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Part III - Communicating the message

Published online by Cambridge University Press:  18 April 2020

William J. Sutherland
Affiliation:
University of Cambridge
Peter N. M. Brotherton
Affiliation:
Natural England
Zoe G. Davies
Affiliation:
Durrell Institute of Conservation and Ecology (DICE), University of Kent
Nancy Ockendon
Affiliation:
University of Cambridge
Nathalie Pettorelli
Affiliation:
Zoological Society of London
Juliet A. Vickery
Affiliation:
Royal Society for the Protection of Birds, Bedfordshire
Type
Chapter
Information
Publisher: Cambridge University Press
Print publication year: 2020
Creative Commons
Creative Common License - CCCreative Common License - BYCreative Common License - NCCreative Common License - ND
This content is Open Access and distributed under the terms of the Creative Commons Attribution licence CC-BY-NC-ND 4.0 https://creativecommons.org/cclicenses/

Chapter Sixteen Citizens and science: media, communication and conservation

Libby Lester
University of Tasmania
and Kerrie Foxwell-Norton
Griffith University
16.1 Introduction

In 2016 a full-page advertisement was placed by 56 Australian scientists in the Brisbane Courier Mail. The context of the advertisement was the continuing commitment of Australian governments, federal and state, to coal mining and coal-fired power stations despite overwhelming evidence connecting this activity to the severe damage being suffered by the Great Barrier Reef (Hoegh-Guldberg, Reference Hoegh-Guldberg2015). As well as presenting their scientific credentials in the advertisement – together they had devoted more than 1200 years to studying climate change, marine ecosystems and the Great Barrier Reef – the scientists prioritised the Reef’s economic value over its conservation values. The burning of fossil fuels, they wrote, is ‘directly threatening a major economic resource. The World Heritage listed Great Barrier Reef earns multiple billions for the economy and provides jobs to tens of thousands of Australians’ (Courier Mail, 2016). ‘[T]here can be no new coal mines …’, the scientists demanded, and ‘No new coal-fired power stations’.

This attempt to influence public opinion and thus political outcomes through media appeared in the face of what is now recognised as one of the world’s most notable failures in conservation: the continuing destruction of a global nature ‘superstar’. We suggest in this chapter that such public acts are often rendered futile because of a poor understanding of the communicative processes underpinning the research-to-policy pathway. This is troubling given the risks some scientists – working within expectations of independence and measured professional response – take when entering public debate. But this is only part of the story. While many scientists do not have the necessary communication skills or knowledge to join controversial debates (Besley & Tanner, Reference Besley and Tanner2011) or have been burned by previous experience (Dunwoody, Reference Dunwoody, Hansen and Cox2015), there is also evidence that others see themselves as remote from the public sphere, a messy space of negotiation and contest that has a clearly troubled relationship with fact (Besley & Nisbet, Reference Besley and Nisbet2013; Dudo & Besley, Reference Dudo and Besley2016; Simis et al., Reference Simis, Madden and Cacciatore2016).

In this chapter, we highlight aspects of this disconnection between environmental science and public debate and policy outcomes from a media and communication perspective. We begin by briefly outlining recent approaches to mediated environmental communication. We then turn to the communication of science more specifically. We argue that models of science communication and public engagement with science need to more explicitly acknowledge issues of power, complexity and conflict within the context of the contemporary media landscape. To conclude, we offer suggestions for how science and communication can be better equipped to influence environmental debate and decision-making.

16.2 Mediated environmental communication

As a starting point, we need to recognise the inherently political nature of environmental and conservation sciences – that even at their least political, they seek to influence behaviours and outcomes, and at their most political they are resisting global pressures for intensified use of land and water and increasing demand for and movement of resources. The politics of the environment consistently test our capacity to civilly negotiate a shared future (Cox, Reference Cox2012; Dryzek, Reference Dryzek2013), whether that concerns the composition of our atmosphere or the fate of a small localised fishery (Murphy, Reference Murphy2017). That environmental activists and journalists are greater targets of violence than ever before in many parts of the world is evidence not only that resource management and conservation are areas of conflict, but that what is said, how and to whom clearly matters (Cottle et al., Reference Cottle, Sambrook and Mosdell2016; Lester, Reference Lester, Tumber and Waisbord2017). Media and communication are central to this flow or containment of environmental information and meanings. As such, here we briefly outline key ideas from communication and media studies as they relate to environmental debate and decision-making.

As others before them, media and communication scholars have turned to nature for useful metaphors to help describe some of the dynamism and complexity they now witness. ‘Media ecology’ is a popular term to capture the interconnection of various media systems, platforms, technologies, genres, formats, and producer and audience practices driving media production and distribution (Altheide, Reference Altheide1994; Singer, Reference Singer2018). How, and to what extent, this metaphor should be applied remains contested (Maxwell & Miller, Reference Maxwell and Miller2012; Lester, Reference Lester2019). Nevertheless, a focus on interconnectivity within media and communication is useful in highlighting the interactions and dynamism of contemporary spheres for public and political negotiation (Habermas, Reference Habermas and Burger1989; Fraser, Reference Fraser2007).

An immediate outcome of applying this metaphor is the redundancy of the definite article in relation to ‘media’. Once it may have made sense to refer to ‘the media’ as a bounded entity, in which media companies hired journalists, editors and camera operators to produce information in the form of news and entertainment that was circulated via newspapers and broadcast outlets to readers and viewers. Now, the use of ‘the’ in front of ‘media’ is as anomalous as it would be if used in front of ‘nature’. Media are no longer separable from our social lives or indeed our environmental futures (Deuze, Reference Deuze2012). Media shape and frame our everyday life, including political decisions. They are the principal means through which we form a shared understanding of the world and come together to debate and negotiate common risks and concerns.

