5.1. Observations


The design and governance of large-scale renewable energy projects relies on a range of standards and various compliance mechanisms to monitor and enforce those standards.

Standards are often set and maintained by the responsible authority (for example, a state planning department or environment department) and there are a variety of arrangements in place for enforcing compliance with the standards. Standards may be ‘borrowed’ from other jurisdictions (for example, Victoria uses the New Zealand (NZ) noise standard, the NSW noise standard is based on the South Australian standard), set by the planning function or set by the state agency responsible for environmental management and regulation.

Enforcement of standards and permit conditions also varies by jurisdiction and the type of standards. Generally speaking, there are no proactive compliance audit regimes in place – rather, compliance relies on authorities receiving and investigating complaints or alleged breaches of permit or license conditions. The pathway to make a compliance complaint or allegation again varies by jurisdiction and type of complaint – in some cases the state environmental regulator can receive and investigate noise or environmental complaints, in other cases it may be a local council, state planning department or the relevant Australian Government department.

Compliance Complaints

It is often unclear to community members where or who they should lodge a complaint to regarding compliance. Planning permits may not always clearly state the accountability and responsibilities with regard to compliance oversight, nor may they prescribe a process for handling potential or actual non-compliance. Further, local councils and state planning functions may not have the necessary skills and expertise to handle and investigate a compliance complaint. Federal agencies, such as the Clean Energy Regulator, rely on a clear understanding of the responsible compliance authority and the authority’s advice if the Regulator is to consider acting on allegations of non-compliance or breach of a law.

Interpretation and Consistency of Standards

Borrowed standards can also be difficult to administrate or enforce if a protocol has not been developed for the local jurisdiction. As an example, the NZ noise standard (used in Victoria and Tasmania) has a concept of low and high amenity areas for determining the appropriate noise limits for a wind farm. Victoria’s planning scheme does not define such areas, making it difficult to interpret and apply the NZ standard ‘as is’ in the Victorian context (see Cherry Tree Wind Farm Pty Ltd vs Mitchell Shire Council – VCAT – P2910/2012).

Issues have also arisen regarding the application of tonal noise penalties provided for in the NZ standard. The application of the standard is open to interpretation in that regard, and Victoria/Tasmania must rely on interpretations from New Zealand court proceedings to clarify the standard’s application. This can be a difficult matter to resolve, particularly in the event the interpretation has also been a topic of debate in New Zealand itself (see Decision of Hearing Commissioners re Palmerston North City Council v New Zealand Windfarms Ltd – November 2017).

Typical standards and permit requirements relevant to a project’s development and operation can include matters such as audible noise, shadow flicker, visual amenity impacts, setback distances, environmental matters related to flora and fauna, vegetation clearance as well as noise and dust levels during construction.

Noise Standards

Noise standards relating to wind farms currently vary by state. For example, the wind farm noise limit standard in Victoria and Tasmania is 40 dB(A)* measured outside the residence. South Australia varies between 35 dB(A)* and 40 dB(A)* based on the location of the wind farm, Western Australia is 35 dB(A)*, New South Wales is 35 dB(A)* and Queensland’s standard is 37 dB(A)* during the day and 35 dB(A)* during the night. The approach to measuring the noise emitted from a wind farm can also vary by project and jurisdiction which can lead to debate over the veracity of the noise assessment results.

The World Health Organization’s (WHO) noise guidelines released in 2018 recommended a 45 dB (Lden) limit for wind farm noise, as measured outside the residence, to prevent negative effects on sleep and health. However, the report noted the lack of research or evidence available to conclusively support this new guideline limit. Previous WHO guidelines were based on an inside measurement limit of 30 dB(A), although it can be difficult and intrusive to carry out wind farm noise testing inside a residence, particularly over a long period of time.

Current noise standards therefore rely on the effects of attenuation of the noise by the residence structure and would assume that a noise level of say 40 dB(A) measured outside the residence should be less than 30 dB(A) measured inside, based on an expected attenuation in the order of 10-15 dB(A). This attenuation may be greater if the windows are closed and the residence is of solid construction and well insulated, however, the effective attenuation may be less if windows are open and/or construction and insulation of the residence is less robust.

Issues can also arise where a wind farm is tested for noise and the result exceeds the limit by a marginal amount, for example 40.2 dB(A) against a limit of 40 dB(A). The Commissioner’s understanding is that the 0.2 dB(A) difference would not be discernible by the human ear and is the result of the complex mathematical calculations that assess multiple noise data points. There may be some merit in allowing for a small, reasonable tolerance level to avoid wind farm’s unnecessarily being in technical breach of compliance.

