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Articles

Developing social impact assessment guidelines in a pre-existing policy context

ORCID Icon, &
Pages 114-123
Received 18 Feb 2018
Accepted 02 Jun 2018
Published online: 02 Jul 2018

ABSTRACT

Few jurisdictions have translated internationally agreed social impact assessment (SIA) principles into statutory provisions. Governments and regulatory bodies tend to provide developers with high-level frameworks, or require that social impacts be ‘considered’, without specifying how this is to be done. In Australia, this lack of clarity leaves all parties uncertain about requirements for SIA. The New South Wales (NSW) Government’s 2017 release of the SIA guideline for State-significant mining, petroleum and extractive industry development represents an attempt to clarify requirements and provide guidance. In this paper, we describe the process of bringing this guideline to fruition from the perspective of being directly involved in its development, and highlight the challenges involved in integrating leading-practice principles into the state’s pre-existing policy framework. While the guideline represents a significant advance in policy-based SIA guidance, some aspects leave room for improvement. The real test of the guideline’s impact will lie in its influence on SIA practice in NSW, and ultimately in social outcomes for communities affected by resources projects.

Introduction

Over recent decades, the body of literature on social impact assessment (SIA) has evolved. It now includes internationally agreed principles and guidelines, ratified by professional organisations, including the International Association of Impact Assessment (IAIA) (Vanclay 2003; Vanclay et al. 2015). The application of these principles and guidelines is, however, a voluntary affair. Rather than being required by host-country legislation, project proponents can invoke them to ease the way for project approval, or claim ‘best practice’ in stakeholder engagement and community interaction. As SIA practice does not always reflect the attributes of international principles, its full potential is rarely realised (Bruekner et al. 2014). This paper focuses on an attempt by an Australian state government to improve SIA practice among extractive industries through a state-sanctioned guideline.

In Australia, no single jurisdiction has comprehensively translated these principles and guidelines into statutory provisions. Some state governments and regulatory bodies have high-level frameworks, or require that social impacts be ‘considered’, but do not specify how. This lack of clarity leaves all parties uncertain about state requirements for SIA. Public policy consultations in New South Wales (NSW) suggest that proponents and regulators seek to clarify expectations of the state; SIA practitioners seek support for conducting robust and meaningful assessments; and project-affected people seek comprehensive, meaningful, and independent assessment of impacts, and confirmation of their right to participate in the project-development process (NSW DPE 2015b, 2017c).

This paper describes the process of bringing to fruition the NSW Government’s Social impact assessment guideline for State significant mining, petroleum and extractive industry development (NSW DPE 2017b). As authors, we write from the perspective of being directly involved in the development of this guideline. To counter any inherent bias, we exercised reflexivity throughout the analytical process by self-critically considering our own assumptions, and exploring alternative interpretations (Alvesson and Deetz 2000). We highlight the challenges involved in integrating internationally agreed principles for SIA into NSW’s framework for assessing major resources projects. The paper proceeds by outlining the global context within which SIA has evolved, and then the policy context for assessing the impacts of major projects in Australia and NSW. We then explain how key issues were addressed in the process of developing the guideline, and within the guideline itself, before concluding with opportunities for further enhancement.

Conceptual and institutional development of SIA

Social impacts comprise the physical and emotional experiences that people, groups, and communities have as consequences of projects and activities that change the way they live, work, relate to one another, relax, and organise themselves (Interorganizational Committee on Principles and Guidelines for Social Impact Assessment 2003). SIA is a process that identifies and assesses the effects of project-induced change on people’s assets, rights, and systems of social organisation, including quality of life, culture, health, social interactions, and livelihoods. According to Vanclay et al. (2015), the process involves predicting, analysing, monitoring, and managing the intended and unintended consequences of the development.

SIA was first conceptualised as a part of environmental impact assessment (EIA). It developed in tandem with regulations on EIA that accompanied the introduction of legislation, such as the National Environmental Policy Act (NEPA) (1969) in the United States of America (USA). The NEPA required developers to consider environmental and social impacts on local communities in planning and decision-making processes (Burdge 2003). Social scientists have since advanced a body of SIA literature and practice (e.g. Wolf 1974; Freudenberg 1986; Lockie 2001; Burdge 2003). The lead article in the first issue of this journal’s predecessor (Impact Assessment) was titled ‘Social Impact Assessment’ (Wolf 1982). In 1994, the USA’s Interorganizational Committee on Principles and Guidelines for Social Impact Assessment developed a set of guidelines and principles for SIA, which were later incorporated by contemporary professional organisations, such as the IAIA.