A second outcome of recognising ecological-type interconnectivity within a media and communication context is the acknowledgement of interaction. It is almost impossible to isolate environmental concerns and risks and the decisions they prompt to a defined locality. When residents in Mackay, Queensland, protested against the impacts of the proposed port expansion on the Great Barrier Reef, they entered a world that stretched communicatively from their local newspaper, to a series of NGO-established hashtags, to transnational corporations that sell ice cream, to European banks, to a US president and his daughters, to international governance bodies (Lester, Reference Lester2016; Foxwell-Norton & Lester, Reference Foxwell-Norton and Lester2017). And back again. Claims by industry of a ‘social licence to operate’ can be challenged when an ‘affected public’ is no longer defined as those living within a 20-km radius of a development site. We might all consider ourselves affected when the future of the Great Barrier Reef is concerned, and media and communication provide us with the means of engaging, and the sense that we have a right and duty to be involved openly in decisions about its future (Volkmer, Reference Volkmer2014).

Dynamism is the third element to be considered. As the traditional business model for the production of news has collapsed, numerous other forms of information production and circulation have emerged. All are constantly adjusting and changing their practices in relation to one another. NGOs collate and publish information on illegal logging in places where it is now too dangerous or expensive for income-losing news organisations to send their journalists. Citizens establish community websites for local audiences or single-issue blogs for targeted business readers. News outlets campaign on climate change to attract subscribers, or do not cover climate change at all if it attracts too few site visits. Other media outlets closely guard a political and/or conservative readership, muscling out potential competitors with tactics sometimes bordering on bullying, in order to maintain a reputation for political influence (McKnight, Reference McKnight2012). Meanwhile, audiences have more choices than ever on what news they will receive and via what platform, self-selecting, re-selecting and screening sources, topics and subject matter via news feeds, hashtags and new sites selection.

Power plays a key role in structuring this interconnected, interactive and dynamic system. Within media and communication, power appears in diverse and often surprising forms, and even ownership of mega-media companies is no guarantee of uninterrupted influence, as both Rupert Murdoch and Mark Zuckerberg have experienced. Power is never certain, although it holds true that some conditions enhance the capacity to control information as it travels. Information emanating from institutional settings, such as universities, scientific organisations, courts, parliaments or international governance bodies, can often travel with authority for longer than NGO-sponsored communications. However, the long-running clash in the Southern Ocean between the NGO, the Sea Shepherd Conservation Society, and the Japanese government-backed whaling fleet provides an excellent example of how geography impacts this. Throughout much of the conflict, Sea Shepherd was able to capitalise on the remote location of the conflict, from which journalists were absent, by producing and distributing images and messages that circulated within media relatively unchallenged. Symbolic power is key here. No amount of Japanese government-sponsored public relations or ‘scientific knowledge’ was able to successfully counter the messages carried by the bloodied corpses of ‘charismatic megafauna’ (McHendry, Reference McHendry2012; Cox & Schwarze, Reference Cox, Schwarze, Hansen and Cox2015).

Environmental NGOs have pioneered the strategic management of symbolic power within media and communication, and here conflict is often a necessary component. Sophisticated multi-pronged campaigns with minimal financial resources have threatened and interrupted the multimillion-dollar flow of goods and capital. The campaign aimed at Japanese buyers of Tasmanian native timbers involved a young woman in a tree with a laptop and a daily blog (albeit for over a year); a string of social media-active international backpackers and celebrity visitors; a single campaigner in Japan translating various media texts; and access to the email addresses of key corporate and social responsibility personnel in relevant Japanese companies (Lester, Reference Lester2014). The Sarawak-based forestry company at the centre of the trade quickly altered its business practices in Tasmania once the Japanese companies withdrew from contracts rather than be seen to be failing to meet their own environmental procurement principles.

This terrain is media saturated, and the role of media and communication is more than mere conduits for data or messages. Modern environmental conflict is hugely influenced by media, as the ‘product of mutually constitutive interactions between activism, journalism, formal politics, and industry’ (Hutchins & Lester, Reference Hutchins and Lester2015, p. 339) enacted in the public sphere. Activists’ strategies and campaigns, journalistic practices and news reporting, formal politics and decision-making processes, and industry activities and trade coalesce to enact moments of environmental conflict in public view. These moments of conflict largely centre on the legitimate dimensions of local, national and international policy and law, underpinned by the pursuit of environmentally sustainable development (Konkes, Reference Konkes2018; Foxwell-Norton & Konkes, Reference Foxwell-Norton and Konkes2019).

For example, state, NGO and industry responses to Japanese whaling conflicts in the southern oceans drew heavily upon the duties of signatories to the International Convention for the Regulation of Whaling, that for over 30 years has delivered a commercial whaling moratorium. Sea Shepherd undertook protest action, with international laws and policy aiming to deliver whale conservation underpinning its media-based efforts, holding nations and industries to institutional and public account. Science was used both to support conservation via the International Whaling Commission (IWC) and to challenge it via the research claims of Japanese whaling fleets. Meanwhile, the IWC’s pursuit of conservation management plans, sanctuaries and marine parks has been underpinned by science that seeks to balance whale populations with the impacts of industry, even when not explicit. Science and scientific knowledge are thus very much a part of these conflicts, powerful, contested factors in contemporary social relations.

Media and communication form an interconnected, interactive and dynamic system, in which power, conflict and threat to established practices and order are always evident. As with any complex ecology, this is delicately balanced and easily interrupted, constantly adjusting and shifting as its component parts struggle for sustainability and/or dominance. They remain integral to the formation of public opinion and the political influence that follows, but contemporary flows and networks of information make the paths from source to policy more difficult to predict than ever. In the next section, we contrast this view of media and communication with that circulating around environmental sciences.

16.3 Communicating environmental sciences

If the view we have presented of media and communication is of a highly political, dynamic and complex system – one that is central to social life and environmental decision-making, but that does not easily lend itself to being understood or charted via neat models – the environmental sciences can present a near opposite view. Communication here is often an add-on activity, and ‘the media’ considered a relatively stable platform or tool to deploy as needed in order to change public opinion and produce policy outcomes. Indeed, a key premise in recent literature is the idea of ‘protecting science communication’ from the dynamism and noise characteristic of public debate and controversy, and of an active separation of science communication from political communication (Hall Jamieson, Reference Hall Jamieson, Hall-Jamieson, Kahan and Scheufele2017; Kahan et al., Reference Kahan, Scheufele, Hall Jamieson, Hall-Jamieson, Kahan and Scheufele2017). Here, ‘science and its communication’ rather than ‘communication and its implications for science’ has underpinned scholarship, leaving science seemingly remote from, rather than a part of, the public.

