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Example mean Doppler shift data fitted with 3rd order polynomial curve ͑ y ͒ . Line indicates true CW frequency; ‘P’ indicates crossover point. Data taken from ‘horizontal’ rotor ensonification at 0.5 m. 

Example mean Doppler shift data fitted with 3rd order polynomial curve ͑ y ͒ . Line indicates true CW frequency; ‘P’ indicates crossover point. Data taken from ‘horizontal’ rotor ensonification at 0.5 m. 

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Bat mortality resulting from actual or near-collision with operational wind turbine rotors is a phenomenon that is widespread but not well understood. Because bats rely on information contained in high-frequency echoes to determine the nature and movement of a target, it is important to consider how ultrasonic pulses similar to those used by bats f...

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Context 1
... the fan was turned off ͑ and it was verified that it therefore contributed no appre- ciable noise to recordings ͒ and measurements taken over a period of 3 s, during which time the rotor could be consid- ered to be rotating with a constant angular velocity. The Doppler shift signatures made by moving blades at a distance of 0.5 m were assessed using a Continuous Wave, Constant Frequency ͑ CW CF ͒ source tone of 40.7 kHz. This was emitted via a MA40B8R ͑ Murata Manufacturing Co., Ltd., Kyoto, Japan ͒ transducer, through a tone generator, situated opposite the turbine. Transducer beam angle was 50°, similar to the beam angle of some bat species ͓ e.g., the FM bat Eptesicus fuscus at 40° ͑ Wotton and Jenison, 1997 ͔͒ , giving a beam diameter of approximately 0.4 m at 0.5 m distance. The transducer was placed in horizontal juxtaposition with a cali- 1 brated, flat response 40BF microphone and 26AC preamp- 4 Љ lifier with 12AK power module ͑ GRAS Sound & Vibration, Holte, Denmark ͒ ͑ frequency range 2 Hz–100 kHz ͒ and a high speed A602fc ͑ Basler AG, Ahrensburg, Germany ͒ video camera set to capture at a rate of 60 frames per second. The camera was positioned to capture roughly the same area of rotor as was ensonified by the transducer. The turbine rotor was then ensonified during operation at one of the following angles to the source: ͑ a ͒ ‘horizontal’, ͑ b ͒ ‘lateral top’, ͑ c ͒ ‘lateral mid’, or ͑ d ͒ ‘lateral bottom’ ͑ Fig. 1 ͒ , accurately aligned with the assistance of a low power laser. The reflected echo was recorded and time-synchronized with the motion capture via a USB-6251 ͑ National Instruments Corporation, TX, USA ͒ DAQ card sampling at a rate of 1250 kS s −1 at 16-bit resolution, over a 3 s period, which enabled exact blade movements and positions to be corre- lated with any Doppler shift patterns returned to source. The operational rotor itself was verified not to contribute to the ambient sound in the ultrasonic frequency band. All recorded data were saved directly to a PC in uncompressed .wav file format and were processed using AUDITION 1.0 ͑ Adobe Systems, Inc., CA, USA ͒ and analyzed using MATLAB 2009b ͑ The MathWorks, Inc., MA, USA ͒ . Moving turbine blades were found to produce Doppler shift signatures that varied according to the angle of rotor ensonification and blade position at the point of reflection. Figure 2 describes the Doppler shift signatures for all angles ensonified, indicating the blade positions resulting in shift portions for each blade sweep. In Fig. 2, Doppler shift portions have been segmented ͑ A, B, C, etc. ͒ and the nature of blade movement resulting in these portions detailed beneath the corresponding signature sonogram. For example, segment ‘A’ of the horizontal shift corresponds to movement of the blade’s leading edge from a position above the source to a position parallel with the source; segment ‘B’ corresponds to the blade becoming parallel with the source; segment ‘C’ corresponds with movement of the blade’s trailing edge from the parallel position to one below the source. The extent of the Doppler shift deviation from the mean shift varied between angles; ‘horizontal’ shift