Environmental impact of wind power

The environmental impact of wind power, when compared to the environmental impacts of fossil fuels, is relatively minor. According to the IPCC, in assessments of the life-cycle global warming potential of energy sources, wind turbines have a median value of between 12 and 11 (geq/kWh) depending, respectively, on if offshore or onshore turbines are being assessed. Compared with other low carbon power sources, wind turbines have some of the lowest global warming potential per unit of electrical energy generated.Begoña Guezuraga, Rudolf Zauner, Werner Pölz, Life cycle assessment of two different 2 MW class wind turbines, Renewable Energy 37 (2012) 37-44, p 37. 
While a wind farm may cover a large area of land, many land uses such as agriculture are compatible with it, as only small areas of turbine foundations and infrastructure are made unavailable for use.
There are reports of bird and bat mortality at wind turbines as there are around other artificial structures. The scale of the ecological impact may or may not be significant, depending on specific circumstances. Prevention and mitigation of wildlife fatalities, and protection of peat bogs affect the siting and operation of wind turbines.
There are anecdotal reports of negative health effects from noise on people who live very close to wind turbines. Peer-reviewed research has generally not supported these claims.
Wind turbines have been criticised as having a visual impact on the landscape. When conflicts arise the arguments often centre on the scenic and heritage values of a landscapes. However, surveys consistently show that most people are not concerned about the look of wind turbines.
One megawatt wind turbine can save 21,600 tons of a year, 29,970,000,000,000/17 btu's of energy, 1,387,500/187 tons of , 360,000,000 gallons of , gain almost 117,000 tons of per year (equal to 900,000 trees)
== Basic operational considerations ==
=== Net energy gain ===
Modern wind turbine systems have a net energy gain, in other words during their service life they produce more energy than is used to build the system. Any practical large-scale energy source must produce more energy than is used in its construction. The energy return on investment (EROI) for wind energy is equal to the cumulative electricity generated divided by the cumulative primary energy required to build and maintain a turbine. According to a meta study, in which all existing studies from 1977 to 2007 were reviewed, the EROI for wind ranges from 5 to 35, with the most common turbines in the range of 2 MW nameplate capacity-rotor diameters of 66 meters, the EROI is on average 16.Dailykos - GETTING TO ZERO: Is renewable energy economically viable? by Keith Pickering MON JUL 08, 2013 AT 04:30 AM PDT. EROI is strongly proportional to turbine size, and larger late-generation turbines average at the high end of this range, at or above 35. Since energy produced is several times energy consumed in construction, there is a net energy gain. Wind turbine manufacturer Vestas claims that initial energy "pay back" is within about 7–9 months of operation for a 1.65-2.0MW wind power plant under low wind conditions, whereas Siemens Wind Power calculates 5–10 months depending on circumstances.Wittrup, Sanne. "6 MW vindmølle betaler sig energimæssigt tilbage 33 gange" English translation Ingeniøren, 26 November 2014. Accessed: 27 November 2014.
=== Carbon dioxide emissions ===
Wind power consumes no fuel and no water for continuing operation, and has no emissions directly related to electricity production. Wind turbines produce no , carbon monoxide, , , , radioactive waste, particulates, , , , or any other type of air pollution, unlike fossil fuel sources and nuclear power plant fuel production.
A meta study from 2009 shows impacts of 5-20 grams per kWh.Anders Arvesen, Åsa Grytli Tveten, Edgar G. Hertwich, Anders Hammer Strømman. "Life-cycle assessments of wind energy systems" Norwegian University of Science and Technology, 2009. Accessed: 27 November 2014.
A 2006 study of 3 installations in the US Midwest found the emissions of wind power ranged from per GWh of energy produced. Most of the emission came from producing the concrete for wind-turbine foundations. A study by the Irish national grid stated that "Producing electricity from wind reduces the consumption of fossil fuels and therefore leads to emissions savings", and found reductions in emissions ranging from of per MWh.
=== Rare-earth use ===
The production of permanent magnets used in some wind turbines makes use of neodymium. Primarily exported by China, pollution concerns associated with the extraction of this rare-earth element have prompted government action in recent years, and international research attempts to refine the extraction process. Research is underway on turbine and generator designs which reduce the need for neodymium, or eliminate the use of rare-earth metals altogether. Additionally, the large wind turbine manufacturer Enercon GmbH chose very early not to use permanent magnets for its direct drive turbines, in order to avoid responsibility for the adverse environmental impact of rare earth mining.