Debate continues as to whether or not a low frequency standard should also be introduced, such as a dB(C) and/or dB(G) weighting. The prevailing argument to date is that the ‘A‑weighted scale’, which has been designed to replicate the human ear’s sensitivity to noise, accommodates a sufficient proxy for low frequency noise – noting that low frequency noise can be difficult to detect at levels that would breach threshold targets.

However, based on complaints received, the possibility remains for annoyance for some people living in proximity to a wind farm and perceiving low frequency noises or vibrations while inside their residence. More work is still required to determine whether or not the noise or vibration source in question is the wind farm or some other source. The Office’s complaint data has seen a significant reduction over time from complainants citing concerns about low frequency noise or vibrations emanating from operating wind farms.

There may be other sources of noise as a result of the project’s operation, in particular noise that would emanate from the electrical infrastructure, including power substations, transformers and back-up generators. The impact of such noise sources should be assessed during the design phase and tested for compliance during any post-construction noise testing.

The Independent Scientific Committee on Wind Turbines has derived a suggested wind turbine noise limit of 35 dB(A) (LA90,10-min) to ensure minimal annoyance. This suggested limit approximately equates to a LAeq,10-min of 37 dB(A) or a Lden of 43 dB(A).

* or background noise plus 5 dB(A), whichever is the greater amount. Measurements of A-weighted sound pressure level are generally taken on the basis of LA90, 10-min.

Setback Distances

A setback distance (also known as a ‘veto’ distance) is a default distance that, if a residence (dwelling) is within that specified distance from a proposed infrastructure, such as a wind turbine or solar array, the resident can either veto the asset or enter into a commercial agreement with the developer to allow the asset to be sited within the setback distance limit.

Setback distances from an asset to a residence also vary across states. For example, Victoria originally had no setback distances for wind turbines, then introduced a 2 km setback distance in 2011 and subsequently amended it to 1 km in 2015. Queensland has a setback distance of 1.5 km, while the New South Wales framework is based on a merit assessment of each project against the criteria and performance standards in the framework. Western Australia has recently recommended a 1.5 km setback in their Position Statement: Renewable Energy Facilities (Western Australian Planning Commission, March 2020). Turbines can be closer to a residence than the default setback distance, however typically require an agreement to be reached between the resident property owner and the developer.

Current setback distances for wind turbines have been predominately set based on legacy turbine dimensions and expected outcomes from noise standards. As a rough rule of thumb, a 40 dB(A) noise contour should be just less than about one kilometre from the turbine(s), whereas 35 dB(A) noise contour is typically less than 1.5 km from turbines, although these distances can vary with topography and terrain. Turbines installed during the last decade have mostly been at tip heights in the order of 150 metres and around 2 MW to 3 MW in capacity.

New projects are now proposing turbines with tip heights in excess of 220 metres and capacity of up to 6 MW or more per turbine. Improvements in turbine design have mitigated the noise effects and, generally speaking, the noise contours have not materially changed for these larger turbines, despite increased hub and tip heights as well as generating capacity. However, there may well be effects of increased visual amenity and shadow flicker impacts that may give rise for a need to revisit current set back distances and increase them accordingly.

While setback distances are typically based on the distance from the wind turbine to the residence, there may also be circumstances where the distance of the turbine from the neighbour’s property boundary should also be a consideration. Such circumstances could include the potential effect of wind turbines on animals such as horses, driving distractions on nearby roads or other situations where turbines may impact neighbouring properties due to their proximity to land use activities on a property.

The British Horse Society recommends a minimum setback distance from wind turbines to horses of 200 metres or three times the blade tip height – whichever is greater – on the basis that horses could potentially react to noise, blade rotation and shadow flicker impacts from wind turbines (see the Society’s Wind Turbines and Horses – Guidance for Planners and Developers, 2015). The Society’s report notes that, while there have been anecdotal reports of livestock such as horses being impacted by turbines, no formally recognised studies have established demonstrable causality.

Upper Lachlan Shire’s Development Control Plan specifies that turbines shall not be located within a distance of two times the tip height of a turbine from a formed public road or a non-involved property boundary. For example, a tip height of 150 metres would require a setback of 300 metres from a road or property boundary according to these guidelines (see Upper Lachlan Development Control Plan 2010, page 93).

