Resource Documents: Regulations (235 items)
Documents presented here are not the product of nor are they necessarily endorsed by National Wind Watch. These resource documents are provided 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.
Author: Crawford, Michael
The substantial body of empirical research now available on wind farm visual impact (VI), from
very credible and impartial teams, shows a consistent and essentially linear relationship between
turbine height, distance and wind farm VI. For any degree of VI (such as the zone of visual
influence, or threshold for visual dominance), if turbine height is doubled, the distance threshold
for that degree of impact also typically doubles.
The research based distances for thresholds for key levels of VI are many times larger than
thresholds proposed by the NSW Department of Planning and Environment in its draft VI
Assessment Bulletin. The Department’s proposed thresholds are repudiated by the consistent
The research also identifies a number of other ways in which wind farm VI assessment practices
accepted by NSW planning agencies are defective, in particular relating to the neglected
importance of blade movement for VI, the fact that photomontages tend systematically to
underestimate VI, and the assessment frameworks commonly used are too simplistic to describe
real world experience.
The NSW Government has a responsibility to reassess its draft VI Assessment Bulletin explicitly in
the context of the published research and produce proposals which it can intellectually justify in the
context of that research – which at present it cannot do.
[ABSTRACT; 6th November 2016]
Author: Vanhellemont, Quinten; and Ruddick, Kevin
In the last decade, the number of offshore wind farms has increased rapidly. Offshore wind farms are typically constructed in near-shore, shallow waters. These waters can be highly productive or provide nursery grounds for fish. EU legislation requires assessment of the environmental impact of the wind farms. The effects on hard and soft substrate fauna, seabirds and marine mammals are most frequently considered. Here we present Landsat-8 imagery that reveals the impact of offshore wind farms on suspended sediments. Turbid wakes of individual turbines are observed that are aligned with tidal currents. They are 30–150 m wide, and several km in length. The environmental impact of these wakes and the source of the suspended material are still unclear, but the wake size warrants further study. The underwater light field will be affected by increased suspended sediments and the turbid wakes could significantly impact sediment transport and downstream sedimentation. The question of whether such features can be detected by other remote sensors is addressed by a theoretical analysis of the signal:noise specification for the Operational Land Imager (OLI), the Enhanced Thematic Mapper Plus (ETM +), the Advanced Very High Resolution Radiometer (AVHRR/3), the Moderate-Resolution Imaging Spectroradiometer (MODIS), the Spinning Enhanced Visible and Infrared Imager (SEVIRI), the Flexible Combined Imager (FCI) and the Multispectral Instrument (MSI) and by a demonstration of the impact of processing OLI data for different spatial resolutions.
Quinten Vanhellemont and Kevin Ruddick
Royal Belgian Institute for Natural Sciences (RBINS), Operational Directorate Natural Environment, Brussels, Belgium
Remote Sensing of Environment Volume 145, 5 April 2014, Pages 105–115
Author: Lintott, Paul; Richardson, Suzanne; Hosken, David; Fensome, Sophie; and Mathews, Fiona
Demand for renewable energy is rising exponentially. While this has benefits in reducing greenhouse gas emissions, there may be costs to biodiversity . Environmental Impact Assessments (EIAs) are the main tool used across the world to predict the overall positive and negative effects of renewable energy developments before planning consent is given, and the Ecological Impact Assessments (EcIAs) within them assess their species-specific effects. Given that EIAs are undertaken globally, are extremely expensive, and are enshrined in legislation, their place in evidence-based decision making deserves evaluation. Here we assess how well EIAs of wind-farm developments protect bats. We found they do not predict the risks to bats accurately, and even in those cases where high risk was correctly identified, the mitigation deployed did not avert the risk. Given that the primary purpose of an EIA is to make planning decisions evidence-based, our results indicate that EIA mitigation strategies used to date have been ineffective in protecting bats. In the future, greater emphasis should be placed on assessing the actual impacts post-construction and on developing effective mitigation strategies.