In considering how this situation has developed, we turn to a subset of literature that is not so interested in public understanding of science as scientists’ understanding of ‘the public’. In a review of findings from surveys of scientists, Besley and Nisbet (Reference Besley and Nisbet2011) found that, when asked about the role of the public, ‘scientists may opt for some type of co-decision-making but also suggest a desire by scientists to differentiate themselves from the public’. Their relevant findings include the following.

  • Scientists say the main barrier to ‘greater understanding of science’ among the public is lack of education. Media are second.

  • Scientists see the public as homogenous – although experience interacting with the public can bring a more nuanced view. Scientists perceive policy-makers as the most important group with which to engage, with the public in the mid-range of importance – somewhat more important than young people or NGOs, but less important than the private sector and educators.

  • Scientists appear to rely on a simple sender–receiver model of media effects that fits poorly with contemporary media research, that is, they ‘tend to favour one-way communication with the public via the media, viewing engagement as chiefly about dissemination rather than dialogue’ (Besley & Nisbet, 2011, p. 653).

Overall, scientists are willing to engage directly with citizens but ‘such engagement is usually still framed in terms of providing information’ ‘to increase citizen knowledge’ (Besley & Nisbet, 2011), while addressing the knowledge deficit and/or ‘scientific literacy’ still dominates scientists’ communication goals (Peters & Dunwoody, Reference Peters and Dunwoody2016).

This transmission model of communication (Shannon & Weaver, Reference Shannon and Weaver1949) – underpinned by a desire for a clear channel of communication that protects the message on its route from sender to receiver – has serious implications for public understanding, awareness and/or engagement with conservation and other sciences. It epitomises frustrated attempts to eliminate ‘noise’ – that is, to control the ‘message’ on a path to the public or policy and decision-makers. In the case of science, and more specifically conservation and ecology, the greatest ‘noise’ is the sound that resonates in the public sphere when citizens and scientific expertise collide. Exploring this noise requires a thoughtful and critical examination of the structural characteristics of this collision, and how this may impact the passage of scientific knowledge to citizens. This is difficult work, occurring in a space where diverse publics and communities with a range of understandings about scientific expertise and/or the primacy of economic imperatives reside. Instead, a range of contexts, influences and often conflict await the path of scientific knowledge to the public. Public understandings of science cannot be divorced from these social processes, and a ‘pure and protected’ science message, unsullied by politics, is unlikely to arrive untouched at its destination audience.

Citizens enter the public communication of science as social, political and cultural beings with a range of historical and contextual nuances. The underlying assumption of communication as mere transmission of data – as a controllable process – will often fail to register the impacts sought and may act to reinforce the communicative distance between scientific expertise and the citizens to whom their message is directed. While some effort has been made to abandon communication models that are based upon ‘knowledge deficit’, the model is still evident in many attempts to distribute scientific research and findings to the public. A carefully crafted tweet, a multimillion-dollar documentary or a full-page advertisement framed by 1200 years of expertise and experience of Great Barrier Reef scientists or equivalent is communication that often underestimates the conditions within which these citizens reside. What is heard by the public can be quite distant from the sender’s intent.

16.4 Better conservation communication

We suggest some key strategies that might help in the communication of conservation. The starting point must be a consciousness of one’s own role – a critical self-reflexivity – that positions science and its communication as only one of many domains of legitimacy and authority in conservation debates and efforts. There are other sources that carry legitimacy and authority in the public and private lives of individuals, institutions and their societies and these also command a place in public communication about conservation. This ‘communication noise’ cannot be bypassed and is indeed a distinctive characteristic of the current era. When conservation science enters this messy sphere of debate, it becomes enmeshed in the public realm of politics and political communication. Efforts to ‘secure’ a message to an audience, even via the expensive production of one’s own media content, underestimate communication’s complexity and unstable networks of connectivity. Seeking innovative collaborations with communication scholars, and inviting their meaningful participation in the constitution and design of research projects, is one way in which conservation scientists might better prepare their work for public deliberations.

Popular messages are not necessarily wedded to scientific rigour, expertise or fact. In the twenty-first century, scientists are encouraged to communicate their knowledge widely, making it increasingly susceptible to challenge and disrepute. An understanding of how science is embedded and implicated in processes of public debate and negotiation may reorient these communication strategies. For example, by prioritising the scientific and economic imperatives to protect the Reef, as evident in our opening example, the scientists could actually have affirmed the powerlessness of the public in relation to the destruction of the Reef, especially when even experts are compelled to take out full-page advertisements in a state newspaper. Conversely, communicating the Reef as a scientific fact and an economic resource may alienate already marginalised public sentiments that do not prioritise this message in their own experience of or relationship with the Reef.

Further, when scientific messages are framed with deliberate reference to the ‘economy’, including the tourism and mining industries, the impacts of mining and tourism on the Great Barrier Reef and the science are (again) diluted by a perhaps unwitting collusion with industry – as has been repeated in the history of Reef policy and protest moments (see Foxwell-Norton & Lester, Reference Foxwell-Norton and Lester2017; Foxwell-Norton & Konkes, Reference Foxwell-Norton and Konkes2019). Conservation science may do better to elevate the impact on the Reef’s ecology, and return to its messages of connectedness between human and natural systems. Is the Reef not worth protecting in itself? In the 1960s, the emergent discipline of ecology was evoked to argue that a mining lease on one part of the Reef would have dire consequences for the entire Reef ecosystem (McCalman, Reference McCalman2013). This ecological approach requires ongoing critical reflection on the concept of ‘ecologically sustainable development’ and the relationship of research to a system of industrial development that threatens ecologies everywhere (Redclift, Reference Redclift2005). Suffice to say, much public trust in science is at stake in these reflections.

In the longer term, better conservation communication can also be fostered in training and development. The distance between the ‘two cultures’ or, more specifically, the humanities, arts and social sciences and that of the science, technology, engineering and mathematics disciplines, is shrinking, but not fast enough. Clearly, neither ‘culture’ alone is sufficient to arrest the current trajectory of ecological decline. As researchers, we must continue to challenge false dichotomies that diminish scholarly contributions to conservation efforts – from global superstar ecologies like the Great Barrier Reef to the local ecologies of the places we live (Foxwell-Norton, Reference Foxwell-Norton2018). This distance can also be lessened in the design of degree programmes and training courses, giving current and next-generation science communicators access to different ways of thinking about their role, their potential place in public sphere debate, and the public.