== Ecology ==
=== Land use ===
Wind farms are often built on land that has already been impacted by land clearing. The vegetation clearing and ground disturbance required for wind farms is minimal compared with coal mines and coal-fired power stations. If wind farms are decommissioned, the landscape can be returned to its previous condition.
A study by the US National Renewable Energy Laboratory of US wind farms built between 2000 and 2009 found that, on average, only 1.1 percent of the total wind farm area suffered surface disturbance, and only 0.43 percent was permanently disturbed by wind power installations. On average, there were 63 hectares (156 acres) of total wind farm area per MW of capacity, but only 0.27 hectares (0.67 acres) of permanently disturbed area per MW of wind power capacity. Paul Denholm, Maureen Hand, Maddalena Jackson, and Sean Ong, Land-Use Requirements of Modern Wind Power Plants in the United States, National Renewable Energy Laboratory, NREL/TP-6A2-45834, Aug. 2009. 
In the UK many prime wind farm sites - locations with the best average wind speeds - are in upland areas which are frequently covered by blanket bog. This type of habitat exists in areas of relatively high rainfall where large areas of land remain permanently sodden. Construction work may create a risk of disruption to peatland hydrology which could cause localised areas of peat within the area of a wind farm to dry out, disintegrate, and so release their stored carbon. At the same time, the warming climate which renewable energy schemes seek to mitigate could itself pose an existential threat to peatlands throughout the UK.
thumb|right|In the United States, landowners typically receive $3,000 to $5,000 per year in rental income from each wind turbine, while farmers continue to grow crops or graze cattle up to the foot of the turbines.American Wind Energy Association (2009). [http://www.awea.org/publications/reports/AWEA-Annual-Wind-Report-2009.pdf Annual Wind Industry Report, Year Ending 2008] pp. 9-10.
Farmers and graziers often lease land to companies building wind farms. In the U.S., landowners may receive annual lease payments of two thousand to five thousand dollars per turbine. In 2011, taxes, fees, and assessments of wind power facilities enabled Sherman County, Oregon to pay each landowner $590 per year "...to reward residents who have made no financial gains [directly] from wind energy development, but whose views of... [the] landscape now include a panorama of turbines".
The land can still be used for farming and cattle grazing. Livestock are unaffected by the presence of wind farms. International experience shows that livestock will "graze right up to the base of wind turbines and often use them as rubbing posts or for shade".
Wind-energy advocates contend that less than 1% of the land is used for foundations and access roads, the other 99% can still be used for farming. A wind turbine needs about 200–400 m² for the foundation. A (small) 500-kW-turbine with an annual production of 1.4 GWh produces 11.7 MWh/m², which is comparable with coal-fired plants (about 15-20 MWh/m²), coal-mining not included. With increasing size of the wind turbine the relative size of the foundation decreases. Critics point out that on some locations in forests the clearing of trees around tower bases may be necessary for installation sites on mountain ridges, such as in the northeastern U.S. This usually takes the clearing of 5,000 m² per wind turbine.
Turbines are not generally installed in urban areas. Buildings interfere with wind, turbines must be sited a safe distance ("setback") from residences in case of failure, and the value of land is high. There are a few notable exceptions to this. The WindShare ExPlace wind turbine was erected in December 2002, on the grounds of Exhibition Place, in Toronto, Canada. It was the first wind turbine installed in a major North American urban city centre. Steel Winds also has a 20 MW urban project south of Buffalo, New York. Both of these projects are in urban locations, but benefit from being on uninhabited lake shore property.
In the UK there has also been concern about the damage caused to peat bogs, with one Scottish MEP campaigning for a moratorium on wind developments on peatlands saying that "Damaging the peat causes the release of more carbon dioxide than wind farms save".
=== Impact on wildlife ===
Environmental assessments are routinely carried out for wind farm proposals, and potential impacts on the local environment (e.g. plants, animals, soils) are evaluated. Turbine locations and operations are often modified as part of the approval process to avoid or minimise impacts on threatened species and their habitats. Any unavoidable impacts can be offset with conservation improvements of similar ecosystems which are unaffected by the proposal.
A research agenda from a coalition of researchers from universities, industry, and government, supported by the Atkinson Center for a Sustainable Future, suggests modeling the spatiotemporal patterns of migratory and residential wildlife with respect to geographic features and weather, to provide a basis for science-based decisions about where to site new wind projects. More specifically, it suggests:
* Use existing data on migratory and other movements of wildlife to develop predictive models of risk.
* Use new and emerging technologies, including radar, acoustics, and thermal imaging, to fill gaps in knowledge of wildlife movements.
* Identify specific species or sets of species most at risk in areas of high potential wind resoures.
