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OPW Fauna Management Plan RFI Response · OPW25/0057
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Fauna Management Plan v1 NCES REF: J001343 Lot 105 on SP118458 – 62 Lake MacDonald Drive, Cooroy, QLD 5 FAUNA MANAGEMENT MEASURES – DURING CLEARING 5.1 Vegetation Clearing Direction All trees are to be searched for wildlife presence prior to felling and potential or known habitat trees are to be left standing for a minimum of one night prior to eventual felling. All trees for removal should be felled in open areas of the site to avoid impacts to surrounding and vegetation. The management measures detailed below are general in nature and all measures may not apply to the subject site. The fauna spotter/catcher will ultimately be responsible for determining which management measures are applicable based on the pre-clearing fauna surveys. 5.2 Sequential Vegetation Clearing Vegetation clearing is to be carried out using a sequential clearing method as follows: 1. Any habitat trees; hollow-bearing trees and/or other significant habitat features identified during the initial site inspection, are to be cleared last. 2. The grassy understorey is to be slashed first to create a disturbance activity which encourages ground dwelling fauna to relocate from the impact area. 3. Non-habitat trees will be cleared and stockpiled for mulching. Clearing of non-habitat trees using machinery will only occur where their removal will not directly impact adjoining habitat trees (e.g., canopies do not interconnect). 4. After clearing of non-habitat trees, an elevated work platform or cherry-picker will be used in conjunction with a chainsaw operator and suitably qualified fauna spotter/catcher to inspect and remove arboreal habitat as necessary prior to habitat tree felling. This method involves the fauna spotter/catcher inspecting each of the potential habitat features to determine the presence of arboreal fauna. This process is detailed following the step-by-step basis below: i. The fauna spotter/catcher (with arborist unless the fauna spotter/catcher has a working from heights certificate and chainsaw certificate) will inspect each potential habitat resource (i.e., ringtail possum drey) identified in each tree using the cherry-picker. This is usually carried out by simply looking into hollows with the assistance of a small torch, however, burrow and bore-scopes can also be useful for deep hollows. ii. If fauna is located within a hollow, the tree is either to be left standing for such time until the fauna relocates on its own accord, or a piece of towel or rag will be firmly placed in the entrance to prevent the wildlife from escaping as in most cases arboreal fauna become aware of the presence of the fauna spotter/catcher and may attempt to flee the nesting/denning hollow due to a perceived threat. If an occupied ringtail possum drey is encountered, the fauna spotter/catcher should quietly approach (i.e., avoid contacting other branches) the drey in the cherry-picker bucket and physically capture the possum by placing the entire drey in a catch bag or only the possum if it emerges from the drey. iii. In instances where the fauna does not relocate on its own accord, and once the hollow entrance has been secured, the arborist or fauna spotter/catcher will cut the entire hollow limb off below the cavity where the branch remains solid. In circumstances where a hollow continues into the main stem of the tree, a small window will be carefully cut into the hollow, allowing the fauna spotter/catcher to plug the hollow above and below the window, then the hollow limb removed and lowered to the ground in sections. iv. When the fauna has been safely secured within its hollow, the entire limb can then be placed in the cherry-picker bucket or lowered to the ground using ropes depending on the size of the limb. v. The catch bag will then be placed in a cool, quiet location until translocation to the recipient habitat site, when at dusk the bag is re-opened to allow the fauna to emerge of its own accord. All vegetation is to be felled onto the site and is to avoid impacts to offsite vegetation. Any disturbance to adjoining vegetation, including incidental deposition of vegetative waste material, is to be © 2024 14
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