In the twenty-first century, where networks of communication link individuals and civic institutions through digital media and mobile communication, a sophisticated understanding of communication is power (Castells, Reference Castells2013). Communication scholars are well-equipped to assist scientists, and their disciplinary communicators, to extend existing understanding of communication, media and journalism. This entails a re-examination of what is meant by ‘science communication’ and its current strategies to engage citizens in support for, and trust in, its work and expertise. Currently, such collaborations overwhelmingly favour scientific expertise, leaving communication expertise (beyond media industry experience or production expertise) underrepresented, despite its potential to add critical dimensions to scientific research and projects. Deeper collaborations could better explore the challenges and capitalise on the opportunities that emerge where communication is pervasive, ubiquitous and complex.

16.5 Real ‘citizen science’?

In liberal democratic societies, science enters the public sphere of debate with a menagerie of mitigating concessions and qualifications. Conservation ecology and science communication that seek to engage the public cannot be protected from these complexities: they are sine qua non to human societies. Communication between science and citizens in the twenty-first century is further impacted by the complex, interconnected network of communication technologies, practices and transnational flows characteristic of the modern experience. The public sphere that scientific knowledge enters is not a level playing field for all participants. Even ‘pure’ science messages are exposed to the unevenness wrought by conflict involving power, wealth, industry and politics.

Our Reef scientists and the scientific community are clearly attuned to the power of media in addressing environmental conflict and the public, hence the advertisement. We have questioned, however, whether such a blunt tool underpinned by a transmission model of communication is likely to result in the protection of the Reef intended by these scientists. We assert that messages, even those that seemingly carry the credibility and authority of scientific expertise, are confused and contorted by ‘communication noise’. This embeds science in the dirty politics of public sphere debate, rather than beyond the politics of knowledge, position and power. Early communication scholar John Dewey expressed these ideas at the turn of the twentieth century:

Society not only continues to exist by transmission, by communication, but it may be fairly said to exist in transmission, in communication. There is more than a verbal tie between the words common, community and communication. Men live in a community in virtue of the things they have in common; and communication is the way in which they come to possess things in common. What they must have in common in order to form a community or a society are aims, beliefs, aspirations, knowledge – a common understanding – like mindedness as the sociologists say. Such things cannot be passed physically from one thing to another like bricks; they cannot be shared as persons would share a pie by dividing it into physical pieces.

Opportunities are repeatedly missed and frustration grows in part because communication is assumed, and the scientists’ ‘camera’ faces out when what is needed is a science ‘selfie’ – a critical self-reflexivity capable of understanding not only the science but how science might be heard once it leaves the minds of experts and enters the community (Foxwell-Norton, Reference Foxwell-Norton2018). Understanding this requires ‘knowing thyself’ as a product of a peculiar set of historical circumstances that have legitimised and given authority to scientific messages but also as part of the politics of the public sphere – where citizens (including scientists) reside and knowledges circulate. Citizens must be the target of science messages in order to shift voting behaviour for a politics that gives due reference and regard to best conservation practice. This is clearly, from a communication perspective, the terrain upon which the Reef scientists are operating, albeit unconsciously. The core problem is that science communication understands itself, and largely gathers its authority and legitimacy, by defining its terrain in terms of ‘science’ rather than communication.

Science communication is very clear about the merits of bringing science to society, but is found wanting in the reverse, of the importance of bringing society to science. This is a tragic flaw, especially relevant at the current juncture when communication networks mean science is everywhere, visible and not, elevated and undermined, in every moment in society. As a starting point, there are a few key strategies that can begin to mitigate against the repetition of the ‘communication breakdowns’.

  • Improve scientists’ understanding of the ways in which their knowledges enter the public sphere of political debate and the politicised nature of their own knowledge.

  • Acknowledge that conservation science is understood by the public in terms mostly not answerable to, or cognisant of, scientific rigour or research.

  • Enter the arena of media-immersed environmental conflict willing to participate alongside and through other interests of politics and decision-making, including activist groups, industries and government.

  • Accept there can be no divorce of any aspect of conservation science from these politics, as it hampers meaningful engagement between science and its publics.

  • Take the ‘scientific selfie in society’ that shows the flaws, the unknowns and the occasional exhilaration.

A thorough and candid examination of the relations between citizens and scientists in a media-saturated society is, we suggest, extraordinarily hard science. It is, however, science that is critical to the development of new directions in the public communication of conservation science.

16.6 Acknowledgements

This chapter draws on research supported by the Australian Research Council’s Discovery Program (DP150103454 ‘Transnational Environmental Campaigns in the Australia-Asian Region’) and the Griffith Centre for Social and Cultural Research.

Chapter Seventeen Campaigning to bring about change

Cathy Dean
Save the Rhino International
and Amy Hinsley
University of Oxford
17.1 Introduction

This chapter examines campaigning: what it is, when it is needed and who conducts campaigns. Drawing upon examples from the NGO conservation sector, we discuss how to plan and execute a campaign, and explore the different types of campaign: behaviour change, policy change and fundraising. Finally, we consider some of the potential pitfalls, including a lack of a strong evidence base, overstating claims of success, the introduction of bias, conflicting views of co-organising partners, the inappropriate use of emotion and the risk of unintended consequences.

17.2 What is campaigning?

Campaigning, also described as influencing or advocacy, is about creating a change. Whether the aim is to reduce trade in the horn of a threatened species of rhino, protect the habitat of a rare population of wild orchids, raise funds for a workshop or the ongoing costs of species monitoring, or change the law on the import of hunting trophies into a country, conservation NGOs campaign to create change. The desired change may be to address the root cause of a conservation problem, such as demand-reduction or behaviour-change campaigns, or the campaign may be focused only on mitigating the effects of a problem, as in the case of grants to improve law enforcement activities that prosecute wildlife traffickers. Some organisations may decide to focus on campaigning to tackle both the cause and the effect.