ranged between Ϯ 25 Hz, ‘lateral top’ shift ranged between Ϯ 595 Hz, ‘lateral mid’ shift ranged between Ϯ 785 Hz and ‘lateral bottom’ shift ranged between Ϯ 730 Hz. Overall, sound reflected from the operational rotor from the horizontal aspect demonstrated slight negative Doppler shift, from the lateral top aspect demonstrated negative shift, from the lateral mid aspect demonstrated slight positive shift and from the lateral bottom aspect demonstrated positive shift. Since an incoming bat-like echolocation pulse approximately 2–6 ms ͒ is much shorter than the blade sweep pass period for this turbine model at low wind speed ͑ approximately 100 ms ͒ , an approaching bat would receive only short samples of the Doppler shift produced by the moving blades. As the extent of the shift observed in these short echoes would depend on the exact blade position at the point of echo reflection it is useful to simulate random sampling of the rotor Doppler shift pattern using a Monte Carlo method. This would allow an estimation of the number of pulse echoes an approaching bat would need to receive in order to determine the true nature of blade movement. To do this, five single blade sweep signatures were extracted from the CW echo data set and had the true CW frequency removed by applying a second order Butterworth band stop filter. Each single signature was divided into ten equal 10 ms segments around a common point, which was taken as the position that the shift sweep crossed the true CW frequency ͑ see Fig. 3 ͒ . A fast Fourier transform ͑ FFT ͒ was then applied to each segment and the frequency of peak energy obtained. The series of ten values for frequency of peak energy was then averaged over five blade sweeps and to this mean shift data a polynomial ͑ 3rd order ͒ curve was fitted, as shown in Fig. 3. To simulate CF sampling, the curve function was applied to sample the frequencies at random time intervals over the course of a single blade sweep generated using MAT- LAB’s random number generator function. Sampled frequencies were generated in increasingly greater numbers ͑ i.e., more echoes per blade sweep ͒ and the mean frequency extracted until the sample size was sufficient for the resulting mean to converge to the mean shift of the signature ͑ within an error margin of Ϯ 10 Hz ͒ . However, some bat species employ a Frequency Modulated ͑ FM ͒ echolocation strategy. For FM simulations, an additional random shift of between Ϯ 200 Hz was combined in order to take into account the more broadband nature of the FM pulse and hence the greater potential for variation in frequency of peak energy. All Monte Carlo simulations were run 20 times to obtain an average number of samples required to converge. Simulation results revealed that, for CF bat-like echoes, the number of samples required to converge to the mean shift per blade pass was 320 Ϯ 121 for ‘horizontal’ ensonification, 150 Ϯ 105 for ‘lateral mid’, 55 Ϯ 16 for ‘lateral top’ and 100 Ϯ 78 for ‘lateral bottom’. For FM simulations, the number of samples required to converge to the mean shift per blade pass was 330 Ϯ 123 for ‘horizontal’ ensonification, 200 Ϯ 91 for ‘lateral mid’, 190 Ϯ 143 for ‘lateral top’ and 150 Ϯ 78 for ‘lateral bottom’. Nearly all cases showed a high degree of variance in the number of samples required for convergence. As bats employ a set duration ultrasonic pulse to ‘sample’ an operational rotor, it is useful to experimentally measure the information contained in such echoes reflected from turbine blades in order to compare with simulation predictions. In order to produce consistent, accurately replicable pulses for analysis, an artificial bat echolocation pulse was simulated, modeled on the FM pulse of a common pipistrelle bat ͑ Pipistrellus pipistrellus ͒ ͑ see Fig. 5 ͒ . The equation used to create this pulse, Y , over time t , is defined as: Y ͑ t ͒ = A ͑ t ͒ · ␭ ͑ t ͒ . ͑ 1 ͒ Time t is divided into four segments, t 0 : t 1 ; t 1 : t 2 ; t 2 : t 3 and t 3 : t end . The amplitude modulation of the pulse, A ͑ t ͒ , is varied over three portions of the pulse and is defined ...