==== Birds ====
 Causes of avian mortality in the United States, annual
Source 	Estimated mortality(in millions)	Estimated deaths(per GWh)
Wind turbines 	0.02 – 0.57 	0.269
Aircraft 	0.08 	(n/a)
Nuclear power plants 	0.33 	0.416
Oilfield oil waste & waste water pits 	0.50 – 1 	(n/a)
Nuisance bird control kills (airports, agriculture, etc...)	2 	(n/a)
Communication towers (cellular, radio, microwave) 	4 – 50 	(n/a)
Large communications towers (over 180', N. America) 	6.8 	(n/a)
Fossil fuel powerplants 	14 	5.18
Cars & trucks 	50 – 100 	(n/a)
Agriculture 	67 	(n/a)
Pesticide use 	72 	(n/a)
Hunting 	100 – 120 	(n/a)
Transmission lines (conventional powerplants) 	174 – 175 	(n/a)
Buildings and windows 	365 – 988 	(n/a)
Domestic and feral cats 	210 – 3,700 	(n/a)
The impact of wind energy on birds, which can fly into turbines directly, or indirectly have their habitats degraded by wind development, is complex. Projects such as the Black Law Wind Farm have received wide recognition for its contribution to environmental objectives, including praise from the Royal Society for the Protection of Birds, who describe the scheme as both improving the landscape of a derelict opencast mining site and also benefiting a range of wildlife in the area, with an extensive habitat management projects covering over 14 square kilometres.
The meta-analysis on avian mortality by Benjamin K. Sovacool led him to suggest that there were a number of deficiencies in other researchers' methodologies. Among them, he stated were a focus on bird deaths, but not on the reductions in bird births: for example, mining activities for fossil fuels and pollution from fossil fuel plants have led to significant toxic deposits and acid rain that have damaged or poisoned many nesting and feeding grounds, leading to reductions in births. The large cumulated footprint of wind turbines, which reduces the area available to wildlife or agriculture, is also missing from all studies including Sovacool's. Many of the studies also made no mention of avian deaths per unit of electricity produced, which excluded meaningful comparisons between different energy sources. More importantly, it concluded, the most visible impacts of a technology, as measured by media exposure, are not necessarily the most flagrant ones.
The Sovacool study did a broad assessment of anthropogenic causes of avian mortality and brought together many studies on deaths due to wind energy, fossil fuel energy and nuclear energy. He estimated a figure for bird deaths due to wind power of 0.269 fatalities per gigawatt-hour (GWh), by which he extrapolated a total of 7193 US bird fatalities in 2006. He concluded that wind farms and nuclear power stations are responsible each for between 0.3 and 0.4 fatalities per gigawatt-hour (GWh) of electricity while fossil-fueled power stations are responsible for about 5.2 fatalities per GWh. Of the bird deaths Sovacool attributed to fossil-fuel power plants, 96 percent were due to the effects of climate change. While the study did not assess bat mortality due to various forms of energy, he considered it not unreasonable to assume a similar ratio of mortality. The Sovacool study has provoked controversy because of its treatment of data. In a series of replies, Sovacool acknowledged a number of large errors, particularly those that relate to a 0.4 fatalities overestimate for the number of bird deaths per GWh of nuclear power, and cautioned that "the study already tells you the numbers are very rough estimates that need to be improved.""… the study already tells you the numbers are very rough estimates that need to be improved. I even explicitly state this, as well, in the conclusion: ‘the rudimentary numbers presented here are intended to provoke further research and discussion,’ in the abstract ‘this paper should be respected as a preliminary assessment,’ and in the title of the study, which has the word ‘preliminary’ in it...you are correct that errors 1 and 2 are true..." Benjamin Sovacool, Benjamin Sovacool takes issue with Lorenzini’s criticism of his work, Atomic Insights website, 11 July 2013.
Sovacool estimated that in the United States wind turbines kill between 20,000 and 573,000 birds per year, and although he states either figure is minimal compared to bird deaths from other causes. He uses the lower 20,000 figure in his study and table (see Causes of avian mortality table). Fossil-fueled power plants, which wind turbines generally require to make up for their weather dependent intermittency, kill almost 20 times as many birds per gigawatt hour (GWh) of electricity. Bird deaths due to other human activities and cats total between 797 million and 5.29 billion per year in the U.S. Additionally, while many studies concentrate on the analysis of bird deaths, few have been conducted on the reductions of bird births, which are the additional consequences of the various pollution sources that wind power partially mitigates.