17.3 When is campaigning appropriate?

Campaigning can be appropriate in a diverse range of situations: from local to global issues, from high-profile to emerging conservation problems, from long-term to opportunist responses. While campaigning is often on high-profile and well-known conservation problems, it may also be used to mobilise or harness existing public support for less well-known or emerging issues, or to tackle issues with impacts at a global scale.

In a recent opportunistic, but highly effective example, several NGOs launched campaigns to urge the public and policy-makers to phase out single-use plastics after the high-profile BBC documentary Blue Planet II, screened in the UK in December 2017, highlighted the problem of plastic pollution in the world’s oceans. The programme showed footage of a pilot whale cow carrying her dead calf for days, with the calf’s death linked to the possibility of its mother’s milk being poisoned with toxins accumulated through the food she had been eating. The combined messaging gained considerable public attention, and in April 2018 the UK Government launched a consultation to explore the possibilities of banning plastic straws and other single-use plastics. While this consultation follows on from other action to reduce plastic usage that took place before these campaigns, such as the introduction of charges for plastic bags in 2015, increased public pressure likely highlighted the issue as a priority at this time. Indeed, the then Environment Secretary Michael Gove reportedly stated that he had been moved by the BBC programme (Rawlinson, Reference Rawlinson2017). In addition, several large companies responded to pressure from consumers by pledging to reduce or phase out single-use plastics.

Campaigning can also be used to give a voice to those without one. NGOs focusing on humanitarian relief or disadvantaged groups of people will often tell the story of a single person as a microcosm of the wider issue. Conservation causes, whether endangered species or ecosystems, are not able to speak for themselves, and NGOs often use ‘ambassador’ animals, such as Sudan, the last male Northern white rhino (euthanised in March 2018 after experiencing an increasing number of age-related problems), which came to embody the long, sorry history of the doomed attempts to conserve the species. Sudan became the focus of numerous fundraising campaigns to generate income for assisted reproduction technologies to try to ‘recreate’ the subspecies.

Finally, campaigning is sometimes the only action possible, especially when the scale of the problem is large or cannot be addressed without state or international intervention (such as plastics in the ocean). One successful example took place in 2002, when campaigning by Project Seahorse played a central role in the listing of all seahorse species on Appendix II of the Convention on the International Trade in Endangered Species of Wild Flora and Fauna (CITES), meaning that international seahorse trade was regulated and monitored for the first time (Project Seahorse, 2018). Through policy recommendations informed by scientific research, Project Seahorse highlighted the huge scale of trade in seahorses and the threat to wild species that unregulated and unsustainable trade was posing. With up to 20 million seahorses traded annually, this listing represented an important step towards sustainability of this trade.

17.4 Who campaigns?

Campaigns can be created and delivered by individuals, groups or organisations, whether commercial or charitable. NGOs are particularly associated with campaigning; their fundamental objective is to make the world a better place, and they have members who feel strongly about the issue in hand. NGOs are often very close to their service users and beneficiaries, and can therefore use evidence from their direct experience to highlight changes needed, whether to attitudes, legislation or budgets. The examples in this chapter are drawn from the conservation NGO sector.

A common cause can bring together disparate voices to create a collective campaign that is louder, more wide-reaching and more effective than could be achieved by any single organisation. The campaign to create a marine reserve around the Pitcairn Islands began in 2011, when the Pew Environment Group’s Global Ocean Legacy project first discussed with Pitcairn islanders the idea of establishing a large-scale marine reserve within their waters. A number of organisations and celebrities then became involved in the campaign, including the Great British Oceans Coalition, National Geographic, the Zoological Society of London, Hugh Fearnley-Whittingstall, Gillian Anderson, Julie Christie and Helena Bonham-Carter; the Pitcairn Island Marine Reserve was eventually legally designated in September 2016.

17.5 Planning a campaign

A well-designed campaign cycle will begin by analysing and selecting the issue, followed by developing the strategy, planning the campaign, delivering it, monitoring progress, evaluating impact and drawing out learning. More complex campaigns may research and develop different strategies and pilot them before conducting monitoring and evaluation on the different groups to determine the most effective strategy. They may begin by establishing an evidence base, developing a theory of change, and embedding within that the system of monitoring and evaluation, to include targets, indicators and means of verification.

Campaigns usually employ a call to action, which will differ depending on the target audience and the chosen goal. Such calls to action need to consider their target audiences. For example, a campaign to conserve water in Europe and the USA may ask people to turn off the tap while brushing their teeth, whereas a water conservation campaign in sub-Saharan Africa may ask farmers to introduce night-time drip irrigation for their crops to minimise evaporation.

If there is no budget previously set aside for the campaign, then funds need to be raised. Communications staff need to work on how to articulate the campaign’s concepts and frame the debate. Finally, the organisation needs to be ready to implement the change, perhaps in partnership with others, with all the resources required, and to be able to manage that implementation without detracting from its ongoing work.

17.6 Types of campaigns

Campaigns generally fall into three categories: bringing about behaviour change, bringing about policy change, or raising funds. We consider each of these in turn and, for each category, we give an example of a successful campaign, seeking to highlight the aspects that, in our view, contributed to that success.

17.6.1 Campaigning to change behaviour

Many campaigns aim to change human behaviour, to reduce the incidence of behaviour that is in some way harmful to wildlife or ecosystems, or promote positive behaviour. Changing behaviour is different to raising awareness of an issue, which involves simply communicating the nature of a threat or conservation problem in the hope that the public or policy-makers will take action. Increasingly, the effectiveness of raising awareness in changing a person’s behaviour is being questioned (Christiano & Neimand, Reference Christiano and Neimand2017).

Greenpeace’s palm oil campaign of 2010 (Greenpeace, 2010) targeted both the people buying Kit Kats and Nestlé, the manufacturer. A one-minute video shows a bored office worker shredding documents while watching the clock until 11:00 and his break. He tears open the wrapper of a Kit Kat. We, the viewer, see that the wafer finger is actually an orangutan’s finger, complete with furry knuckle and nail. The chocolate bar drips into his keyboard; oblivious, he wipes his mouth and spreads a smear of blood. The video ends with a call to ‘Stop Nestlé buying palm oil from companies that destroy the rainforests’. A link to Greenpeace’s website, with suggestions for how concerned viewers could take action, was provided. Greenpeace reported 1.5 million views of the advert, more than 200,000 emails and phone calls to Nestlé HQ and countless comments posted on Facebook. This, combined with protests at Nestlé AGM and its headquarters all over the world, and meetings between Greenpeace campaigners and Nestlé executives, resulted in swift action. Nestlé developed a plan to identify and remove any companies in their supply chain with links to deforestation so their products would have ‘no deforestation footprint’, although it has been reported that they have since backtracked on these commitments (Neslen, Reference Neslen2017).