The International Principles for Social Impact Assessment constitute the most widely recognised internationally agreed benchmark for effective SIA (Vanclay 2003). There is broad consensus about the characteristics, principles, and performance standards for SIA in these and other notable frameworks and guidelines, including Social Impact Assessment: Guidance for Assessing and Managing the Social Impacts of Projects (Vanclay et al. 2015) and international standards, such as ISO31000: Risk Management – Principles and Guidelines and ISO26000: Guidance on Social Responsibility. Numerous guides and resources for SIA practitioners and other stakeholders reflect these characteristics (Arce-Gomez et al. 2015). In essence, SIA practice is recognised as an iterative, community-focused, and participatory process that uses diverse forms of data and information to produce values-based assessments and strategies to address the opportunities, risks, and uncertainties associated with significant development projects and processes (Aledo-Tur and Domínguez-Gómez 2017) (see also ).

Policy context for SIA in Australia and New South Wales (NSW)

As understandings of SIA have evolved, so too has the approach of Australian legislators and regulators. The Queensland Government’s introduction of its Sustainable Resource Communities policy in 2008 was a significant turning point. This policy required a Social Impact Management Plan (SIMP) as part of the SIA process. SIMPs required project proponents to identify potential social impacts and to propose mitigation measures for negative impacts (Franks and Vanclay 2013). The Queensland government later released a package of initiatives, including ‘A new approach to managing the impacts of major projects in resource communities’ (State of Queensland DSDIP 2013), with Australia’s first guideline for SIA.1 The Northern Territory government produced a guideline for economic and SIA the same year, including a requirement for impact management plans as part of Public Environmental Reports or Environmental Impact Statements under the Environmental Assessment Act (NT EPA 2013).2

Australian governments had earlier initiated impact assessment processes that reached beyond single projects. In 2005, NSW conducted a strategic assessment to analyse the coal-mining potential of the Upper Hunter Valley. The assessment considered coal resources and mine-development potential alongside other issues, including surface and groundwater, social and amenity issues, natural and cultural heritage, land, and agriculture. This was followed, in late 2006, with a strategic review of the impacts of underground mining – especially subsidence – in the Southern Coalfield (Franks et al. 2010).

In 2008, the year it released its Sustainable Resource Communities policy, the Queensland Government initiated strategic regional impact assessments in the Galilee and Surat Basins. In 2010, the Western Australia (WA) and Commonwealth (federal) governments conducted a strategic regional assessment for the Browse Basin that considered the interconnections with existing and proposed projects in the area. In 2015, the NSW Government introduced provisions for preliminary regional issues assessment (PRIA) (NSW DPE 2015a) in its Strategic Release Framework for Coal and Petroleum Exploration. PRIAs were designed to identify regional-scale social, environmental, and economic issues relating to exploration for coal or gas.3 These strategic assessments can embed SIA into broader development processes and regulatory frameworks (Partidário and Clark 2000) and can encourage an integrated approach by recognising that social impacts are inextricably linked to other types of impacts. Nonetheless, in NSW, guidance about project-level SIA was not available.

SIA in NSW

In the absence of guidance, there were ongoing questions about the ‘adequacy’ of SIAs in the context of major resource developments. For example, the Warkworth Extension Project, the Metgasco coal-seam gas proposal, the Wilpinjong Extension Project, and the Bylong and Drayton South coal projects all attracted community opposition, partly owing to a view that social impacts were not afforded due attention in the impact assessment process (e.g. Preston 2014; Luke 2017; Askland 2018). In NSW, assessment of physical impacts, such as noise, dust, and vibration, was commonplace, whereas the experiential and more intangible impacts were largely being overlooked.

In NSW, the Department of Planning and Environment (DPE) is the authority responsible for assessing major project applications. DPE initiated the development of the new SIA guideline in 2016, following consultations with industry, community, and environmental groups for review of the State Environmental Planning Policy in 2015. The review and ensuing report (NSW DPE 2015b) indicated that, while the NSW planning system formally required ‘balanced assessment’ of likely economic, environmental, and social impacts, concerns remained that economic factors were being prioritised over other considerations.