Context 2
... to rotate freely up to a speed of 10.5 rad s −1 , measured by stroboscope, consistent with low wind speeds of 4.1 m s −1 ͑ previous research has found bat mortality to be highest on nights of wind speed less than 6 m s Arnett et al. , 2008; Horn et al. , 2008 measured by anemometer. At this point the fan was turned off ͑ and it was verified that it therefore contributed no appre- ciable noise to recordings ͒ and measurements taken over a period of 3 s, during which time the rotor could be consid- ered to be rotating with a constant angular velocity. The Doppler shift signatures made by moving blades at a distance of 0.5 m were assessed using a Continuous Wave, Constant Frequency ͑ CW CF ͒ source tone of 40.7 kHz. This was emitted via a MA40B8R ͑ Murata Manufacturing Co., Ltd., Kyoto, Japan ͒ transducer, through a tone generator, situated opposite the turbine. Transducer beam angle was 50°, similar to the beam angle of some bat species ͓ e.g., the FM bat Eptesicus fuscus at 40° ͑ Wotton and Jenison, 1997 ͔͒ , giving a beam diameter of approximately 0.4 m at 0.5 m distance. The transducer was placed in horizontal juxtaposition with a cali- 1 brated, flat response 40BF microphone and 26AC preamp- 4 Љ lifier with 12AK power module ͑ GRAS Sound & Vibration, Holte, Denmark ͒ ͑ frequency range 2 Hz–100 kHz ͒ and a high speed A602fc ͑ Basler AG, Ahrensburg, Germany ͒ video camera set to capture at a rate of 60 frames per second. The camera was positioned to capture roughly the same area of rotor as was ensonified by the transducer. The turbine rotor was then ensonified during operation at one of the following angles to the source: ͑ a ͒ ‘horizontal’, ͑ b ͒ ‘lateral top’, ͑ c ͒ ‘lateral mid’, or ͑ d ͒ ‘lateral bottom’ ͑ Fig. 1 ͒ , accurately aligned with the assistance of a low power laser. The reflected echo was recorded and time-synchronized with the motion capture via a USB-6251 ͑ National Instruments Corporation, TX, USA ͒ DAQ card sampling at a rate of 1250 kS s −1 at 16-bit resolution, over a 3 s period, which enabled exact blade movements and positions to be corre- lated with any Doppler shift patterns returned to source. The operational rotor itself was verified not to contribute to the ambient sound in the ultrasonic frequency band. All recorded data were saved directly to a PC in uncompressed .wav file format and were processed using AUDITION 1.0 ͑ Adobe Systems, Inc., CA, USA ͒ and analyzed using MATLAB 2009b ͑ The MathWorks, Inc., MA, USA ͒ . Moving turbine blades were found to produce Doppler shift signatures that varied according to the angle of rotor ensonification and blade position at the point of reflection. Figure 2 describes the Doppler shift signatures for all angles ensonified, indicating the blade positions resulting in shift portions for each blade sweep. In Fig. 2, Doppler shift portions have been segmented ͑ A, B, C, etc. ͒ and the nature of blade movement resulting in these portions detailed beneath the corresponding signature sonogram. For example, segment ‘A’ of the horizontal shift corresponds to movement of the blade’s leading edge from a position above the source to a position parallel with the source; segment ‘B’ corresponds to the blade becoming parallel with the source; segment ‘C’ corresponds with movement of the blade’s trailing edge from the parallel position to one below the source. The extent of the Doppler shift deviation from the mean shift varied between angles; ‘horizontal’ shift ranged between Ϯ 25 Hz, ‘lateral top’ shift ranged between Ϯ 595 Hz, ‘lateral mid’ shift ranged between Ϯ 785 Hz and ‘lateral bottom’ shift ranged between Ϯ 730 Hz. Overall, sound reflected from the operational rotor from the horizontal aspect demonstrated slight negative Doppler shift, from the lateral top aspect demonstrated negative shift, from the lateral mid aspect demonstrated slight positive shift and from the lateral bottom aspect demonstrated positive shift. Since an incoming bat-like echolocation pulse approximately 2–6 ms ͒ is much shorter than the blade sweep pass period for this turbine model at low wind speed ͑ approximately 100 ms ͒ , an approaching bat would receive only short samples of the Doppler shift produced by the moving blades. As the extent of the shift observed in these short echoes would depend on the exact blade position at the point of echo reflection it is useful to simulate random sampling of the rotor Doppler shift pattern using a Monte Carlo method. This would allow an estimation of the number of pulse echoes an approaching bat would need to receive in order to determine the true nature of blade movement. To do this, five single blade sweep signatures were extracted from the CW echo data set and had the true CW frequency removed by applying a second order Butterworth band stop filter. Each single signature was divided into ten equal 10 ms segments around a common point, which was taken as the position