In a contrasting example, campaigns to increase consumer awareness of the impact of their purchases on overfishing, including labels for certified sustainable products, have been found to have little effect on purchasing choice or consumer demand (Jacquet & Pauly, Reference Jacquet and Pauly2007). Therefore, it is essential that behaviour-change campaigns go beyond simple awareness-raising and base their messages on sound research into when, where, how, why and by whom the behaviour is occurring.

Lynn Johnson has developed a useful pyramid (Figure 17.1) to show the difference between behaviour-change and awareness-raising campaigns. However, the majority of so-called behaviour-change campaigns actually operate at the awareness-raising level, rather than that at the demand-reduction level. Programme managers dealing with the direct consequences of poaching understandably must feel frustrated when they see substantial funds being invested in ineffective efforts to change consumer behaviour in the main consumer countries for illegal wildlife products.

Figure 17.1 Model showing differences between behaviour-change and awareness-raising campaigns developed by Nature Needs More Ltd for its Breaking The Brand RhiNo Campaign.

(Breaking The Brand, 2016)

Doug Mackenzie-Mohr (Reference Mackenzie-Mohr2011) has written extensively about fostering sustainable behaviours and has broken down the steps involved. The process starts by identifying which behaviour you want to change and in whom, while also considering when and where they exhibit this behaviour. The next step involves identifying what might be stopping people from changing behaviour, and what the incentives might be for doing so. This allows informed strategies to be developed that consider the design of the messaging but also other factors, such as how social norms can be used to reinforce the desired behaviour. These strategies should then be fully tested in a pilot phase before full-scale implementation, with monitoring and evaluation throughout.

Although behaviour-change campaigns focused on illegal products often suffer from a lack of available data on consumers, there are examples of targeted campaigns that have carefully planned their messages based on evidence. In 2014, TRAFFIC in Vietnam launched the Chi campaign, a behaviour-change campaign based on consumer research into the groups most likely to buy illegal rhino horn. This research established that the key driver for the consumption of rhino horn was its ‘emotional’ value rather than its ‘functional’ (i.e. medicinal) value and that the main users were wealthy businessmen aged between 35 and 50 living in Hanoi and Ho Chi Minh City (TRAFFIC, 2013). They valued the strength and power of the animal that had been killed to obtain it, but also the scarcity and high cost of rhino horn and the difficulty of obtaining it; being able to do so demonstrated the extent of the buyer’s networks. Having segmented the consumer market, and with the information on the motivations of the prime target audience and the drivers of consumption, there was little point in launching a campaign that relied on photographs of traumatically dehorned rhinos, or on debunking beliefs that rhino horn could cleanse the body of toxins following chemotherapy. Instead, the campaign focused solely on the importance of ‘Chi’, an inner power and strength that negated the need for rhino horn. While it is too early to evaluate the success of this campaign, it is a good example of the careful designing and tailoring of messages to a specific situation that should be employed in campaigns of this type. Audience segmentation is a commonly used approach of subdividing populations into groups with shared characteristics, such as socio-demographic, behavioural or psychographic profiles (Wedel & Kamakura, 2000).

17.6.2 Campaigning to bring about policy change

When it comes to bringing about a change in policy, NGOs usually try to both influence and inform the target audience, who may be legislators or Members of Parliament. They may employ methods that include media campaigns, public speaking, commissioning and publishing research, online petitions (change.org and avaaz.org are two of the most popular English-language online petition websites), organising protest marches or demonstrations, recruiting advice from experts, or making direct approaches to legislators or Members of Parliament on the issue concerned.

In 2017, a group called Two Million Tusks was concerned about the plight of African elephants and the UK’s role in the global ivory trade. They researched the quantity of ivory being sold through UK auction houses and whether those auctioneers were compliant with the UK’s rules on ivory trade. The resulting report, published in October 2017, exposed weaknesses in auction houses’ compliance and called upon the Department for Environment, Food and Rural Affairs to ban all trade in ivory within the UK (Two Million Tusks, 2017). While the debate about ivory sales has been long-fought, a linked television programme, presented by Hugh Fearnley-Whittingstall, revealed new concerns. He arranged for eight ivory items on sale in UK antiques shops to be radiocarbon-dated, and found that three of the pieces were from modern, i.e. post-1947, ivory, and as such could not be legally sold in the UK. During a televised press briefing on this finding, the then Environment Minister, Andrea Leadsom, came under sustained pressure to address the UK’s role in laundering ivory from poached African elephants; the eventual result was a Bill to restrict severely the conditions under which ivory can be sold in the UK.

17.6.3 Campaigning to raise funds

Fundraising wisdom says that the most effective calls for donations are ones that engage the audience(s) on an emotional level (Hill, Reference Hill2010). Handling such messaging can be challenging: whether to use images that provoke negative (horror, disgust) or positive (empathy, inspired) emotions; whether to hold donors to ransom (‘Unless we act now, this species will go extinct’) or focus on success stories; whether to focus on a single, named animal as an ambassador for its species, while being clear that donations will be spent on a wide range of activities, or on a species or habitat as a whole.

In the UK, the Fundraising Regulator, formerly known as the Fundraising Standards Board, sets and maintains the standards for charitable fundraising in England, Wales and Northern Ireland, and aims to ensure that fundraising is respectful, open, honest and accountable to the public, and regulates fundraising practice via The Code of Fundraising Practice (Fundraising Regulator, 2016). Its guidance on ‘Content of Fundraising Communications’ says that organisations: must not imply that donations will be used for a specific purpose if they will be allocated to general funds; must be legal, decent, honest and truthful; must make it clear if they alter any elements of real-life case studies; and must give warnings about and be able to justify the use of any shocking images.

