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Resource Documents: Belgium (4 items)

RSSBelgium

Unless indicated otherwise, documents presented here are not the product of nor are they necessarily endorsed by National Wind Watch. These resource documents are shared here to assist anyone wishing to research the issue of industrial wind power and the impacts of its development. The information should be evaluated by each reader to come to their own conclusions about the many areas of debate. • The copyrights reside with the sources indicated. As part of its noncommercial effort to present the environmental, social, scientific, and economic issues of large-scale wind power development to a global audience seeking such information, National Wind Watch endeavors to observe “fair use” as provided for in section 107 of U.S. Copyright Law and similar “fair dealing” provisions of the copyright laws of other nations.


Date added:  March 21, 2015
Belgium, NoisePrint storyE-mail story

Annoyance, detection and recognition of wind turbine noise

Author:  Van Renterghem, Timothy; Bockstael, Annelies; De Weirt, Valentine; and Botteldooren, Dick

ABSTRACT:
Annoyance, recognition and detection of noise from a single wind turbine were studied by means of a two-stage listening experiment with 50 participants with normal hearing abilities. In-situ recordings made at close distance from a 1.8-MW wind turbine operating at 22 rpm were mixed with road traffic noise, and processed to simulate indoor sound pressure levels at LAeq 40 dBA. In a first part, where people were unaware of the true purpose of the experiment, samples were played during a quiet leisure activity. Under these conditions, pure wind turbine noise gave very similar annoyance ratings as unmixed highway noise at the same equivalent level, while annoyance by local road traffic noise was significantly higher. In a second experiment, listeners were asked to identify the sample containing wind turbine noise in a paired comparison test. The detection limit of wind turbine noise in presence of highway noise was estimated to be as low as a signal-to-noise ratio of −23 dBA. When mixed with local road traffic, such a detection limit could not be determined. These findings support that noticing the sound could be an important aspect of wind turbine noise annoyance at the low equivalent levels typically observed indoors in practice. Participants that easily recognized wind-turbine(–like) sounds could detect wind turbine noise better when submersed in road traffic noise. Recognition of wind turbine sounds is also linked to higher annoyance. Awareness of the source is therefore a relevant aspect of wind turbine noise perception which is consistent with previous research.

Timothy Van Renterghem, Annelies Bockstael, Valentine De Weirt, Dick Botteldooren
Department of Information Technology, Ghent University, Gent, Belgium

Science of the Total Environment 456–457 (2013) 333–345

Download original document: “Annoyance, detection and recognition of wind turbine noise

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Date added:  February 9, 2009
Belgium, WildlifePrint storyE-mail story

Effecten van windturbines op de fauna in Vlaanderen

Author:  Everaert, Joris

In Dutch. Instituut voor Natuur- en Bosonderzoek (Nature and Forest Institute), Brussels, Belgium. English Abstract:

Effects of wind turbines on fauna in Flanders

Birds and bats can collide with wind turbines, or encounter the vortex wake behind the turbines. They can also become disturbed in their breeding, resting, and foraging areas, or during migration. Therefore, the impact on fauna was studied on 7 wind farm locations in Flanders (=northern part of Belgium). At 2 additional locations, a reduced random test was also performed. The study results are presented in this report and discussed with foreign results. Recommendations for further study and the selection of new wind farm locations, are also included.

The collision numbers in Flanders, with applied necessary correction factors, varied from 0 to around 125 birds per individual wind turbine per year. No bats were found. The mean number for the 7 wind farms (with correction factors) varied substantially with resp. 1, 3, 7, 12, 21, 26 and 42 birds per wind turbine per year. Wind farms in The Netherlands (comparable locations and species) had similar results.