that the shift sweep crossed the true CW frequency ͑ see Fig. 3 ͒ . A fast Fourier transform ͑ FFT ͒ was then applied to each segment and the frequency of peak energy obtained. The series of ten values for frequency of peak energy was then averaged over five blade sweeps and to this mean shift data a polynomial ͑ 3rd order ͒ curve was fitted, as shown in Fig. 3. To simulate CF sampling, the curve function was applied to sample the frequencies at random time intervals over the course of a single blade sweep generated using MAT- LAB’s random number generator function. Sampled frequencies were generated in increasingly greater numbers ͑ i.e., more echoes per blade sweep ͒ and the mean frequency extracted until the sample size was sufficient for the resulting mean to converge to the mean shift of the signature ͑ within an error margin of Ϯ 10 Hz ͒ . However, some bat species employ a Frequency Modulated ͑ FM ͒ echolocation strategy. For FM simulations, an additional random shift of between Ϯ 200 Hz was combined in order to take into account the more broadband nature of the FM pulse and hence the greater potential for variation in frequency of peak energy. All Monte Carlo simulations were run 20 times to obtain an average number of samples required to converge. Simulation results revealed that, for CF bat-like echoes, the number of samples required to converge to the mean shift per blade pass was 320 Ϯ 121 for ‘horizontal’ ensonification, 150 Ϯ 105 for ‘lateral mid’, 55 Ϯ 16 for ‘lateral top’ and 100 Ϯ 78 for ‘lateral bottom’. For FM simulations, the number of samples required to converge to the mean shift per blade pass was 330 Ϯ 123 for ‘horizontal’ ensonification, 200 Ϯ 91 for ‘lateral mid’, 190 Ϯ 143 for ‘lateral top’ and 150 Ϯ 78 for ‘lateral bottom’. Nearly all cases showed a high degree of variance in the number of samples required for convergence. As bats employ a set duration ultrasonic pulse to ‘sample’ an operational rotor, it is useful to experimentally measure the information contained in such echoes reflected from turbine blades in order to compare with simulation predictions. In order to produce consistent, accurately replicable pulses for analysis, an artificial bat echolocation pulse was simulated, modeled on the FM pulse of a common pipistrelle bat ͑ Pipistrellus pipistrellus ͒ ͑ see Fig. 5 ͒ . The equation used to create this pulse, Y , over time t , is defined as: Y ͑ t ͒ = A ͑ t ͒ · ␭ ͑ t ͒ . ͑ 1 ͒ Time t is divided into four segments, t 0 : t 1 ; t 1 : t 2 ; t 2 : t 3 and t 3 : t end . The amplitude modulation of the pulse, A ͑ t ͒ , is varied over three portions of the pulse and is defined ...

Citations

... The laser receiver (photo-detector, D) receives the reference signal and the coherent signal. After demodulation, filtering and some signal processing steps are performed to obtain the voice signal [1]. As laser speech detection systems use lasers for voice measurement, they can detect speech in non-contact situations, undertake long−range measurements and are easy to conceal and operate [2]. ...
Article
Full-text available
Laser speech measurement is a new sound capture technology based on Laser Doppler Vibrometry (LDV). It avoids the need for contact, is easily concealed and is ideal for remote speech acquisition, which has led to its wide-scale adoption for military and security applications. However, lasers are easily affected by complex detection environments. Thus, speckle noise often appears in the measured speech, seriously affecting its quality and intelligibility. This paper examines all of the characteristics of impulsive noise in laser measured speech and proposes a novel automatic impulsive noise detection and removal method. This method first foregrounds noise using decorrelation based on a linear prediction (LP) model that improves the noise-to-signal ratio (NSR) of the measured signal. This makes it possible to detect the position of noise through a combination of the average short-time energy and kurtosis. The method not only precisely locates small clicks (with a duration of just a few samples), but also finds the location of longer bursts and scratches (with a duration of up to a hundred samples). The located samples can then be replaced by more appropriate samples whose coding is based on the LP model. This strategy avoids unnecessary processing and obviates the need to compromise the quality of the relatively large fraction of samples that are unaffected by speckle noise. Experimental results show that the proposed automatic speckle noise detection and removal method outperforms other related methods across a wide range of degraded audio signals.
... At a higher rotor velocity, the distance maintained by the bats to the SWT and the reference pole was similar. This behavior may have been due to a disruption of echolocation calls with increasing rotor speed [27,28], which hindered a closer examination by the bats. ...