In October 2014, Save the Rhino International (SRI) began planning its annual fundraising appeal for 2015. The decision was made to focus on Kenya, which had not benefited from previous appeals and which had suffered a spike in rhino poaching in 2013, when 59 rhinos were killed, as compared to 29 the previous year. SRI had a long history of supporting rhino conservation efforts with its in-country partners. It was suggested that a focus on the canine units employed by Lewa Wildlife Conservancy, Borana Conservancy, Ol Jogi Conservancy and Ol Pejeta Conservancy, as part of their anti-poaching and community engagement strategies, would provide an interesting and engaging angle for a public fundraising appeal. These units use Belgian Malinois and bloodhounds for tracking (i.e. following poachers’ scent trails) and/or detection (i.e. dogs are trained on specific scents to be able to carry out, for example, vehicle searches at road blocks). A name for the appeal, ‘Rhino Dog Squad’, was chosen as being descriptive, punchy and memorable.

Based on results from previous appeals, SRI’s primary objective for the appeal was to raise a total £40,000 for the three canine units in Kenya by February 2016, of which £30,000 would come from a campaign marketed to the general public and £10,000 from zoos via spin-off campaigns.

Three distinct target audiences were identified: the general public/animal lovers, particularly those with pet dogs, living in the UK, continental Europe or the USA, across a broad age range, with some but not detailed knowledge of the rhino poaching crisis; high–net-worth individuals who have visited or have links with Kenya; and zoo visitors. Save the Rhino applied successfully to BBC Radio 4 to have the Rhino Dog Squad featured as one of the station’s charity appeals: this greatly increased the charity’s ‘reach’ to the first audience.

SRI’s appeal planning team realised early on that the choice of presenter would influence the script, and considered the merits of having a celebrity record the appeal versus one of the Kenyan field programme staff. In the event, SRI recruited Sam Taylor, Chief Conservation Officer at Borana, to read the script, giving SRI an opportunity to personalise the script. Furthermore, knowing that the appeal would be broadcast just before Christmas 2015 (twice on the last Sunday before Christmas and once on Christmas Eve) meant that the SRI team had to consider where radio listeners would be, and how to engage their emotions at such a time.

The BBC Radio 4 appeal alone raised more than £22,000, with the Rhino Dog Squad in total realising about £60,000 by 31 March 2016; some donors set up standing orders and funds are still being received for the canine units at the time of writing (June 2018). The BBC said that the appeal was one of the most successful of its type, and attributed this to:

  • a knowledgeable presenter: having someone who worked at one of the beneficiary conservancies read the appeal meant that it could be written in a way that was highly personal and credible;

  • an unusual script: the first words of the appeal were ‘Sausage bonus! Now there’s an image to conjure with. I’m guessing you don’t often see the words “Sausage bonus” in a budget. I do, in my work as Conservation Officer in a wildlife sanctuary in northern Kenya’. The first two words caught and held the attention, as Sam went on to explain how the canine units help the rangers with their work;

  • making the most of the timing: SRI knew that listeners would likely be at home with their families, wrapping presents, decorating the tree or beginning to cook Christmas meals. Contrasting listeners’ lives at Christmas with that of the rangers in Africa would be powerful. ‘This Christmas, as you enjoy time with your families, friends and your pets, please remember our dogs and rangers. They’ll be at work, protecting Africa’s wildlife. Please help the Rhino Dog Squad’;

  • the famous British love of dogs: ‘We use bloodhounds and Belgian Malinois, and they’re awesome. They can track scent for up to three days. They’re better than a bullet – they can go around trees and hold poachers until our rangers can safely make an arrest. The dogs work at roadblocks, detecting rhino horn, ivory, and weapons. We also use them to help find lost children or recover stolen property. Our dogs are part of our team’;

  • the wider appeal held by SRI: in addition to the BBC 4 appeal, SRI had planned a strong social media campaign with many assets: ezines, blogs written in advance ready to be posted, lots of high-quality images (including photographs taken during a visit in March of dogs tearing into parcels wrapped in Christmas paper containing bones and toys), and a main 4-minute film supported by four supplementary 2-minute films.

17.7 Potential pitfalls for campaigns
17.7.1 Lack of a strong evidence base

While reports of incredible successes offer good news stories for conservation and boost the reputation of the organisations that carry out the campaign, there is the risk that once the evidence base (where it exists) is questioned, the outcomes turn out to be not quite the success story that they initially appeared. Although in the majority of cases this may just lead to wasted donor funds and NGO time, there are also examples of where this has created a conservation problem in itself.

A good example is the ‘Save the Bay, Eat a Ray’ campaign that followed all of the rules for a good campaign. It used clear messaging to communicate a simple evidence-based action that members of the public could take to help restore Chesapeake Bay: eating more cownose rays (Rhinoptera bonasus) (National Aquarium Baltimore, 2016). The evidence said that a huge population increase of cownose rays was decimating the Bay’s oyster populations, and some also claimed that the species was invasive. However, further analysis of the science found that the models used were flawed and, not only was the ray a native species that was not responsible for the decline, it was itself extremely vulnerable to overfishing (Grubbs et al., Reference Grubbs, Carlson and Romine2016; National Aquarium Baltimore, 2016). In this case, a lack of robust scientific evidence relating to the ecology of the system led to negative conservation consequences, even if these outcomes were intended in the first place.

Behaviour-change campaigns can become particularly complex when they are based around reducing the use of illegal wildlife trade products. Communicating messages to the consumers of an illegal product is difficult because, if admitting to using the product could result in some kind of punishment, even identifying the consumers of it will be a challenge (see Chapter 5 for a discussion of approaches to gathering information about sensitive topics, including illegal resource use). Often, in-depth research focusing on consumer preferences and behaviour is needed to understand motivations for consumption (e.g. Nuno & St John, Reference Nuno and St John2015; Hinsley et al., Reference Hinsley, Verissimo and Roberts2015). However, behaviour-change campaigns are often carried out by NGOs without the time, expertise, resources or capacity to do this kind academic research. This has resulted in several campaigns based on very little knowledge of who the target audience should be, often using high-profile celebrities or eye-catching graphics to get the message out to as many people as possible, with the hope that this will include the actual consumers of the product. Unfortunately, it is not possible to say whether this works: a recent review found that almost no behaviour-change campaigns focused on wildlife consumers report evidence of impact, and very few carry out any kind of robust evaluation at all (Veríssimo & Wan, Reference Veríssimo and Wan2018). One way to address this could be greater collaboration between NGOs that do not have in-house scientists and academics, to ensure that campaigns are based on good scientific evidence, and that results are analysed in depth to evaluate the impact.