Most of the collision fatalities in Flanders were local relatively common birds like Black-headed Gull, Herring Gull, Lesser Black-backed Gull, Mallard, Wood Pigeon and Starling, but also rarer or even endangered species were found such as Grey Heron, Common Shelduck, Common Pochard, Wigeon, Common Teal, Kittiwake, Mediterranean Gull, Eurasian Sparrowhawk, Peregrine Falcon, Kestrel, Redshank, Black-tailed Godwit, Oystercatcher, Kentish Plover, Common Tern, Sandwich Tern, Little Tern, Woodcock, Swift and Meadow Pipit. For Common Tern, Sandwich Tern and Little Tern, the number of fatalities was also high. The large number of collided gulls and terns in the Brugge and Zeebrugge wind farms was striking, all the more because these birds are largely diurnally active. This will be the result of local migration of gulls towards a large sleeping place (Brugge) and foraging flights of gulls and terns in the vicinity of a breeding colony (Zeebrugge). It is not clear whether this resulted in a significant impact on the local gull population. The large number of tern collision fatalities during the breeding season in the Zeebrugge wind farm, resulted in a significant impact on the breeding colony of Common Tern, Sandwich Tern and Little Tern. The planned repowering of the Zeebrugge turbines by larger ones with more free space at the height where most terns are flying, must result in less fatalities in the future. A study will determine if additional measures will be needed.

At some foreign wind farm locations, significant numbers of collided birds and bats are also found, including raptors and several rare species. Whether this current impact is significant for national populations, is unclear. At least in some cases, a certain or probable significant impact on local and/or regional populations has been determined. More research is needed to have better clarity on that subject. But at the same time, with a persistent very important impact (including local), effective measures must be taken. This should also include switching off the wind turbines during certain risk periods, or even in some extreme cases the dismantling of turbines.

From the research in Flanders, it was found that modern large wind turbines can also have relatively large numbers of collision fatalities among birds, just like small wind turbines. In several foreign locations, this was also the case, even for bats. The number of tern and gull collision fatalities in Flanders seems to depend largely on the number of present and/or flying birds at the wind farms. For the locations near waterbodies in Flanders, The Netherlands and France, on average for all species, the size of the wind turbine (hub height and/or rotor area) seems to be a less important factor, although there is a tendency (not significant) towards slightly more collision fatalities with larger turbines (numbers per turbine). The calculated collision chances at rotor height for gulls in wind farms with small and large turbines in Flanders seem to confirm this trend. Obviously, factors like species, flight height, flight behavior, and properties of the wind farm and surroundings, will also be very important. When the results are presented per megawatt installed capacity, a wind farm with large wind turbines would have on average less collision fatalities then a wind farm with more smaller turbines. Of course, local differences can play a very important role (for example ‘inland‘ vs. ‘coast’), therefore the results cannot simply be generalized.

The research on disturbance at the wind farm locations in Flanders was rather limited, partly due to the lack of reliable reference situations (highly changing surrounding area in industrial zones). Nevertheless, it was clear that foraging and roosting waterfowl and waders outside the breeding season, experienced some disturbance. Breeding birds had less or no clear disturbance. There are however large differences between species and locations, and still many open questions. Gulls and terns experienced no barrier effect during their local foraging flights in the breeding season, resulting in a large number of birds that crossed the turbines at close distance and consequently also more collisions. Outside the breeding season, for gulls flying towards the sleeping place, the situation was not that clear with only an indication for a partly (small) barrier effect.

An analysis of many foreign studies, confirms that certainly foraging and resting waterfowl like geese, ducks and some wader species outside the breeding season, can experience a disturbance of up to 500m from wind turbines (in some exceptional cases possibly 600-800m). Depending on the local situation, this can result in an important degradation of nature areas. Breeding birds are less disturbed, but still quite important for at least some waders.

In contrast to breeding birds, it was found that for most studied bird species outside the breeding season, the disturbance increased with wind turbine height.

Disturbance of local migration routes can happen, but this will depend on several factors. Many seasonal migrating birds do experience an important barrier effect during the day, but the situation during the night is less known.

Study results in Flanders and from foreign locations clearly show that, under certain circumstances, wind turbines can cause an important negative impact on birds and bats. Cumulative effects because of the expansive growth of wind farms, must be taken into account seriously. More wind turbines will result in extra pressure on top of the already existing sources of negative impact, like power lines, roads, disruption of nature areas, etc. In a densely populated region like Flanders, this degrades the total suitability for ecological functions such as the presence of bird and bat populations and the guarantee for regional or international migration routes.

The right policy for wind farm planning, should include a strategic planning on regional, national and certainly also for the offshore wind farms on an international scale. Based on all information like the amount of wind, residences, protected and other important nature areas and migration routes, maps for potential wind farms can be created.