The high legal protection of bats (e.g., Europe: EUROBATS 2014; North America: Endangered Species Act 1973), together with the known risks to bats from wind farms (e.g. ), means that detailed preconstruction ecological assessments are frequently undertaken. Acoustic surveys are widely used to provide an estimate of bat activity from which collision risk is inferred. However, bat activity is highly variable – both spatially and temporally. It is therefore unclear whether the survey protocols currently employed assess bat activity with sufficient precision and repeatability to be of practical value in inferring risk for developments. Determining the best methods to assess likely impacts on bats from wind turbines is regarded as a research priority by EUROBATS . To our knowledge, there has only been one study (in North America) that investigates the value of using bat activity to predict the risk to bats from future wind turbines. This found that pre-construction bat activity was not a significant indicator of collision risk ; however, the value of EIAs in predicting risk was not assessed. We therefore assessed the effectiveness of pre-construction EIAs as a tool to aid decision-makers in determining the impact of wind energy on bats.
We surveyed 46 wind farms across the UK for bat fatalities as part of a separate field study investigating the impact of wind turbines on bats. We were able to obtain EcIAs for 29 of these sites; the remaining EcIAs could not be obtained from public sources or developers. Eighteen EcIAs concluded that a field assessment of bat presence/activity was not required (evidenced by statements in the EcIA such as “Surveys are unnecessary as the development does not affect any features likely to be used by bats”), or inferred based on field surveys that no significant effects on any protected species would occur (see also Table S1 in Supplemental Information, published with this article online). However, during our post-construction surveys we found that half of these sites contained casualties (ranging from one to 64 fatalities per month during the July–October survey period), and 97% had evidence of bat activity (ranging from one to 236 passes per night). The perception of risk to bats during EcIAs was not significant in predicting either bat casualty rates (Figure 1A) or activity levels post-construction (see also Figure S1). While there was a positive relationship between sites ranked by perceived risk to bat populations and the ranking of sites by casualties per month (Figure 1B), there was considerable scatter in the data, and 9 sites identified as having the lowest risk had more than 1 casualty per month.
Our results show that sites which may have been perceived as of poor quality for bats can contain casualties after wind turbine construction. Similarly, bat activity recording during pre-construction surveys may not accurately reflect activity levels post-construction. This may be due to bats changing their behaviour at turbines , as bats may be attracted to wind farm sites for a variety of reasons, including the emission of ultrasound from turbines  and increased prey availability . It is therefore essential that future mitigation strategies are formed with an understanding of how bat behaviour differs at sites after turbines have been constructed. Additionally, surveying effort has to be adequate both spatially and temporally to assess risks to bats in the first place. Pre-construction surveys are conducted predominantly at ground level due to the difficulties and cost of surveying at height; however, where meteorological masts are in place (or as drone technology develops) then conducting acoustic surveys within the rotor-swept area may give a more accurate assessment of risk. But this relationship has yet to be tested.
Of those sites identified as posing a significant risk to bats in the EcIA surveys, risk does not appear to have been adequately mitigated. Indeed, one of these mitigated sites had the highest recorded casualty rate. In the UK, regulations state that “if significant harm cannot be avoided, adequately mitigated, or as a last resort, compensated for, planning permission should be refused” and similar legislation applies in many other countries. We conclude that significant harm was not avoided at these significant risk sites.
Given the economic cost of EcIAs, the value attached to their findings during planning applications, and the possible consequences to biodiversity of errors, it is vital that they are fit for the purpose. We highlight that although EIAs give the perception of rigorous safeguarding of environmental standards and may portray energy companies with an environmentally friendly public image, considerable time and expense goes into deploying bat detectors at pre-construction sites with little justification. Although the use of EIAs has evolved differently between nations , there is a pressing global need to identify the procedures which can accurately identify risk to bats (e.g., Brazil ). The precautionary principle indicates that sites perceived to contain little collision threat to bats should be treated with caution until there is a greater understanding of how to identify risk factors to bats. On occasions when mitigation is currently deemed unnecessary, post-construction surveys should still be conducted (e.g. carcass searches) to ensure that the predictions are accurate and bat behaviour has not altered from pre-construction levels. Establishing the species assemblage at a site may nevertheless have some value in identifying the presence of species at high collision risk and/or of particular conservation concern in the region. In mainland Europe, automated systems using weather variables and site-specific post-construction bat activity data have been used to trigger turbine curtailments to minimise bat collisions . Pre-construction surveys may therefore still be useful as the data (e.g., nightly and seasonal peaks of activity) may provide an indication of the extent of curtailment that is required and therefore the economic viability of the project. Our results highlight the importance of longitudinal monitoring of major developments and a feedback mechanism for practitioners to share the success or failure of mitigation strategies.