A 2013 meta-analysis by Smallwood identified a number of factors which result in serious under-reporting of bird and bat deaths by wind turbines. These include inefficient searches, inadequate search radius, and carcass removal by predators. To adjust the results of different studies, he applied correction factors from hundreds of carcass placement trials. His meta-analysis concluded that in 2012 in the United States, wind turbines resulted in the deaths of 888,000 bats and 573,000 birds, including 83,000 raptors.K. Shawn Smallwood, "Comparing bird and bat fatality-rate estimates among North American wind-energy projects", Wildlife Society Bulletin, 26 Mar. 2013.
Also in 2013, a meta-analysis by Lossa and others in the journal Biological Conservation found that the likely mean number of birds killed annually in the U.S by wind turbines was 234,000. The authors acknowledged the larger number reported by Smallwood, but noted that Smallwood’s meta-analysis did not distinguish between types of wind turbine towers; older wind turbines were more often on lattice towers, which attract birds. The monopole towers used almost exclusively for new wind installations appear to result in fewer bird deaths.
Bird mortality at wind energy facilities can vary greatly depending on the facility's location, with some facilities reporting nearly zero bird fatalities, and others as high as four birds per turbine per year. An article in the journal Nature stated that each wind turbine in the U.S. kills an average of 0.03 birds per year, and recommends that more research needs to be done.
Wind facilities have attracted the most attention for impacts on iconic raptor species, including golden eagles. The Pine Tree Wind energy project near Tehachapi, California has one of the highest raptor mortality rates in the country; by 2012 at least eight golden eagles had been killed according to the U.S. Fish and Wildlife Service (USFWS). Biologists have noted that it is more important to avoid losses of large birds as they have lower breeding rates and can be more severely impacted by wind turbines in certain areas.
Large numbers of bird deaths are also attributed to collisions with buildings. An estimated 1 to 9 million birds are killed every year by tall buildings in Toronto, Canada alone, according to the wildlife conservation organization Fatal Light Awareness Program. Other studies have stated that 57 million are killed by cars, and some 365 to 988 million are killed by collisions with buildings and plate glass in the United States alone. Promotional event lightbeams as well as ceilometers used at airport weather offices can be particularly deadly for birds, as birds become caught in their lightbeams and suffer exhaustion and collisions with other birds. In the worst recorded ceilometer lightbeam kill-off during one night in 1954, approximately 50,000 birds from 53 different species died at the Warner Robins Air Force Base in the United States.
In the United Kingdom, the Royal Society for the Protection of Birds (RSPB) concluded that "The available evidence suggests that appropriately positioned wind farms do not pose a significant hazard for birds." It notes that climate change poses a much more significant threat to wildlife, and therefore supports wind farms and other forms of renewable energy as a way to mitigate future damage. In 2009 the RSPB warned that "numbers of several breeding birds of high conservation concern are reduced close to wind turbines" probably because "birds may use areas close to the turbines less often than would be expected, potentially reducing the wildlife carrying capacity of an area.
Concerns have been expressed that wind turbines at Smøla, Norway are having a deleterious effect on the population of white-tailed eagles, Europe's largest bird of prey. They have been the subject of an extensive re-introduction programme in Scotland, which could be jeopardised by the expansion of wind turbines.
The Peñascal Wind Power Project in Texas is located in the middle of a major bird migration route, and the wind farm uses avian radar originally developed for NASA and the United States Air Force to detect birds as far as away. If the system determines that the birds are in danger of running into the rotating blades, the turbines shut down and are restarted when the birds have passed. A 2005 Danish study used surveillance radar to track migrating birds traveling around and through an offshore wind farm. Less than 1% of migrating birds passing through an offshore wind farm in Rønde, Denmark, got close enough to be at risk of collision, though the site was studied only during low-wind conditions. The study suggests that migrating birds may avoid large turbines, at least in the low-wind conditions the research was conducted in.
In 2012, researchers reported that, based on their four-year radar tracking study of birds after construction of an offshore wind farm near Lincolnshire, that pink-footed geese migrating to the U.K. to overwinter altered their flight path to avoid the turbines.
At the Altamont Pass Wind Farm in California, a settlement between the Audubon Society, Californians for Renewable Energy and NextEra Energy Resources who operate some 5,000 turbines in the area requires the latter to replace nearly half of the smaller turbines with newer, more bird-friendly models by 2015 and provide $2.5 million for raptor habitat restoration. The proposed Chokecherry and Sierra Madre Wind project in Wyoming, however, is expected to kill nearly 5,400 birds each year, including over 150 raptors, according to a Bureau of Land Management environmental analysis.
==== Bats ====
Bats may be injured by direct impact with turbine blades, towers, or transmission lines. Recent research shows that bats may also be killed when suddenly passing through a low air pressure region surrounding the turbine blade tips.
