strong>:<br />

Medium<br />

priority<br />

Eradicati<strong>on</strong>:<br />

Low priority<br />

Retain &<br />

Manage<br />

56 18 72 43 64<br />

22 7 29 17 25<br />

Retain:<br />

Private<br />

<str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> <str<strong>on</strong>g>Pines</str<strong>on</strong>g> as an EPYTBC food resource<br />

<strong>Eyre</strong> Peninsula Yellow-tailed Black-Cockatoos are adept feeders <strong>on</strong> <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine c<strong>on</strong>es. In the<br />

breeding area, EPYTBCs spend at least 75% <str<strong>on</strong>g>of</str<strong>on</strong>g> their foraging time feeding <strong>on</strong> seeds from <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g><br />

Pine c<strong>on</strong>es (pre-fire data). Risk <str<strong>on</strong>g>of</str<strong>on</strong>g> terrestrial predati<strong>on</strong> is also reduced while EPYTBCs are feeding in<br />

<str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine.<br />

EPYTBCs display habitual feeding behaviour and have str<strong>on</strong>g site fidelity for particular <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine<br />

trees, revisiting the same stand and even the same tree every seas<strong>on</strong>, both in their breeding area<br />

and winter habitat.<br />

EPYTBC nest selecti<strong>on</strong> is influenced by the proximity <str<strong>on</strong>g>of</str<strong>on</strong>g> traditi<strong>on</strong>al <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine stands. The majority<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> nests are within 2 kilometres <str<strong>on</strong>g>of</str<strong>on</strong>g> known feed trees.<br />

A comparis<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> food availability <str<strong>on</strong>g>of</str<strong>on</strong>g> native (Wrinkled Hakea, Hakea rugosa) and n<strong>on</strong>-native<br />

(<str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine) EPYTBC food resources illustrated that an average size <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine (8-10 metres)<br />

has over <strong>on</strong>e thousand times more available seed (974,524.4) than <strong>on</strong>e large size hakea bush<br />

(718.6). This has important implicati<strong>on</strong>s for EPYTBC c<strong>on</strong>servati<strong>on</strong> and the replacement <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

equivalent food resources if known <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine feed trees are removed.<br />

It is estimated that 1.77 hectares <str<strong>on</strong>g>of</str<strong>on</strong>g> pure hakea revegetati<strong>on</strong> would be required to replace the<br />

equivalent available food resource if 10 medium sized <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g>s <str<strong>on</strong>g>Pines</str<strong>on</strong>g> were removed. This equates<br />

to 35.4 hectares <str<strong>on</strong>g>of</str<strong>on</strong>g> representative Sugar Gum Woodland direct seeding (with an abundance <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

5% hakea per hectare).<br />

Nutriti<strong>on</strong>ally, <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine seeds are higher in crude fats and have greater total energy c<strong>on</strong>tent<br />

compared to both Wrinkled Hakea and Elm-seed Hakea (H. cycloptera), but are harder to digest<br />

and c<strong>on</strong>siderably lower in calcium. There was no evidence that <str<strong>on</strong>g>Aleppo</str<strong>on</strong>g> Pine seeds c<strong>on</strong>tain any<br />

<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 iii

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