The NSW Environmental Planning and Assessment Act 1979 No. 203 (current as at 15 April 2018) recognises that impacts on people are an important consideration in the assessment process for ‘State significant developments’ (SSDs).4 sets out the legislative and regulatory provisions relating to social impacts that were in place in early 2016, when the SIA guideline project was initiated.5 It shows that the Act intends the term ‘environment’ to incorporate social and economic considerations.

As shows, the legislative and regulatory framework required proponents to consider the social dimensions of major project developments. However, guidance about how proponents should understand and manage social impacts, and how the state should factor social impacts into decision-making for project approvals, was absent. This left project proponents, the state, the public, and project-affected communities unsure as to exactly what was required of a SIA process. It also became apparent that the NSW Government had limited capacity to evaluate SIAs produced by proponents. Most DPE staff have qualifications in urban planning and/or environmental sciences, rather than social sciences or cognate disciplines.

Table 1. Provisions for considering social impacts in NSW policy framework.

The SIA component of EIA in NSW became the subject of criticism. Community members claimed that project proponents and DPE gave less weight to social considerations than to economic matters. SIA reports that were commissioned and funded by proponents were considered to be biased documents designed to secure project approval, rather than providing impartial assessments. Community members were also frustrated that the window of opportunity to participate in assessments was inadequate, and that they were poorly resourced relative to project proponents. Proponents, meanwhile, criticised the time-consuming and onerous nature of the assessment process, and the vague nature of the state’s requirements (NSW DPE 2017c). In the absence of specific guidance, proponents tended to produce voluminous documents that considered all possible impacts, rather than investing time and resources to prioritise ‘material’ issues. These lengthy documents were, in turn, a frustration for both community and government. Six key criticisms of SIA performance under the pre-existing policy regime in NSW are summarised in and compared to internationally agreed practice as identified in the literature.

Table 2. Comparison between existing and preferred characteristics of SIA.

Having received stakeholder feedback about the need for early engagement of communities in development decisions, and having given a commitment to reduce ‘red tape’ under the Better Regulation Statement of 2008, the NSW Government sought to refocus policy and planning processes on people and the public interest (NSW Government 2012). The DPE Secretary declared 2016 the ‘Year of the Community’. That year, the NSW Department of Industry (2016) published an Exploration Code of Practice: Community Consultation. NSW DPE (2016) published Community Consultative Committee Guidelines and in 2017 released draft guidance on Community and Stakeholder Engagement for EIAs (NSW DPE 2017a). The Social impact assessment guideline for State significant mining, petroleum and extractive industry development was initiated in this period.

To progress the SIA guideline, DPE appointed a SIA Specialist (one author of this paper) to coordinate the development of guideline, internally. DPE determined that, in NSW, the resources sector was in most need of a dedicated SIA guideline, making projects in this sector the focal point of the SIA guideline project. DPE then commissioned The University of Queensland’s (UQ) Centre for Social Responsibility in Mining (the employer of the other two authors of this paper) to consult with resource-sector stakeholders, review available guidance, and prepare advice to DPE on leading-practice SIA in the resources sector.

The prioritisation of the resources sector reflects events in NSW. The social impacts of major projects were raised in submissions on the draft Integrated Mining Policy in 2015. Furthermore, several major resources projects, mentioned above, had been opposed on the basis of social impacts being overlooked. The Warkworth Extension Project was the site of local opposition, as well as legal challenge, partly owing to potential social impacts on the local community of Bulga. The Metgasco coal-seam gas proposal also attracted widespread dissent, and was opposed not only by community and environment groups but also by farmers and local councils. In more general terms, extractive industries induce a diverse set of impacts that can polarise communities (Bice 2015; Harvey and Bice 2014; Kemp and Vanclay 2013; Owen and Kemp 2017; Petrova and Marinova 2015). This reflects a general sentiment that ‘extractive industries are usually unpopular and generally mistrusted’ (Harvey and Bice 2014, p. 331). In an attempt to address this malaise, DPE’s SIA guideline project team, and its advisers, sought to reflect leading-practice SIA principles both in the process of drafting the guide, and within the guideline itself. The following sections provide insights into process and content.