The numbers of bats killed by existing onshore and near-shore facilities have troubled bat enthusiasts.
In April 2009 the Bats and Wind Energy Cooperative released initial study results showing a 73% drop in bat fatalities when wind farm operations are stopped during low wind conditions, when bats are most active. Bats avoid radar transmitters, and placing microwave transmitters on wind turbine towers may reduce the number of bat collisions.
A 2013 study produced an estimate that wind turbines killed more than 600,000 bats in the U.S. the previous year, with the greatest mortality occurring in the Appalachian Mountains. Some earlier studies had produced estimates of between 33,000 and 888,000 bat deaths per year.
==== Livestock ====
In 2014, a first of its kind Veterinary study attempted to determine the effects of rearing livestock near a wind turbine, the study compared the health effects of a wind turbine on the development of two groups of growing geese, preliminary results found that geese raised within 50 meters of a wind turbine gained less weight and had a higher concentration of cortisol in their blood than geese at a distance of 500 meters.
=== Weather and climate change ===
Wind farms may affect weather in their immediate vicinity. This turbulence from spinning wind turbine rotors increases vertical mixing of heat and water vapor that affects the meteorological conditions downwind. Overall, wind farms lead to a slight warming at night and a slight cooling during the day time. This effect can be reduced by using more efficient rotors or placing wind farms in regions with high natural turbulence. Warming at night could "benefit agriculture by decreasing frost damage and extending the growing season. Many farmers already do this with air circulators".
A number of studies have used climate models to study the effect of extremely large wind farms. One study reports simulations that show detectable changes in global climate for very high wind farm usage, on the order of 10% of the world's land area. Wind power has a negligible effect on global mean surface temperature, and it would deliver "enormous global benefits by reducing emissions of and air pollutants". Another peer-reviewed study suggested that using wind turbines to meet 10 percent of global energy demand in 2100 could actually have a warming effect, causing temperatures to rise by in the regions on land where the wind farms are installed, including a smaller increase in areas beyond those regions. This is due to the effect of wind turbines on both horizontal and vertical atmospheric circulation. Whilst turbines installed in water would have a cooling effect, the net impact on global surface temperatures would be an increase of . Author Ron Prinn cautioned against interpreting the study "as an argument against wind power, urging that it be used to guide future research". "We’re not pessimistic about wind," he said. "We haven’t absolutely proven this effect, and we’d rather see that people do further research".
== Impacts on people ==
=== Aesthetics ===
Aesthetic considerations of wind power stations have often a significant role in their evaluation process.Thomas Kirchhoff (2014): Energiewende und Landschaftsästhetik. Versachlichung ästhetischer Bewertungen von Energieanlagen durch Bezugnahme auf drei intersubjektive Landschaftsideale, in: Naturschutz und Landschaftsplanung 46 (1), 10-16. To some, the perceived aesthetic aspects of wind power stations may conflict with the protection of historical sites.Tourismus und Regionalentwicklung in Bayern, Diana Schödl, Windkraft und Tourismus – planerische Erfassung der Konfliktbereiche, in Marius Mayer, Hubert Job, 05.12.2013, Arbeitsgruppe „Tourismus und Regionalentwicklung" der Landesarbeitsgemeinschaft Bayern der ARL, p 125. ff Wind power stations are less likely to be perceived negatively in urbanized and industrial regions.Günter Ratzbor (2011): Windenergieanlagen und Landschaftsbild. Zur Auswirkung von Windrädern auf das Landschaftsbild. Thesenpapier des Deutschen Naturschutzrings DNR, p. 17-19 Aesthetic issues are subjective and some people find wind farms pleasant or see them as symbols of energy independence and local prosperity. While studies in Scotland predict wind farms will damage tourism, in other countries some wind farms have themselves become tourist attractions, with several having visitor centers at ground level or even observation decks atop turbine towers.
In the 1980s, wind energy was being discussed as part of a soft energy path.Windenergie in Deutschland: Konstellationen, Dynamiken und Regulierungspotenziale Im Innovationsprozess, Bö Ohlhorst, Springer-Verlag, 2009, p.90 ff Renewable energy commercialization led to an increasing industrial image of wind power, which is being criticized by various stakeholders in the planning process, including nature protection associations.Windenergie in Deutschland: Konstellationen, Dynamiken und Regulierungspotenziale Im Innovationsprozess, Bö Ohlhorst, Springer-Verlag, 2009, p.163, "Kritik an zunehmend industrieller Charakter der Windenergienutzung" Newer wind farms have larger, more widely spaced turbines, and have a less cluttered appearance than older installations. Wind farms are often built on land that has already been impacted by land clearing and they coexist easily with other land uses.