Article
Full-text available
Small wind turbines (SWTs) have become increasingly common within the last decade, but their impact on wildlife, especially bats, is largely unknown. We conducted an operational experiment by sequentially placing a mobile SWT with five different operational modes at six sites of high bat activity, including roosts, commuting structures, and highly frequented hunting areas. Bat flight trajectories around the SWT were documented at each site during five consecutive nights using a specifically designed high-spatial-resolution 3D camera. The recordings showed high bat activity levels close to the SWT (7,065 flight trajectories within a 10-m radius). The minimum distance to the rotor of each trajectory varied between 0 and 18 m, with a mean of 4.6 m across all sites. Linear mixed models created to account for site differences showed that, compared to a reference pole without a SWT, bats flew 0.4 m closer to the rotor (95% CI 0.3–0.6 m) if it was out of operation and 0.3 m closer (95% CI 0.1–0.4 m) if it was moving slowly. Exploratory behavior was frequently observed, with many bats deviating from their original flight trajectory to approach the rotor. Among 7,850 documented trajectories, 176 crossed the rotor, including 65 while it was in motion. The collision of one P . pygmaeus individual occurred during the experiment. These results demonstrate that, despite the generally strong ability of bats to evade moving rotor blades, bat casualties at SWTs placed at sites of high bat activity can reach or exceed the current threshold levels set for large wind turbines. As SWTs provide less energy than large turbines, their negative impact on bats should be minimized by avoidance measures such as a bat-friendly site selection or curtailment algorithms.
... Fast rotating objects scatter the incoming echolocation call in a way that the information of the back-scattered echo is not usable for the bat. Two British research projects show concurring results as they investigated characteristics of scattered echos from rotation blades (Long et al., 2009;Long et al., 2010). The authors focused sound sources from different angles on a moving rotor (diameter 0.9 m, tip velocity 4 − 5 m/s). ...
Thesis
Localizing bats is a common task in many research projects. But working in the field with this equipment is often challenging since these tracking devices consist of numerous parts, require calibration and power supplies. Many researchers even have no access to localization instruments due their price and availability. This thesis describes new approaches for localizing bats. An eight channel microphone array which does not require laptops or computers and runs entirely on battery power was developed from scratch, from new low cost and small size microphones over the analog-to-digital conversion up to the software and hardware implementation of real-time detection and recording of all channels. The resulting system allowed sampling eight channels simultaneously with 1MHz at 16 bit and running 50 h on battery while real-time detecting echolocation calls. A second method to localize bats during the absence of light are near infrared video recordings. Based on the popular Raspberry Pi single board computer, a low cost stereo camera system is introduced that enables localization of bats in the field at minimum costs. Ten stereo-infrared cameras were assembled to asses flight behavior of bats around small wind turbines in northern and southern Germany. An object detection was implemented that allowed processing of nearly 550 h of stereo video and triangulate all detections resulting in three dimensional flight trajectories.
... For example, red aviation lights on top of turbine towers have been considered a pos si ble attractant to bats; however, studies have shown that bat mortality at towers with aviation lights is similar to or even lower than mortality at towers without aviation lights , Baerwald 2008, Bennett and Hale 2014). Another possibility is that bats are attracted to noises generated from the blades or nacelle, blade movement, or Doppler effects resulting from blade movement (Long et al. 2009(Long et al. , 2010. ...
... En effet, il a été montré que la rotation des pales des éoliennes provoque des change ments de fréquence et d'intensité des ultrasons produits par les chauvessouris (Long et al., 2009(Long et al., et 2010. Par conséquent, l'écho renvoyé est difficilement interprétable. ...
... L'émission d'un très grand nombre de signaux -plus de 50 -depuis le même angle serait nécessaire pour que l'individu assimile correctement le mouvement des pales. Mais cela semble impossible au vu du comportement de vol d'une chauvesouris (Long et al., 2010). ...
... Cette impossibilité de détecter les pales en mouvement, couplée à cette attractivité des éoliennes, constitue un piège efficace et mortel pour les chiroptères. Même si ce phé nomène n'a été étudié qu'avec des machines de petit gabarit, il paraît vraisemblable qu'il soit similaire voire plus important avec des rotors de plus grande taille (Long et al., 2009(Long et al., et 2010. ...
