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Draft National Wind Farm Development Guidelines - July 2010

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used throughout these <strong>Guidelines</strong> as a term of convenience for all causes of bird and bat<br />

deaths that may result from interactions with wind turbines. These include barotrauma,<br />

potential traumatic effects of turbulence caused by rotors, and direct collision strikes (see<br />

Section D.6 for a glossary of terms).<br />

Account should be taken of the fact that mortalities due to turbine collisions are either not<br />

possible or are not considered to be an issue for some species of birds. Assessment of<br />

collision risk for the following categories of birds is not necessary or is unlikely to be required<br />

for most sites within Australia:<br />

• Introduced and feral taxa.<br />

• Flightless and near-flightless birds.<br />

• Other taxa that rarely fly within or through rotor-swept-height.<br />

Some species routinely fly within or through rotor-swept-height (which for current turbines is<br />

generally in the range 30-130 metres above the ground), but many other species rarely if<br />

ever fly in that height range. Flight-height data collected in south-eastern Australia<br />

indicates that many bird taxa rarely fly above 25 metres (Biosis Research unpublished<br />

data) and that interactions with turbines do not need to be assessed for these birds other<br />

than for exceptional sites or circumstances (see also Section D.7). The potential for<br />

exceptional circumstances should be evaluated for each wind farm. Examples may<br />

include locations on defined routes of migration or other long-distance movements if birds<br />

there fly at greater heights than they do during the majority of their routine activities. Unless<br />

the species in question is also a key taxon, assessment is unlikely to be required.<br />

All Australian bat species have capacity to fly within rotor-swept height and, while some<br />

may do so less than others, current knowledge is insufficient to suggest the exclusion of any<br />

key bat taxa from this component of the assessment.<br />

If key taxa with capacity to fly at rotor height are known from the site, further preliminary<br />

investigations of those taxa will be necessary. For resident species, their home range<br />

requirements should be considered and for all key species that might use the site their<br />

foraging, roosting, breeding and other species-specific needs are to be considered at this<br />

phase. Other aspects that should be given preliminary consideration relative to potential<br />

risks for the species involved are typical sizes of flocks, behaviours, where they are most<br />

readily detected and particular behaviours or habitat preferences that may expose them<br />

to high risk.<br />

This phase does not require full or detailed assessments, and information gathering at this<br />

phase does not need to be of a standard that might provide inputs to detailed risk<br />

assessment. The information does, however guide later evidence gathering studies, and is<br />

critical to ensure full alignment of pre- and post-construction assessments using BACI<br />

(Before – After – Control – Impact) designs. Local or otherwise expert knowledge gleaned<br />

during this preliminary phase may be supported by targeted pilot studies to establish<br />

background methodologies and necessary parameters that will guide later phase surveys<br />

and assessments. Pilot surveys are short field studies to further identify and to scope<br />

potential issues. They allow approximation of relevant information such as typical<br />

population on site, number of movements on site, seasonal dependencies, observability<br />

and detectability. If occurrence of key taxa at the site is likely to be seasonal, then pilot<br />

studies must be timed to maximise potential to obtain such information.<br />

The principal purpose of such trials is to establish a sound basis for the need and<br />

subsequent design of any more detailed investigations of risk for key species specific to the<br />

site.<br />

If there is an identified potential for a key species to interact with turbines, the assessment<br />

should proceed to the next phase. If not, relevant authorities may determine that no<br />

further assessment of risk is required for birds or bats.<br />

Page 124 <strong>Draft</strong> <strong>National</strong> <strong>Wind</strong> <strong>Farm</strong> <strong>Development</strong> <strong>Guidelines</strong> – 2 <strong>July</strong> <strong>2010</strong>

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