Coastal areas and areas of higher altitude such as ridgelines are considered prime for wind farms, due to constant wind speeds. However both locations tend to be areas of high visual impact and can be a contributing factor in local communities' resistance to some projects. Both the proximity to densely populated areas and the necessary wind speeds make coastal locations ideal for wind farms.Dipert, Brian. Cutting the carbon-energy cord: Is the answer blowin' in the wind?, EDN Network website, December 15, 2006.
 
Wind power stations can impact on important sight relations which are a key part of culturally important landscapes, such as in the Rhine Gorge or Moselle valley. Conflicts between heritage status of certain areas and wind power projects have arisen in various countries. In 2011 UNESCO raised concerns regarding a proposed wind farm 17 kilometres away of the French island abbey of Mont-Saint-Michel.UNESCO's Wind Turbine Problem: Mont-Saint-Michel's World Heritage Status Under Threat, Stefan Simons, Der Spiegel In Germany, the impact of wind farms on valuable cultural landscapes has implications on zoning and land-use planning.Sören Schöbel (2012): Windenergie und Landschaftsästhetik: Zur landschaftsgerechten Anordnung von Windfarmen, Jovis-Verlag, BerlinNohl, Werner (2009): Landschaftsästhetische Auswirkungen von Windkraftanlagen, p.2, 8 For example sensitive parts of the Moselle valley and the background of the Hambach Castle, according to the plans of the state government, will be kept free of wind turbines.Fittkau, Ludger: Ästhetik und Windräder, Neues Gutachten zu "Windenergienutzung und bedeutenden Kulturlandschaften" in Rheinland-Pfalz, Kultur heute, 30 July 2013
Wind turbines require aircraft warning lights, which may create light pollution. Complaints about these lights have caused the US FAA to consider allowing fewer lights per turbine in certain areas. Residents near turbines may complain of "shadow flicker" caused by rotating turbine blades, when the sun passes behind the turbine. This can be avoided by locating the wind farm to avoid unacceptable shadow flicker, or by turning the turbine off for the time of the day when the sun is at the angle that causes flicker. If a turbine is poorly sited and adjacent to many homes, the duration of shadow flicker on a neighbourhood can last hours.
=== Noise annoyance ===
Nina Pierpont, a New York pediatrician and wife of an anti-wind energy activist, states that noise can be an important disadvantage of wind turbines, especially when building the wind turbines very close to urban environments. The controversy around Pierpont's work centers around her statements made in a self-published, non-peer-reviewed book that ultra-low frequency sounds affect human health, which are based on a very small sample of self-selected subjects with no control group for comparison. She asserts that wind turbines affect the mood of people and may cause physiological problems such as insomnia, headaches, tinnitus, vertigo and nausea. Simon Chapman, professor of public health at Sydney University has said that "wind turbine syndrome" is not recognised by any international disease classification system and does not appear in any title or abstract in the massive US National Library of Medicine's PubMed database. He says that the term appears to be spread by anti-wind farm activist groups.
A 2007 report by the U.S. National Research Council noted that noise produced by wind turbines is generally not a major concern for humans beyond a half-mile or so. Low-frequency vibration and its effects on humans are not well understood and sensitivity to such vibration resulting from wind-turbine noise is highly variable among humans. There are opposing views on this subject, and more research needs to be done on the effects of low-frequency noise on humans.
A 2008 guest editorial in Environmental Health Perspectives published by the National Institute of Environmental Health Sciences, the U.S. National Institutes of Health, stated: "Even seemingly clean sources of energy can have implications on human health. Wind energy will undoubtedly create noise, which increases stress, which in turn increases the risk of cardiovascular disease and cancer."
A 2009 expert panel review, sponsored by the Canadian Wind Energy Association and American Wind Energy Association, delved into the possible adverse health effects of those living close to wind turbines. Their 85-page report concluded that wind turbines do not directly make people ill. The study did allow that some people could experience stress or irritation caused by the swishing sounds wind turbines produce. "A small minority of those exposed report annoyance and stress associated with noise perception..." [however] "Annoyance is not a disease." The study group pointed out that similar irritations are produced by local and highway vehicles, as well as from industrial operations and aircraft.