In general, from the study results, it is recommended not to build new wind farms near important breeding, resting and foraging areas and local or seasonal migration routes. Although the possible impact for planned wind farms can be estimated, in an important number of cases, there can be a substantial lack of data to make a reliable assessment of the potential impact. Certainly in case of a potential impact on the fauna in nature areas that are protected or meet the criteria to be protected, including important migration corridors, the precautionary principle must be applied. Despite all studies and possible proposed mitigation measures, proper site selection (“macro-siting”) is still the best and certain way to reduce the impact. So, this should be the first stage in the search for new wind farm locations. Depending on the quality of the area (for example industrial vs. open undisturbed) and the importance for fauna, other methods can be investigated like mitigation measures and/or compensation measures.

On several levels, there is still an important lack of knowledge concerning the impact of wind turbines of birds and bats. Considering the further expansion of wind energy, more research is urgently needed. This is best performed by independent long-term study in which specific points of interest are conducted.

Download original document: “Effecten van windturbines op de fauna in Vlaanderen

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Date added:  July 18, 2007
Belgium, Siting, WildlifePrint storyE-mail story

Wind turbines and birds in Flanders

Author:  Everaert, Joris; and Kuijken, Eckhart

The average number of collision fatalities in different European wind farms on land varies between a few birds up to 64 birds per turbine per year (Langston and Pullan 2003; Everaert 2006a; Everaert 2007; see Table 1). Also within one wind farm, the impact can strongly differ between individual turbines (Everaert et al. 2002; Everaert & Stienen 2006), clearly showing that ‘site selection’ can play an important role in limiting the number of collision fatalities. …

Study results clearly show that reasonable amounts of birds and bats can collide with wind turbines. An exhaustive study before the selection of future locations is a key factor to avoid deleterious impacts of wind farms on birds and bats.

Cumulative negative impacts with an increasing amount of wind turbines must be taken into account (Langston & Pullan 2003). This especially is developing along fixed bird migration corridors (coasts, mountain passes). More wind farms also means an extra pressure on top of the already existing sources of negative impact (powerlines, traffic etc.). In a densely populated region like Flanders, this degrades the total suitability for ecological functions such as the presence of bird and bat populations and the guarantee for regional or international migration routes. For the offshore situation, international cooperation will be necessary to determine the possible cumulative impact.

Download original document: “Wind turbines and birds in Flanders (Belgium)

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Date added:  November 16, 2006
Belgium, WildlifePrint storyE-mail story

Impact of wind turbines on birds in Zeebrugge (Belgium)

Author:  Everaert, Joris; and Stienen, Eric

Published in Biodiversity and Conservation, November 2006

Abstract: We studied the impact of a wind farm (line of 25 small to medium sized turbines) on birds at the eastern port breakwater in Zeebrugge, Belgium, with special attention to the nearby breeding colony of Common Tern Sterna hirundo, Sandwich Tern Sterna sandvicensis and Little Tern Sterna albifrons. With the data of found collision fatalities under the wind turbines, and the correction factors for available search area, search efficiency and scavenging, we calculated that during the breeding seasons in 2004 and 2005, about 168 resp. 161 terns collided with the wind turbines located on the eastern port breakwater close to the breeding colony, mainly Common Terns and Sandwich Terns. The mean number of terns killed in 2004 and 2005 was 6.7 per turbine per year for the whole wind farm, and 11.2 resp. 10.8 per turbine per year for the line of 14 turbines on the sea-directed breakwater close to the breeding colony. The mean number of collision fatalities when including other species (mainly gulls) in 2004 and 2005 was 20.9 resp. 19.1 per turbine per year for the whole wind farm and 34.3 resp. 27.6 per turbine per year for 14 turbines on the sea-directed breakwater. The collision probability for Common Terns crossing the line of wind turbines amounted 0.110-0.118% for flights at rotor height and 0.007-0.030% for all flights. For Sandwich Tern this probability was 0.046-0.088% for flights at rotor height and 0.005-0.006% for all flights. The breeding terns were almost not disturbed by the wind turbines, but the relative large number of tern fatalities was determined as a significant negative impact on the breeding colony at the eastern port breakwater (additional mortality of 3.0-4.4% for Common Tern, 1.8-6.7% for Little Tern and 0.6-0.7% for Sandwich Tern). We recommend that there should be precautionary avoidance of constructing wind turbines close to any important breeding colony of terns or gulls, nor should artificial breeding sites be constructed near wind turbines, especially not within the frequent foraging flight paths.

Download original document: “Impact of wind turbines on birds in Zeebrugge

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