Process of developing the SIA guideline

From the outset, the DPE project team sought to develop the guideline in a way that reflected SIA principles of inclusivity, equity, transparency, and impartiality. By conceptualising the development of the guideline as a social process, the team recognised that the project would involve social interactions about contested issues among diverse groups with a stake in SIA in NSW.

As O’Faircheallaigh (2009) notes, even the purpose of SIA is contested, and positionality will depend on one’s relationship to the project. In this contested terrain, there are struggles between discourses as heterogeneous systems of language and practice compete to form a new discursive order (Fairclough 1992, p. 115–120). During these struggles, power is renegotiated and meaning reconstituted, potentially allowing for ‘new fields of action’ (Wodak 2001, p. 66). Concepts such as ‘social licence’ and ‘SIA’ are examples of such contested fields (Owen and Kemp 2013; Parsons and Moffat 2014a, 2014b).

The project team therefore approached the process of developing the SIA guideline with the knowledge that SIA involves competing discourses. This required an acceptance of the contested nature of SIA, and framed the team’s role as one of navigating multiple perspectives to conduct a credible process and deliver a credible outcome. Reconciling contrasting and competing perspectives is consistent with SIA principles, but is not easy. Speaking about the adequacy of the law in identifying and satisfying society’s expectations of mining projects, Chief Judge Brian Preston (2014), of the Land and Environment Court of NSW, describes four key challenges.

Firstly, he notes that identifying ‘the community’ may not be a simple matter of delineating geographical boundaries, as others may have legitimate interests. Secondly, communities – and individual members within communities – have heterogeneous values, interests, and perceptions, and some are more vulnerable to adverse social impacts than others. Thirdly, Preston notes that people tend to be reticent about articulating their expectations, until those expectations are violated. Fourthly, expectations change over time, as the membership of communities changes, and in response to external influences, such as the media and social change. We adopt Preston’s list of challenges to structure our discussion of the project team’s attempts to enable a consultation process that reflected internationally agreed SIA principles.

Defining ‘community’

When consulting about a new policy, an immediate challenge is defining the ‘community’. Too narrow a definition risks a tokenistic approach that excludes and marginalises certain groups. To broad a definition risks the process becoming unmanageable. SIA principles recognise the right of affected and interested stakeholders to be heard (e.g. Vanclay et al. 2015). Policy development in Australia can be a unilateral, technocratic affair, with perfunctory forms of minimalist consultation that do not achieve meaningful community input (Gregory et al. 2008). Acknowledging this, the project team sought to listen to the views of affected and interested stakeholders, to focus on mining-intensive regions and sectors, and to facilitate opportunities for different groups to have input.

Since the locations of existing and likely future resources projects in NSW are known, two rounds of community consultation, eight months apart, were held in these regions. Round one comprised eight workshops, during which representatives of various interest groups were invited to discuss expectations and aspirations of the proposed guideline. As the draft guideline was on public exhibition by round two, open meetings were held in four of those same regions. Attendance at these meetings was unrestricted, with no requirement to pre-register.

In addition to the regional meetings, at various times the project team held sector-specific workshops and meetings with industry, Indigenous representative bodies, community and environmental groups, researchers, SIA consultants, and other government agencies. Further, during the three-month public exhibition period, any group or individual was entitled to lodge a written submission. Ultimately, the process solicited input from a broad range of affected and interested stakeholders. It aimed to accommodate both geographic and other legitimate interests.

Heterogeneity

Leading-practice SIA aims to consider a diversity of views relating to a project or initiative, and to ensure that marginalised and vulnerable people are able to participate. Yet policy development, when it does involve consultation, tends to cater for the ‘articulate, the vocal and those with vested interests’ (Gregory et al. 2008, p. 3), who may not represent broader values or interests. To enable heterogeneous voices and perspectives to be incorporated into the process, representatives of a diverse range of groups were invited to attend the first round of consultations. These meetings provided an opportunity for interactive small group discussions, with each participant given time to share expectations of the SIA guideline, drawing on their own or their group’s experiences, values, and interests. The project team encouraged people to highlight flaws in SIA practice, and to suggest how the SIA process could be improved. During the public consultations, any individual or group could offer an opinion on the draft guideline. The drawback of public meetings, however, is that prominent voices dominate proceedings (Brackertz and Meredyth 2009) and this was the experience during the largest of the four round two meetings.