Technical Report
Full-text available
La LPO et l'ONCFS présentent au sein d’un seul et même ouvrage les résultats de dizaines d’années de travaux scientifiques menés à travers le monde. Le document se focalise sur l’éolien terrestre, le seul mis en œuvre de manière commerciale en France pour le moment. Il permet de mieux appréhender les deux principales menaces que représentent les éoliennes pour les oiseaux et les chauves-souris : le risque de collision, pour les espèces ayant des difficultés à détecter ou à éviter les éoliennes, voire qui sont attirées par elles, et le dérangement que les parcs peuvent engendrer, qui s’apparente à une perte d’habitat. L’ouvrage propose des solutions et recense en outre les lacunes dans nos connaissances, se voulant ainsi une feuille de route pour la poursuite des études scientifiques dans les années à venir.
... Although the mechanism for any avoidance behaviour is unclear, experimental studies in a laboratory setting have shown that the return of echolocation pulses off spinning turbine blades may be erratic, potentially causing navigational problems for bats (Long, Flint & Lepper, 2010). Alternatively, some bats may avoid foraging in noisy environments (Schaub, Ostwald & Siemers, 2008), but whether noise generated by turbines (including SWTs) has this effect has not been tested. ...
Article
While the effects of wind farms on bats are widely studied, effects of small wind turbines (SWTs, here <25 m hub height) remain understudied. SWTs are installed in a wider range of habitats compared to wind farms and their effect on wildlife can therefore be different. While single SWTs can adversely affect bat activity in their immediate vicinity, they are often installed in clusters, and to date, no data are available on whether installation of more than one turbine increases the likelihood of adverse effects on bats. Here, we test whether (1) SWT installations affect the activity of two species of bat (the common pipistrelle Pipistrellus pipistrellus and soprano pipistrelle P. pygmaeus) on a landscape scale (here defined as up to 500 m from SWTs) and (2) such an effect is stronger when multiple (2–4) SWTs are installed. We show that, after accounting for potentially confounding effects (e.g. variation in habitat and weather), (1) mean P. pipistrellus activity is lower at 0–100 m compared to 200–500 m from SWTs and (2) the effect on P. pygmaeus activity tends to be similar and stronger in multiple SWT sites, although evidence for the latter is limited. We conclude that in some cases, adverse effects of SWTs on bat activity may be measurable over longer spatial scales (within 100 m) than previously thought. However, combined with earlier findings, it is likely that the bulk of such effects operate within relative close proximity of SWTs (<25 m). Moreover, although these effects may be species-specific, with, for example, P. pygmaeus potentially more strongly affected by multiple SWT sites, this requires further data. These findings are highly relevant to decision-making aimed at minimizing any adverse effects of wind turbines, specifically single- versus multiple SWT developments, on wildlife.
... Such attraction could be either direct or indirect (Kunz et al., 2007;Cryan and Barclay, 2009). For example, the bats may be attracted by the turbines themselves, including their color (Long et al., 2011) or the aviation warning lights (Horn et al., 2008), or the heat, noise, electric fields or Dopplereffects caused by the generator or by the movement of the rotor (Long et al., 2010). Alternatively, attraction to the turbines is indirect, and relates to resources provided at the turbine tower, including insects on which the bats may feed (Kunz et al., 2007, Rydell et al., 2010b or roosting or mating opportunities, as the bats 'mistake' turbines for trees that may provide roosting or mating sites (Cryan, 2008). ...
Article
Full-text available
Activity of bats at an old wind park four km off the island of Gotland in the Baltic Sea was monitored during 50 nights from August to October 2013, using an automatic bat detector (Pettersson D500-X) mounted on one of the turbines. Single individuals or pairs of common noctules Nyctalus noctula were recorded on five occasions only (26 and 27 August), all in calm weather and when little or no rotor movement occurred. Since such conditions were unusual (five of 50 nights of observation) the visits by the bats were unlikely to be chance events (migrating bats passing the turbine), but more likely involved bats attracted to the turbines. However, no feeding buzzes were recorded and the bats never stayed near the turbine more than one minute. The turbines studied are lit by 250 W white lights and this could have been the reason why bats visited the turbines, because such lights potentially attract insects. The bats could not have been attracted to the turbines by any factor related of the movement of the rotor or the generator, such as Doppler-effects, noise, heat or electric fields.
... In this context, it is extremely important to understand which conditions influence bat mortality at wind farms. Most published data about bats and wind farms are derived from studies conducted in North America (e.g., Kunz et al., 2007aKunz et al., , 2007bArnett et al., 2008;Baerwald et al., 2008;Horn et al., 2008;Baerwald and Barclay, 2009) and, to a much lesser extent, in northern and western Europe (e.g., Nichols and Racey, 2009;Long et al., 2010;Rydell et al., 2010aRydell et al., , 2010b. Most European data, and particularly data from the Mediterranean region, remain unpublished. ...