Further, there is the possibility of a turbine blade ‘dropping’ or being ‘thrown’ from the turbine while in operation. The Commissioner is aware of five such events in Australia in recent times. As discussed in further detail in Section 9 (Health and Safety), the Commissioner facilitated meetings with industry to discuss wind farm safety incidents, agreeing to adopt measures to ensure full transparency and sharing of incident information across the industry. Corrective actions and mitigation strategies are in the process of being implemented to avoid future incidents, however these recent events also support the need for a setback distance from roads and boundary fences in the order of 200 metres to allow for a safety margin in the event of a blade drop or blade throw.

Electrical infrastructure required for the project, such as transmission lines, may also cause a change in visual amenity for community members. Consideration should be given for those impacts and setback distances as they may also be appropriate to mitigate visual amenity loss and noise issues arising from the infrastructure.

Shadow Flicker

Consideration should also be given to the current standards for wind turbine shadow flicker. A typical standard at present is a limit of 30 hours of shadow flicker per year at a resident’s external window or garden area. This standard, used across Australia, has been sourced from shadow flicker standards developed and used in Europe, where setback distances to residences are typically less restrictive. At, say, a 1 km distance from a turbine, the residence would be very unlikely to receive 30 hours of actual shadow flicker.

A more appropriate standard in the Australian context may be no more than a total 15 hours of actual shadow flicker per year at a residence and no more than 30 minutes of shadow flicker should be experienced on a given day. Neighbours experiencing (or likely to experience) shadow flicker that is annoying should also be provided with the opportunity for having visual screening installed. To date, shadow flicker complaints have been minimal.

Harmonisation of Standards

The opportunity exists for a clearer framework of standard setting and enforcement of standards, whereby there is independence in the setting and enforcement of standards from the planning function. Such independence allows for increased community confidence in the objectivity of setting standards and assessing compliance. It also allows the relevant independent agency to acquire and maintain the appropriate skills and expertise to fulfil its standards and compliance responsibilities.

The opportunity also exists for increased harmonisation of key standards across state jurisdictions, such as noise, visual amenity, shadow flicker and setback distances, providing a consistent approach and expectations for governments, industry and the community. Consistency across the states will not only provide a more equitable outcome for residents potentially affected by projects, but may also result in the additional benefit of driving improvements in the technology across the entire market based on the more stringent, while appropriate, standard.

While there may be a number of ways to address these issues, best practice appears to be assigning responsibility for the setting and compliance oversight of environmental-related standards with the state environmental regulator, while the application of the standards to specific projects rests with the state or local government planning authority. The current arrangements in place in New South Wales and South Australia generally reflect practices along these lines.

While standards and categories of standards for wind farm projects is reasonably mature, more work is required to detail the equivalent set of planning and environmental standards for solar farms.

Deemed Compliance

Finally, once a wind or solar farm commences operations, it may not have achieved formal compliance of all conditions until all of the post-construction compliance testing has been completed and accepted. Typically, formal post construction testing, such as noise testing of a wind farm, can only commence once all turbines are operating. The testing itself may take up to 12 months to complete and report. There may be a period of two or more years where the wind farm is partially or fully operating but is yet to be confirmed as compliant.

A project may therefore effectively be assessed as compliant in some jurisdictions, even though post-construction assessments have not commenced or been completed, relying on the predictive assessments undertaken prior to construction. There may be an opportunity to introduce more formal processes to properly clarify the ‘deemed’ compliance period and then clearly state when a project is confirmed as compliant (once all the required post-construction testing is complete) and the timeframes for when that must occur.

The interim period of compliance uncertainty can cause a range of community concerns, particularly at, say large wind farm projects that may have a two year plus construction cycle followed by a 12-month post-construction testing/reporting program.

Anecdotally, some wind farms have been described as being ‘not non-compliant’ when unable to confirm compliance with required permit conditions, highlighting the difficulty of declaring a wind farm to be ‘non-compliant’ when its default status is compliant. Again, it may be appropriate to consider that a wind farm is deemed to be operationally compliant during the construction, commissioning and testing periods, but ongoing compliance is subject to final confirmation by the responsible or regulatory authority after compliance testing is completed.

From the Commissioner’s observations, one solution to this issue is for a wind farm to be licensed by the appropriate environmental regulator. Under this scenario, the wind farm would need to confirm and maintain its compliance with the applicable license and permit conditions or risk losing its license to operate in the event of unrectified material breaches of the license and/or permit conditions. The license conditions could include conditions to be met during the period prior to post-construction testing, particularly with regard to handling abnormal or mechanical noise issues that can arise.

