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Forthbank Wind Energy Development - Partnerships for Renewables

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<strong>Forthbank</strong> <strong>Wind</strong> <strong>Energy</strong> <strong>Development</strong><br />

enclosed by the 4 turbines) it is unlikely that birds will have to make large detours in order to<br />

avoid the development and so no increase in energy expenditure is expected 33 .<br />

12.4.17 Furthermore, although some birds may avoid flying through the operational wind energy<br />

development, given the configuration of the four turbines (i.e. a cluster of three to the south<br />

east of the site and a single isolated turbine located approximately 800m to the north east, see<br />

Figure 1.1 (Site Location Plan) and Figure 1.2 (Site Layout)), it is likely that many will still be<br />

able to commute safely between the Forth Estuary and adjacent habitats through this corridor.<br />

Even assuming an avoidance distance of 100m from the nearest turbines this would still leave<br />

a corridor of over 500m.<br />

12.4.18 Consequently, it is considered that the proposed wind energy development is unlikely to<br />

present a significant barrier to the movement of birds in the vicinity of the wind energy<br />

development.<br />

Collision<br />

12.4.19 Collision of a bird with the turbine rotors is almost certain to result in the death of the bird. The<br />

impact of an individual loss on a population is influenced by several characteristics of the<br />

affected population, notably its size, density, recruitment rate (additions to the population<br />

through reproduction and immigration) and mortality rate (the natural rate of losses due to<br />

death and emigration).<br />

12.4.20 In general, the impact of an individual lost from the population will be greater <strong>for</strong> species that<br />

occur at low density, are relatively long-lived and reproduce at a low rate. Such species<br />

include wildfowl and the larger raptors. Conversely, the impact will often be insignificant <strong>for</strong><br />

short-lived species with high reproductive rates found at high densities, including most<br />

passerines (e.g. skylark).<br />

12.4.21 In broad terms, the number of collisions during a given period (e.g. a year) is the product of 2<br />

factors:<br />

• The number of birds flying through the rotors during the period (the number of rotor<br />

transits). The number of rotor transits is influenced by the frequency with which a<br />

species flies through the wind farm area and, crucially, the probability that any bird<br />

on a collision course will take avoiding action (the avoidance rate); and<br />

• The probability that a bird will be struck by the rotors on any given transit. The<br />

probability of collision <strong>for</strong> a bird passing through the rotors is mainly determined by<br />

the size of the bird, its mode of flight (flapping or gliding) and its flight speed, along<br />

with the dimensions of the rotors and the speed at which they rotate.<br />

12.4.22 Collision risk is perceived to be higher in birds that spend much of the time in the air, such as<br />

<strong>for</strong>aging raptors and those that have regular flight paths between feeding and<br />

breeding/roosting grounds (e.g. divers and geese). Vulnerability to collision is also influenced<br />

by factors such as the flight manoeuvrability of a species and its tendency to fly in conditions of<br />

reduced visibility (e.g. at night or in fog).<br />

November 2010 Chapter 12 Page 40<br />

Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> <strong>Development</strong> Co. Ltd 2010 ©

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