The project team read all the material generated from the consultation phase – including notes from meetings, workshops, and written submissions. From this material, key points were extracted for further analysis. Points were organised against sections of the draft guideline and discussed among the project team. The team decided whether to (a) accept the point and incorporate it in a revision; (b) partially accept the point and adjust the draft accordingly; or (c) reject the point. When the guideline was released, the project team published a report (NSW DPE 2017c) summarising the 650 key points raised in these fora, and the Department’s response. This report explained where points were not accepted or incorporated into the guideline. The team sought to respect and respond to every point on merit, regardless of authorship.

Articulating interests

Judge Preston’s third challenge is that people rarely commit to writing or formally express their expectations of how businesses ought to operate, until those expectations come under threat. This highlights the need for structured, deliberative processes to stimulate expression of deeply held values, and reflection on how an initiative might reinforce or threaten those values. Gregory et al. (2008) note that, while deliberative processes are assumed to be institutionalised in Australia’s policy-making approach, genuine deliberation is the exception, leaving many communities cynical and distrusting towards governments.

The various workshops and meetings for the NSW SIA guideline project, while not explicitly designed as deliberative processes, did endeavour to encourage participants to reflect on their values, through dialogue, and to critically assess how those values might be reflected in the guideline. The round one community workshops were facilitated by the NSW Land and Water Commissioner – a person with considerable credibility and experience in engaging with rural communities about contested, resource-related issues.

A leading authority on community engagement, accredited by the International Association of Public Participation (IAP2), facilitated the four open meetings in round two. During these sessions, the facilitator invited participants to consider each section of the draft guideline, and, using various engagement techniques, prompted them to think about issues that were important to them. This encouraged participants to reflect on their experiences with mining and other large-scale projects, and to articulate how the guideline could improve the assessment and management of social impacts in future.

The strategy of placing a draft guideline on public exhibition was a more passive approach to soliciting feedback, since it relies on people knowing about the initiative and responding in writing. As part of the suite of engagement strategies, it was constructive in that it prompted additional feedback. The project team received 63 formal submissions, many of which were lengthy reports that involved substantial work by the authors. A specialist consultancy, for example, effectively provided a peer review voluntarily. Of the 63 formal submissions, 61 expressed support for the initiative.

Change over time

Judge Preston’s final challenge is that community expectations change over time. This can be pronounced in mining-affected communities, which may experience profound social change, over generations. While the eight-month gap between the two rounds of community consultation provided an opportunity for people to digest the information discussed in round one, and check or adjust their views, documenting changes in views and expectations was not part of the consultation process. Nonetheless, in the various discussions, the long timeframe of most large-scale mining projects was a prominent point of discussion. This had implications for how the guideline itself sought to address long-term impacts.

Key features of the new guideline

The final guideline provides a comprehensive, yet reasonably succinct, document that relates SIA to each phase of the pre-existing NSW EIA process. The guideline includes:

  • objectives of SIA in each EIA phase

  • SIA steps to undertake in each EIA phase

  • SIA outputs for each EIA phase

  • roles of the proponent, departmental officers, the community, and other stakeholders

  • reference to useful and practical tools

  • supplementary material in 20 pages of appendices, including a list of review questions.6

This section describes how the content of the guideline sought to reconcile the gaps between leading practice and SIA performance in NSW as identified in the literature and in the community consultations. It describes how and why the new guideline covers four key topics: context, interlinkages, impact type, and data diversity.

SIA that puts the project into context

The project team sought to develop a guideline that was universal enough to offer consistency, yet flexible enough to enable SIAs to be tailored to specific contexts (Suopajärvi 2013). The guideline defines SIA as an iterative process requiring continuous improvement and adaptive management systems that account for complex impact pathways and interactions in particular contexts. It emphasises the importance of ongoing SIA, and continuing to assess, monitor, report, and manage social impacts over time, during the mine-life-cycle, and beyond closure and relinquishment.

Rather than prescribing how to conduct SIA, the guideline encourages proponents to apply methods that are appropriate to the context, and to describe and defend their choice of methods. Understanding context includes understanding the social, environmental, and historical trends. The guideline expects proponents to ‘document the trajectory of a change over time and give a dynamic benchmark against which potential impacts can be assessed and any change monitored’ (NSW DPE 2017b, p. 39). The guide notes that the scope of the study should be determined on a case-by-case basis, and that impacts may extend beyond a single project locality.