Measurement approaches for measuring compliance with the standards can also vary between projects and jurisdictions. Given the extraordinary number of variables to be measured, consideration needs to be given to the consistency of measurement, calculations and reporting for assessing environmental measures such as noise and flora and fauna impacts when setting permit or license conditions.

For example, there is much scope for variability when selecting the noise data points to be included in a noise compliance assessment and determining the ‘line of best fit’ for those set of noise data points – such variances could mean the difference between compliance or otherwise when assessing the results of a noise testing program. Section 6, which follows this section, discusses the merits of an independent audit regime to check the accuracy and integrity of environmental assessments, such as noise.

5.2 Recommendations

5.2.1 State governments should review and clarify their arrangements for the setting of and maintaining environmental standards, along with the arrangements for oversight and confirmation of compliance with those standards. It is preferred that the department(s) or agency setting and maintaining the various standards is independent of the department or agency responsible for planning and applying those standards.

5.2.2 The compliance authorities for a project should be clearly defined, transparent, accessible to the community and able to receive and investigate allegations of compliance breaches. Where compliance oversight currently rests with local government, appropriate support and resources should be made available to the council/shire to enable them to effectively perform their compliance and investigative responsibilities, including being equipped with the appropriate policies and procedures to handle alleged breaches of permit/license compliance and/or laws.

5.2.3 Based on the outcome of the review outlined in Recommendation 5.2.1, state governments should consider whether the current arrangements are appropriate, effective and consistent with best practices for the independent development, maintenance, compliance management and governance of environmental standards applicable to wind and solar projects.

5.2.4 In considering the above recommendations and possible reforms, the potential roles of an appropriate independent, state based, standards and compliance agency (such as a state environmental protection or regulatory authority) could include responsibility to:

  • Set and maintain the environmental standards applied to wind and solar farms, including setback distances, noise, shadow flicker, visual amenity, flora and fauna, environment and heritage (noting the role of the Commonwealth Environment Protection and Biodiversity Conservation Act 1999 with regard to Matters of National Environmental Significance including protected flora and fauna), along with specifying the methods and procedures for measurement of the prescribed standards.
  • Review planning applications for projects and recommend/require permit conditions related to the environmental standards. Environmental standard conditions in permits should clearly state the process for how the measurements are to be undertaken and reported as well as provide the opportunity for peer review of the process, calculations and results.
  • Provide or facilitate peer review and audit of expert reports, including review of testing and modelling programs, submitted by the developer related to permit requirements (see also Section 6).
  • Where appropriate, license the facility once it is constructed and issue and monitor license conditions for the operation of the asset that may be subject to review and renewal. State governments should also receive and review regular reporting against those licence conditions from the project operator and may withdraw licences in the event of unrectified material breaches of applicable license and permit conditions.
  • Receive and investigate complaints related to environmental standards, including alleged breaches of non-compliance with permit requirements or relevant laws.
  • Confirm as required the compliance or non-compliance of an operating project with regard to environmental standards, related permit conditions and relevant laws.
  • Report material breaches and investigations to the Clean Energy Regulator and other relevant agencies.
  • Liaise with other agencies (e.g. Civil Aviation Safety Authority, Australian Government Department of Agriculture, Water and the Environment) on assessments and compliance matters that involve such agencies.

5.2.5 Planning permits (and/or applicable licenses) for projects should clearly state:

  • The oversight organisation(s) or person(s) accountable for determining compliance of a project with its permit (and/or license) conditions, both at post-construction and ongoing operational stages.
  • The process and contact details for lodging a complaint or alleged breach of permit (and/or license) compliance.
  • The process to be followed if an operating project is found to be non-compliant with one or more of the permit (and/or license) conditions.
  • A requirement for the developer or operator to publish transparently, on the project website, the process and contact details to make a complaint or alleged compliance breach to the designated oversight organisation.

5.2.6 During the period between the commencement of a project’s commissioning/operation and the completion of any required post-construction assessments, the project could be designated to be in ‘provisional’ or ‘deemed’ compliance, pending the results of the assessments. In this scenario, a project can only move from ‘provisional compliance’ status to being confirmed as ‘compliant’ once the responsible authority has confirmed it is satisfied that the project is compliant as a result of any post-construction assessments. While the project is in ‘provisional compliance’ it is deemed to be compliant. Once a project has completed its post-construction assessments and confirmed to be compliant by the responsible authority, ongoing compliance is then overseen by the designated agency or responsible compliance authority. For the avoidance of doubt, a project that has been constructed in a way that is consistent with the requirements of any predictive assessments would be deemed compliant unless proven otherwise.