Article
Full-text available
Our study aims to determine how different climatic variables influence bat activity and mortality at wind farms in Portugal. The study was conducted from March to October 2007 at a wind farm with 20 turbines located in Northern Portugal. Bat activity was determined by ground bounded acoustic sampling, while mortality was assessed through fatality searches around each turbine. Sampling occurred weekly and activity was measured the night before fatality search. The highest activity and mortality rates were from Nyctalus leisleri and Pipistrellus pipistrellus. The majority of activity and mortality (95% and 94% in that order) occurred from August to October and both were significantly correlated with wind speed, temperature and relative humidity; mortality also appeared to be influenced by wind direction. Our results show that it is possible to establish a relationship between ground bounded activity and mortality. Our results are relevant for the implementation of effective minimization measures and, therefore, for bat conservation in the Mediterranean region. Specifically, our results show that nearly all (94%) of bat mortality at wind farms happens from August to October, at temperatures higher than 13.0ºC, and wind speeds lower than 5.0 m.s-1.
... By contrast, we suggest bat activity may be lowered by SWT operation for a variety of reasons. Firstly, there is experimental evidence that the reflection of echolocation pulses off spinning SWT blades can be erratic [39], therefore affecting detection and possibly causing echolocating bats to avoid poorly detected (and thus potentially risky) objects. Alternatively, foraging behaviour and feeding success of some bat species may be affected by ambient noise [40]. ...
Article
Full-text available
The development of renewable energy technologies such as wind turbines forms a vital part of strategies to reduce greenhouse gas emissions worldwide. Although large wind farms generate the majority of wind energy, the small wind turbine (SWT, units generating <50 kW) sector is growing rapidly. In spite of evidence of effects of large wind farms on birds and bats, effects of SWTs on wildlife have not been studied and are likely to be different due to their potential siting in a wider range of habitats. We present the first study to quantify the effects of SWTs on birds and bats. Using a field experiment, we show that bird activity is similar in two distance bands surrounding a sample of SWTs (between 6-18 m hub height) and is not affected by SWT operation at the fine scale studied. At shorter distances from operating turbines (0-5 m), bat activity (measured as the probability of a bat "pass" per hour) decreases from 84% (71-91%) to 28% (11-54%) as wind speed increases from 0 to 14 m/s. This effect is weaker at greater distances (20-25 m) from operating turbines (activity decreases from 80% (65-89%) to 59% (32-81%)), and absent when they are braked. We conclude that bats avoid operating SWTs but that this effect diminishes within 20 m. Such displacement effects may have important consequences especially in landscapes where suitable habitat is limiting. Planning guidance for SWTs is currently lacking. Based on our results we recommend that they are sited at least 20 m away from potentially valuable bat habitat.
... However, some wind energy facilities have been responsible for the death of large numbers of migratory bats (e.g. Johnson et al. 2003, Baerwald et al. 2008, Jana & Pogacnik 2008, Long et al. 2010, Rydell et al. 2010. Climate change may also indirectly alter prey-predator dynamics. ...
Article
Climate influences the biogeography of bats, their access to food, timing of hibernation, reproduction and development, frequency and duration of torpor and rate of energy expenditure. Empirical data on the impact of climate change on bats are a cause for concern as current increases in global temperature are one fifth, or less, of those expected over the next century. We review observed impacts of climate change on bats and identify risk factors allowing species‐specific predictions. The impact on species is reviewed in relation to six aspects, namely foraging, roosting, reproduction, biogeography, extreme weather events and indirect effects of climate change. For some aspects of species' ecology, there are insufficient data available to make accurate assessment of impacts. We identify seven risk factors encompassing three broad aspects: biogeography – small range size, high latitude or high altitude range and a range occupying a geographic area likely to become water stressed; foraging niche – frugivory and species restricted to aerial hawking; dispersal ability – species with restricted dispersal behaviour. We use the European and north‐west African bats as a case study to assess the relative risk of climate change to individual species. Risk scores are compared with existing International U nion for C onservation of N ature conservation assessments providing further insight into the conservation outlook for individual species. We provide a base for C hiroptera to be incorporated into future frameworks of risk assessment and identify areas that require further research.