The 2009 study panel members included: Robert Dobie, a doctor and clinical professor at the University of Texas, Geoff Leventhall, a noise vibration and acoustics expert in the United Kingdom, Bo Sondergaard, with Danish Electronics Light and Acoustics, Michael Seilo, a professor of audiology at Western Washington University, and Robert McCunney, a biological engineering scientist at the Massachusetts Institute of Technology. McCunney contested statements that infrasounds from wind turbines could create vibrations causing ill health: "It doesn't really have much credence, at least based on the literature out there" he stated The academic and medical experts who conducted the study stated that they reached their conclusions independent of their sponsors. "We were not told to find anything," said panel expert David Colby, a public health officer in Chatham-Kent and a Professor of Medicine at the University of Western Ontario. "It was completely open ended."
In a 2009 report about "Rural Wind Farms", a Standing Committee of the Parliament of New South Wales, Australia, recommended a minimum setback of two kilometres between wind turbines and neighbouring houses (which can be waived by the affected neighbour) as a precautionary approach. In July 2010, Australia's National Health and Medical Research Council reported that "there is no published scientific evidence to support adverse effects of wind turbines on health".
In 2011, Simon Chapman wrote in the Sydney Morning Herald that the British Acoustics Bulletin had published the 10th independent review of the evidence on wind farms causing annoyance and ill health in people. The correct reference should be to a Literature Review by Dani Fiumicelli in the November/December 2011 edition of the Acoustic Bulletin. Chapman says that "annoyance has far more to do with social and psychological factors in those complaining than any direct effect from sound or inaudible infrasound emanating from wind turbines". Chapman went on to quote the review as saying that two factors repeatedly came up. "The first is being able to see wind turbines, which increases annoyance particularly in those who dislike or fear them. The second factor is whether people derive income from hosting turbines, which miraculously appears to be a highly effective antidote to feelings of annoyance and symptoms".
A 2011 literature review stated that wind turbines can be associated with some health effects, such as sleep disturbance, and argued that the health effects reported by those living near wind turbines were probably caused not by the turbines themselves but rather by "physical manifestation from an annoyed state."
Eighteen research reviews about wind turbines and health, published since 2003, all concluded that there was very little evidence that wind turbines were harmful in any direct way. Simon Chapman said that if wind farms did genuinely make people ill there would by now be a large body of medical literature that would preclude putting them near populated areas. But this is not the case. Sickness being attributed to wind turbines is more likely to be caused by people getting alarmed at the health warnings circulated by activists. Complaints of illness were far more prevalent in communities targeted by anti-wind groups. Chapman's report concludes "that illnesses being blamed on windfarms are more than likely caused by the psychological effect of suggestions that the turbines make people ill, rather than by the turbines themselves".
A meta study published in 2014 concluded:McCunney, Robert J. MD, MPH; Mundt, Kenneth A. PhD; Colby, W. David MD; Dobie, Robert MD; Kaliski, Kenneth BE, PE; Blais, Mark PsyD. Wind Turbines and Health: A Critical Review of the Scientific Literature Journal of Occupational and Environmental Medicine, November 2014 - Volume 56 - Issue 11 - p e108–e130 . 
*Infrasound is emitted by wind turbines. The levels of infrasound at customary distances to homes are typically well below audibility thresholds.
*Components of wind turbine sound, including infrasound and low-frequency sound, have not been shown to present unique health risks to people living near wind turbines.
*Among the cross-sectional studies of better quality, no clear or consistent association is seen between wind turbine noise and any reported disease or other indicator of harm to human health.
*Annoyance associated with living near wind turbines is a complex phenomenon related to personal factors. Noise from turbines plays a minor role in comparison with other factors in leading people to report annoyance in the context of wind turbines
In Ontario, Canada, the Ministry of the Environment created noise guidelines to limit wind turbine noise levels 30 metres away from a dwelling or campsite to 40 dB(A). These regulations also set a minimum distance of for a group of up to five relatively quiet [102 dB(A)] turbines within a radius, rising to for a group of 11 to 25 noisier (106-107 dB(A)) turbines. Larger facilities and noisier turbines would require a noise study.
Modern wind turbines produce significantly less noise than older designs. Turbine designers work to minimise noise, as noise reflects lost energy and output. Noise levels at nearby residences may be managed through the siting of turbines, the approvals process for wind farms, and operational management of the wind farm.
=== Safety ===
Some turbine nacelle fires cannot be extinguished because of their height, and are sometimes left to burn themselves out. In such cases they generate toxic fumes and can cause secondary fires below. However, newer wind turbines are built with automatic fire extinguishing systems similar to those provided for jet aircraft engines. These autonomous systems, which can be retrofitted to older wind turbines, automatically detect a fire, order the shut down of the turbine unit and immediately extinguish the fires completely.
During winter ice may form on turbine blades and subsequently be thrown off during operation. This is a potential safety hazard, and has led to localised shut-downs of turbines.