The guideline stipulates that SIA should be proportionate to the nature and scale of the project and its potential impacts. It encourages proponents to conduct SIAs that are responsive to material issues, where materiality considers the extent, duration, and severity of the impact, and levels of stakeholder sensitivity and concern/interest. The guideline also asks proponents to pay attention to changing circumstances, and to recognise that predictions may not always be accurate.

SIA that recognises interlinkages

The EP&A Act 1979 requires consent authorities to consider the likely impact of project developments ‘on both the natural and built environments, and social and economic impacts in the locality’ (s. 79C (1)(b)). The Act does not indicate how the interrelationships between these dimensions should be assessed. There are many ways in which social impacts interact with environmental and economic impacts. For example, health impacts may be linked to air and water-quality; impacts on the built environment can affect quality of life; and employment has economic and social dimensions. In NSW, SIAs form a sub-section of an EIS. This approach has been criticised because it renders social considerations subsidiary to environmental considerations, and it de-links SIA from other assessments (Esteves et al. 2012). The new guideline (NSW DPE 2017b, p. 7) requires these linkages to be made explicit, through synthesis, integration, and cross-referencing between social, environmental, economic, and other specialist assessments.

While the guideline encourages disciplinary linkages, other linkages could be strengthened. For instance, the guideline encourages individual proponents to assess how impacts could accumulate if numerous projects are situated in a particular locality, but gives limited practical guidance as to how an individual proponent can achieve this. Considering the impacts of a single project or action rather than the full range of stresses on the social context is insufficient to keep the total effects of all stresses at acceptable levels, and to enhance opportunities through co-ordination (Franks et al. 2010). In the context of the pre-existing policy framework, however, placing the onus on proponents to assess the combined impact of various activities over time is not feasible. For the moment, the single, stand-alone and individual approach to project assessment remains intact in NSW.

Assessing positive and negative impacts

Leading-practice SIA considers adverse impacts, as well as benefits that may accrue to local communities. Vanclay et al. (2015, p. 11) advocate that ‘sustainable social development’ should be the goal of project development, suggesting that the positive versus negative reading of impacts creates an unnecessarily binary assessment framework. However, in NSW, comprehensive assessment of both positive and negative social impacts was not common, let alone conducting assessments through a holistic framework that accounts for future generations and impacts throughout the mine life-cycle (Michell and McManus 2013). Most resource developers restrict their discussion of positive social impacts to social investment inputs, projected employment levels, and local business opportunities, without analysing social impacts (e.g. improvements in health and wellbeing flowing from meaningful employment).

To encourage a more comprehensive approach, the guideline stipulates that proponents should identify and assess both positive and negative social impacts, ensuring that risks are adequately managed and opportunities realised and enhanced (NSW DPE 2017b, p. 19–20, 41–45). The guideline details those factors that should be considered in the analytical process. It also notes that mitigation measures should relate directly to the adverse impacts identified. In other words, proponents are required to demonstrate how proposed measures (which may include social benefits) will avoid, reduce, or mitigate negative social impacts, rather than assuming that positive contributions automatically offset negative impacts.

SIA that utilises a diversity of data

The NSW guideline defines social impacts broadly, highlighting that they can be physical and/or based on experience or perceptions, and they may be quantifiable and/or qualitative. Leading SIA practice should incorporate data generated during stakeholder participation, as well as expert scientific data. The dual objective of the SIA guideline is therefore to improve the process of public participation in SIA, and improve the data and information available to decision makers. This is a deliberate response to the view that the worst forms of community engagement in SIA are ‘little more than a feeble attempt at project legitimisation’ (Esteves et al. 2012, p. 37).

The guideline includes a dedicated section on the role of community engagement (or public participation) in SIA. It explains how proponents can enable the participation of vulnerable and marginalised groups; maximise diversity and representativeness in data collection; and engage Aboriginal peoples in culturally appropriate ways, at different stages in the SIA process. More broadly, it identifies the objectives of engagement in SIA, suggests methods for identifying who to engage, and offers examples of relevant engagement techniques aligned with the IAP2 (2006) spectrum of participation.

