email a friend
printable version
Offshore wind farms are impacting seabirds and migrating passerines

Middelgruden offshore wind farm in Denmark, © UN Photo/ flickr

With the number of offshore wind farms in European waters, and elsewhere, set to rise dramatically in the coming years, it is critical that the implications for wildlife are fully considered. Birds, in particular, are at risk through collisions, barrier effects and habitat loss.


Operational and planned offshore wind farms in the United Kingdom

There are currently 10 operational wind farms (red circles) along the country’s coastline, with a further 36 (green stars) under development (WAB 2009).

There is a growing political impetus to reduce anthropogenic carbon emissions. Wind power has emerged as a leading renewable technology and is currently the fastest growing source of energy in the world. By the end of 2008, wind turbines were satisfying more than 1.5 % of the world’s electricity demand, generating 260 TWh annually (WWEA 2009).

In Europe, there has been a rapid proliferation of wind farms in the marine environment, which may portend a global trend. Within European waters, there are currently some 160 offshore farms either in operation, under construction or being planned. At the forefront of this expanding industry is the United Kingdom with ten operational wind farms made up of 203 turbines, and plans for a further 7,000 turbines by 2020 (see figure). The United Kingdom, together with Germany, currently accounts for around 60 percent of the global offshore wind market (WAB 2009). Although more costly than their terrestrial counterparts, offshore wind farms have a number of advantages. Winds at sea tend to be stronger and more consistent, and weighty turbine components are more easily transported at sea permitting larger turbines to be constructed (European Commission 2008). In addition, offshore wind farms typically encounter less resistance from local communities (Dolman et al. 2003).

However, there are growing concerns that offshore wind farms can have detrimental impacts on wildlife. Birds are particularly vulnerable for three reasons. Firstly, seabirds are negatively impacted through the loss and modification of resting and foraging grounds. Secondly and most importantly, they are killed as a result of collisions with turbine blades: for example, significant fatalities have been reported at marine wind farms situated close to breeding colonies (Everaert and Stienen 2007). Also, during their seasonal migrations, huge numbers of passerines cross Europe’s seas mostly at night and at a low altitude. It is inevitable that birds will collide with turbines, particularly under adverse weather conditions with poor visibility (Hüppop et al. 2006). Thirdly, several studies have found that offshore wind farms act as barriers to travelling seabirds. Displacement from their favoured routes is likely to increase travel distances, causing greater energy expenditure and potentially impacting the survival of nestlings by lowering provisioning rates (Petersen et al. 2003, Fox et al. 2006). For example, at the Nysted offshore wind farm in Denmark, travelling birds (particularly seaduck) displayed profound avoidance behaviour, with the number of birds entering the area declining dramatically following the construction of the wind farm (Desholm and Kahlert 2005).

It is vital that the design, position and alignment of future offshore wind farms take into account the distribution and sensitivity of seabird populations (Garthe and Hüppop 2004, Fox et al. 2006), whilst avoiding zones of dense migration (Hüppop et al. 2006).



Related Case Studies in other sections

References

Desholm, M. and Kahlert, J. (2005) Avian collision risk at an offshore wind farm. Biol. Lett. 1: 296–298.
 
Dolman, S. J., Simmonds, M. P. and Keith, S. (2003) Marine wind farms and cetaceans. Paper submitted to the Scientific Committee of the IWC (IWC/SC/55/E4).
 
European Commission (2008) Offshore wind energy: action needed to deliver on the energy policy objectives for 2020 and beyond. Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions, Brussels.
 
Everaert, J. and Stienen, E. W. M. (2007) Impact of wind turbines on birds in Zeebrugge (Belgium). Biodiv. Conserv. 16: 3345–3359.
 
Fox, A. D., Desholm, M., Kahlert, J., Christensen, T. K. and Krag Petersen, I. B. (2006) Information needs to support environmental impact assessment of the effects of European marine offshore wind farms on birds. Ibis 148 (Suppl. 1): 129–144.
 
Garthe, S. and Hüppop, O. (2004) Scaling possible adverse effects of marine wind farms on seabirds: developing and applying a vulnerability index. J. Appl. Ecol. 41: 724–734.
 
Hüppop, O., Dierschke, J. Exo, K.-M., Fredrich, E. and Hill, R. (2006) Bird migration studies and potential collision risk with offshore wind turbines. Ibis 148: 90–109.
 
Petersen, I. K., Fox, A. D. and Clausager, I. (2003) Distribution and numbers of birds in Kattegat in relation to the proposed offshore wind farm south of Læsø –Ornithological impact assessment. Department of Wildlife Ecology and Biodiversity, National Environmental.
 
WAB (2009) Offshore wind energy. Windenergie-Agentur Bremerhaven/ Bremen e.V. (WAB).
 
WWEA (2009) World Wind Energy Report 2008. Bonn: World Wind Energy Association.

Compiled 2009

Recommended Citation:
BirdLife International (2009) Offshore wind farms are impacting seabirds and migrating passerines. Presented as part of the BirdLife State of the world's birds website. Available from: http://www.birdlife.org/datazone/sowb/casestudy/289. Checked: 27/08/2014