Paul R. Lintott, Suzanne M. Richardson, David J. Hosken, Sophie A. Fensome, and Fiona Mathews
Hatherly Laboratories, Biosciences, College of Life and Environmental Sciences, University
of Exeter, Prince of Wales Road, Exeter, UK; and (S.A.F.) Centre for Ecology and Conservation, University of Exeter, Cornwall, Tremough, Penryn, Cornwall, UK.
Current Biology 26, R1119–36, November 7, 2016 [Correspondence]
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2. Arnett, E.B., and Baerwald, E.F. (2013). Impacts of wind energy development on bats: implications for conservation. In Bat Evolution, Ecology, and Conservation, R.A. Adams and S.C. Pedersen, eds. (Springer: New York), pp. 435–456.
3. Rodrigues, L., Bach, M.-J., Dubourg-Savage, B., Karapandža, D., Kovacˇ , T., Kervyn, J., Dekker, A., Kepel, P., Bach, J., Collins, C. et al. (2015). Guidelines for consideration of bats in wind farm projects – Revision 2014. EUROBATS Publication Series NO. 6 (English version). (Bonn: UNEP/EUROBATS Secretariat).
4. Hein, C.D., Gruver, J., and Arnett, E.B. (2013). Relating pre-construction bat activity and postconstruction bat fatality to predict risk at wind energy facilities: a synthesis. A report submitted to the National Renewable Energy Laboratory. Bat Conservation International, Austin, TX, USA.
5. Cryan, P.M., Gorresen, P.M., Hein, C.D., Schirmacher, M.R., Diehl, R.H., Huso, M.M., Hayman, D.T.S., Fricker, P.D., Bonaccorso, F.J., Johnson, D.H., et al. (2014). Behaviour of bats at wind turbines. Proc. Natl. Acad. Sci. USA 111, 15126–15131.
6. Kunz, T.H., Arnett, E.B., Erickson, W.P., Hoar, A.R., Johnson, G.D., Larkin, R.P., Strickland, M.D., Thresher, R.W., and Tuttle, M.D. (2007). Ecological impacts of wind energy development on bats: questions, research needs, and hypotheses. Front. Ecol. Environ. 5, 315–324.
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8. Valença, R.B., and Bernard, E., (2015). Another blown in the wind: bats and the licensing of wind farms in Brazil. Natureza & Conservação 13, 117–122.
9. Behr, O., Brinkmann, R., Niermann, I., and Korner-Nievergelt. F. (2011). Fledermausfreundliche Betreibsalgorithm fur Windenergieanlagen. In Entwicklung von Methoden zur Untersuchung und Reduktion des Kollsionsrisikos van Fledermäusen an Onshore- Windenergieanlagen. Umwelt und Raum, eds R. Brinkmann., O. Behr., I. Niermann and M. Reich, eds. (Cuvillier Verlag: Göttingen), pp. 354–383.
Author: WSP Parsons Brinckerhoff
This review was commissioned by the Department of Energy & Climate Change (DECC) in spring 2015 and finalised before DECC became part of the Department for Business, Energy and Industrial Strategy in July 2016.
The research has reviewed the evidence on the response to amplitude modulation (AM) in relation to wind turbines. It was undertaken by a research team lead by WSP Parsons Brinkerhoff, who are responsible for the overall editorial content of the report, and supported by three independent external reviewers.
The review considered the robustness of relevant dose-response relationships and how, in a policy context, the level(s) of AM in a sample of noise data should be interpreted. In particular, it considered at what point AM causes a significant adverse impact and has recommended how excessive AM from wind turbines might be controlled through the use of an appropriate planning condition.
The final report addresses comments raised by three peer reviewers, appointed by DECC. The reviewers, from Denmark and the Netherlands, are experts in noise and health.
While this research does not represent planning guidance, BEIS encourages developers and planning authorities in England to consider this research when determining if an AM condition would be appropriate.
The contractor worked closely with the Institute of Acoustics’ AM working group, who in August 2016 recommended a preferred metric and methodology for quantifying and assessing the level of AM in a sample of wind turbine noise data [click here for review from the Independent Noise Working Group].