The guideline positions community engagement as a vital means of primary research to inform the SIA. It explains that engagement should consider the views of potentially affected and interested people in a meaningful way. This can include drawing on secondary data, such as previous assessments, local planning initiatives, and other technical studies, as a basis for engagement. Proponents are encouraged to use insights from community engagement to ‘inform project planning and design, mitigation and enhancement measures, and monitoring and management frameworks’ (NSW DPE 2017b, p. 12). Supporting the use of diverse forms of data, the guideline also presents 12 principles, derived and adapted from Vanclay (2003) and Vanclay et al. (2015). These principles promote ongoing stakeholder engagement, and include impartiality, inclusivity, materiality, and transparency.

While the guideline does not conflate community engagement and social research, the case presented for conducting social science research is not as strong as the case for conducting community engagement. This inadvertently may lead proponents to see community engagement as a substitute for rigorous social research, whereas both are essential inputs to SIA. Social science research can inform community engagement, and can be used as a part of engagement processes (alongside scientific research from other disciplines). Likewise, engagement can benefit from scientific research on social issues, rather than relying on stakeholder perceptions alone. Social science research has much to offer beyond engagement, and engagement processes can benefit when they use social data as inputs; that is, by helping to identify what research is needed, and by using this research as a basis for engagement.

The guideline also specifies the selection criteria for consultants preparing SIAs, in terms of qualifications, experience, and organisational affiliation. SIA lead authors are additionally required to declare that the report contains no false or misleading information. As they currently stand, these provisions do not require consultants to be independent from the proponent, leaving assessments open to perceptions of bias. However, DPE is now investigating ways to enhance professional practice requirements through a broad review of EIA, including independent peer review (NSW DPE 2018).

Conclusion

This paper sought to outline the challenges associated with developing a guideline that reflects leading-practice SIA concepts and principles, within a pre-existing planning system. It also sought to describe the outcome of this process in terms of the key features of the new guideline, and specifically how they contrast with prior SIA practice in NSW. By applying leading-practice principles of SIA, the project team incorporated participatory methods that actively sought a diversity of views on the guideline and its application to State-significant resources projects. A participatory process also helped the project team to identify key aspects of SIA practice that needed to be included in the guideline for it to be responsive to stakeholder needs. Producing a public document that explained how DPE responded to the issues raised reinforced this process-content link.

While the guideline represents a significant advance in policy-based SIA guidance, some aspects leave room for improvement. For example, guidance on assessing cumulative impacts and health impacts is sparse, and the issue of human rights (e.g. Kemp and Vanclay 2013) was not incorporated because of difficulty aligning this issue with pre-existing NSW legislation. There is provision to revise the guideline over time, particularly as the broader review takes shape. This provides opportunities to integrate emerging ideas and address Preston's (2014) fourth challenge of a changing social context.

The test of the guideline’s impact will lie in its influence on SIA practice in NSW, and ultimately in social outcomes for communities affected by resources projects. The NSW Government has also undertaken to extend and adapt the guideline beyond the resources sector, to all major projects, and to apply the lessons learned from this project. In the meantime, we would encourage applied researchers and SIA practitioners to track the implementation of the guideline in specific contexts.

Acknowledgements

The authors would like to thank the anonymous reviewers for their comments on a previous version of this paper. They would also like to thank staff at the NSW Department of Planning and Environment for their role in developing the SIA guideline, and others who provided advice, submissions, and ideas for improving the draft version of the guideline.

Disclosure statement

No potential conflict of interest was reported by the authors.

Notes

1. The Queensland Government released an updated guideline as this article was under review.

2. While these developments are progressive from a historical perspective, they did not specify how proponents should give attention to indirect, intangible, positive, or cumulative impacts, or to specialist impact assessments (e.g. health and human rights).

3. These provisions are scheduled for implementation in 2018.

4. According to schedule 1 of the State Environmental Planning Policy (State and Regional Development 2011), ‘State significant developments’ (SSDs) include: all coal, mineral sands and underground coal gasification projects; mining, petroleum and extractive industries in an environmentally sensitive area of state significance; or mining, oil and gas development or related works (including processing plants) with over $30 million of capital investment.

5. The EP&A Act was revised in October 2017, although revisions did not specifically mention SIA.

6. The list is based on Vanclay et al. (2015) and was designed to support a comprehensive approach to SIA, rather than ‘box-ticking’.

References

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