Modern turbines can detect ice formation and excess vibration during operations, and are shut down automatically. Electronic controllers and safety sub-systems monitor many different aspects of the turbine, generator, tower, and environment to determine if the turbine is operating in a safe manner within prescribed limits. These systems can temporarily shut down the turbine due to high wind, ice, electrical load imbalance, vibration, and other problems. Recurring or significant problems cause a system lockout and notify an engineer for inspection and repair. In addition, most systems include multiple passive safety systems that stop operation even if the electronic controller fails.
== Offshore ==
Many offshore wind farms have contributed to electricity needs in Europe and Asia for years, and as of 2014 the first offshore wind farms are under development in U.S. waters. While the offshore wind industry has grown dramatically over the last several decades, especially in Europe, there is still some uncertainty associated with how the construction and operation of these wind farms affect marine animals and the marine environment.Rodmell, D. & Johnson, M., 2002. The development of marine based wind energy generation and inshore fisheries in UK waters: Are they compatible? In M. Johnson & P. Hart, eds. Who owns the sea? University of Hull, pp. 76–103.
Traditional offshore wind turbines are attached to the seabed in shallower waters within the near-shore marine environment. As offshore wind technologies become more advanced, floating structures have begun to be used in deeper waters where more wind resources exist.
Common environmental concerns associated with offshore wind developments include:
* The risk to seabirds being struck by wind turbine blades or being displaced from critical habitats;
* Underwater noise associated with the installation process of monopile turbines;
* The physical presence of offshore wind farms altering the behavior of marine mammals, fish, and seabirds by reasons of either attraction or avoidance;
* Potential disruption of the near-field and far-field marine environments from large offshore wind projects.
Due to the landscape protection status of large areas of the Wadden Sea, a major World Heritage Site with various national parks (e.g. Lower Saxon Wadden Sea National Park) German offshore installations are mostly restricted on areas outside the territorial waters.Internationales Wirtschaftsforum Regenerative Energien (IWR), German wind power industry Offshore windpark website Offshore capacity in Germany is therefore way behind the British or Danish near coast installments, which face much lower restrictions.
In January 2009, a comprehensive government environmental study of coastal waters in the United Kingdom concluded that there is scope for between 5,000 and 7,000 offshore wind turbines to be installed without an adverse impact on the marine environment. The study—which forms part of the Department of Energy and Climate Change's Offshore Energy Strategic Environmental Assessment—is based on more than a year's research. It included analysis of seabed geology, as well as surveys of sea birds and marine mammals. There does not seem to have been much consideration however of the likely impact of displacement of fishing activities from traditional fishing grounds.Johnson, M.L. & Rodmell, D.P., 2009. Fisheries, the environment and offshore wind farms: Location, location, location. Food Ethics, 4(1), pp.23–24.
A study published in 2014 suggests that some seals prefer to hunt near turbines, likely due to the laid stones functioning as artificial reefs which attract invertebrates and fish.Warwicker, Michelle. "Seals 'feed' at offshore wind farms, study shows" BBC, 21 July 2014. Accessed: 22 July 2014. Video of seal path However studies of the impacts of dredging on complex soft sediment communities suggest that the impacts caused by construction of structures such as windfarms may still be discernible up to 10 years afterNewell, R.C., Seiderer, L.J. & Hitchcock, D.R., 1998. The impact of dredging works in coastal waters: A review of the sensitivity to disturbance and subsequent recovery of biological resources on the sea bed. Oceanography and Marine Biology Annual Review, 36, pp.127–178.
== See also ==
* Environmental movement
* Environmental concerns with electricity generation
* Environmental effects of coal
* Environmental effects of nuclear power
* Environmental issues with energy
* Health effects from noise
* Renewable energy debate
== References ==
== Further reading ==
* Robert Gasch, Jochen Twele (ed.), Wind power plants. Fundamentals, design, construction and operation, Springer 2012 ISBN 978-3-642-22937-4. 
* Erich Hau, Wind turbines: fundamentals, technologies, application, economics Springer, 2013 ISBN 978-3-642-27150-2 (preview on Google Books)
* Alois Schaffarczyk (ed.), Understanding wind power technology, Wiley & Sons 2014, ISBN 978-1-118-64751-6. 
* Hermann-Josef Wagner, Jyotirmay Mathur, Introduction to wind energy systems. Basics, technology and operation. Springer 2013, ISBN 978-3-642-32975-3.
== External links ==
* NWCC. National Wind Coordinating Collaborative website, facilitated by the American Wind and Wildlife Institute, includes its updated summaries of wind-wildlife interactions from 2010.
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