5.2.7 If a project’s facilities are deemed by a responsible authority to be in an unrectified material breach of compliance, the project should be required by the responsible compliance authority to cease operating or curtail the non-compliant facilities until compliance is achieved.

5.2.8 The Federal Government could review the compliance enforcement powers and actions that may be taken by the Clean Energy Regulator in the event of a suspected or confirmed unrectified material breach of compliance, including the Regulator’s ability to directly take punitive actions against a non-compliant project.

5.2.9 Governments should consider reviewing the primary standards across all jurisdictions for noise limits and setback distances. The following relate to wind farms only: Based on current observations and the findings of the World Health Organization, it would appear that an appropriate level for a consistent wind farm noise limit would be 35 dB(A)*, measured outside of the residence. Noise standards that specify ‘high’ and ‘low’ amenity noise level limits must have clear guidance that define where those limits are applicable. 

* LA90, 10-min; or background noise plus 5 dB(A), whichever is the greater amount Applied penalties for specific noise conditions such as tonality and special audible characteristics continue to be set at 5 dB(A), however such noise complaints should also be assessed on a subjective and reasonableness test by an approved, independent expert. Protocols should be developed and in place to clarify interpretation of ‘borrowed’ noise standards from other jurisdictions. A default setback distance of 1.5 km between a residence or dwelling and the nearest turbine (note: for turbines with a tip height of 200 metres or greater, a greater setback distance may be more appropriate to accommodate increased visual amenity impacts). Local topography, existing trees and vegetation as well as terrain need to be also considered when applying any default setback measures. In addition to a setback distance between a turbine and a residence, a minimum setback distance of 200 metres (as measured at ground level from the centre of the tower or 150 metres from the extended horizontal blade tip, whichever is the greater) and a neighbour’s boundary fence line or public road carriageway, should also be considered to mitigate potential safety risks. In relation to proposed transmission lines, a transmission line that is less than 220 kV should have a setback distance of 100 metres from a residence, while a powerline that is 220 kV or greater should have a setback distance of 200 metres. Transmission lines should also be set back from public roads, with the suggested setback distance of the transmission line towers measured as the tower height plus 20 metres. Consideration should be given to setback distances between a wind farm and a materially populated township or city boundary. A distance of 5 km may be appropriate to preserve amenity and provide some flexibility for planning growth of the township (note – consideration of reducing these suggested setback provisions may be appropriate in the case of a small-scale, community-supported and owned wind energy facility).

5.2.10 The noise assessment design and compliance testing conditions should include assessment and testing of the project’s electrical infrastructure (transformers, substations, back-up generators etc.) and noise levels from these sources need to be compliant with the applicable standards.

5.2.11 A setback distance between a residence and other infrastructure associated with the project, such as transmission lines, should also be considered to help alleviate visual amenity impacts and noise considerations. This would include a setback distance between a residence and major transformer or generation infrastructure, such as a terminal substation. Where possible, transmission infrastructure should be placed underground and/or well away from residences and road reserves. If this is not possible, a minimum setback distance of 100 metres between a rural residence and powerline infrastructure should be considered in planning guidelines for powerlines of 66 kV or greater.

5.2.12 Power poles installed in the road reserve must comply with relevant standards and guidelines for setback distances from the carriageway, comply with any road safety requirements and road safety barrier specifications, and pole locations must be pre-approved by the responsible authority.

5.2.13 Consideration should also be given to the current standards for wind turbine shadow flicker. A typical standard at present is a limit of 30 hours of shadow flicker per year at a resident’s external window or garden area. A more appropriate standard could be no more than a total 15 hours of actual shadow flicker per year at a residence and no more than 30 minutes of shadow flicker should be experienced on a given day. Neighbours experiencing (or likely to experience) shadow flicker that is annoying should also be provided with the opportunity for having visual screening installed.

5.2.14Final siting adjustments for turbines during construction (‘micro-siting’) should be limited to a distance of no more than 100 metres from the approved site location, be no closer to a residence (or property boundary as per Recommendation 5.2.7) and be properly documented, including the reasons for the change. Micro-siting of a distance greater than 100 metres should require written approval from the responsible authority.

Further information