17.7.2 Over-stated claims of success

Some NGOs have focused their behaviour-change campaigns at children, banking on the ‘pester-power’ factor (cf. Figure 17.1, activity that ‘Educates segments of the population who don’t currently use rhino horn, e.g. children’). Humane Society International, for example, launched a campaign aimed at stopping the use of illegal rhino horn in Vietnam via a book called I’m a little Rhino that was used in schools to help teach children about rhino poaching concerns and conservation efforts. No information is available on how the campaign was designed, targeted or evaluated, but claims that demand for rhino horn had fallen by 77% in Hanoi following the campaign have been heavily criticised by conservation practitioners (Roberton, Reference Roberton2014).

17.7.3 Bias in campaigns

One of the dangers of advocacy/campaigning is that it may not be sufficiently inclusive or consultative. For example, the NGO leading the campaign may have a particular stance on a controversial issue, or an NGO with a direct line to a Member of Parliament or Minister may be able to exert undue influence.

For example, IFAW, Lion Aid and the Born Free Foundation, among others, have worked closely with a group called ‘MEPs for Wildlife’ (MEPs are Members of the European Parliament). While there was an initial focus on banning the hunting of canned lions (canned hunts are trophy hunts in which an animal is kept in a confined area, such as in a fenced-in area, increasing the likelihood of the hunter obtaining a kill), MEPs for Wildlife expanded its efforts to call for an EU-wide ban on the import of lion trophies, in keeping with decisions made by the Netherlands, French and Australian governments.

However, as an IUCN Briefing Paper for European decision-makers explains (with reference to the then recent and still notorious case of ‘Cecil the Lion’, shot in July 2015):

Intense scrutiny of hunting due to these bad examples has been associated with many confusions (and sometimes misinformation) about the nature of hunting, including:

  • trophy hunting is the same as ‘canned’ hunting;

  • trophy hunting is illegal;

  • trophy hunting is driving declines of iconic species, particularly large African mammals like elephant, rhino and lion;

  • trophy hunting could readily be replaced by photographic tourism.

None of these statements is correct. (IUCN, 2016)

The Briefing Paper goes on to conclude that ‘legal, well-regulated trophy hunting programmes can – and do – play an important role in delivering benefits for both wildlife conservation and for the livelihoods and wellbeing of indigenous and local communities living with wildlife’ (IUCN, 2016).

Making the case for positions, particularly ‘unpopular’ ones such as advocating for well-run trophy hunting, is extremely difficult to do. The IUCN Briefing Paper includes two graphs on rhinos and trophy hunting: the first showing the change in estimated numbers of Southern white rhino in South Africa before and after limited trophy hunting was introduced in 1968; and the second showing growth in estimated total numbers of black rhino in South Africa and Namibia before and after CITES approval of limited hunting quotas (a maximum of five animals per country per year, and even then only if suitable candidate animals can be identified) in 2004. Both graphs show populations increasing exponentially until the current poaching crisis began (IUCN, 2016).

Numerically speaking, the evidence in the Briefing Paper is conclusive: trophy hunting of rhinos, while fatal for the individuals concerned, has not adversely affected the species’ meta-population growth. Simultaneously, it has generated incentives for landowners (government, private individuals or communities) to conserve or restore rhinos on their land; and generated revenue for wildlife management and conservation, including anti-poaching activities. This does not hold sway, however, with NGOs that are ideologically opposed to trophy hunting.

17.7.4 Conflicting views

It would be wrong to assume that all conservation NGOs speak with a common voice. The Global March for Elephants and Rhinos (GMFER) has become a worldwide campaign, taking place in more than 160 cities in 2016, and thus enabling people from many different countries to take part. In the beginning, the march was about ‘raising awareness, generating global media attention on the crisis, and keeping political pressure on world leaders to protect our endangered wildlife’. Such broad aims made it possible for a broad church of elephant- and rhino-focused conservation organisations to take part in the march.

However, in more recent years, the GMFER has focused on banning trade in ivory and rhino horn, including applying pressure on South Africa to maintain a ban on domestic rhino horn trade (the ban was eventually overturned in early 2017) and on Japan and Hong Kong to ban online and domestic sales of ivory. A number of NGOs that are working to tackle the rhino and elephant poaching crises are actually pro-sustainable use, and have taken the decision not to participate in GMFER’s annual event, because its aims were incompatible with their own.

17.7.5 Inappropriate use of emotion

Conservation or animal welfare/animal rights NGOs must tread a fine line when campaigning about emotive subjects. Some of the most difficult images to view are those showing animal abuse or suffering, bushmeat and the impact of poaching. A photograph that is too upsetting will result in the viewer turning the page quickly without taking in the call to action.

There are ways around this challenge. Photographs of dead elephants with their tusks hacked out certainly tell the story behind the poaching crisis, but so too does Nick Brandt’s monochrome image, Line of rangers holding tusks killed at the hands of man, Amboseli 2011. As the photographer writes (Brandt, Reference Brandt2015),

I wish that I had never had to take this photo. I wish that it had never been possible to take this photo. The photo was taken as a deliberate visual echo of Elephants Walking Through Grass, a very different world – a vision of paradise and plenty – taken only a couple of miles away three years earlier. But instead of a herd of elephants striding across the grassy plains of Africa, we see only their remains: the tusks of 22 elephants killed at the hands of man within the Amboseli/Tsavo Ecosystem.

Brandt’s post goes on to hold out hope in the form of the work being done by Big Life Foundation’s rangers; a good example of a strong image, which does not in itself provoke feelings of disgust or revolt in the viewer (Fundraising Regulator, 2016), but which explains the catastrophe that has occurred and offers a way of helping to solve the problem.

17.7.6 Risk of unintended consequences

Ensuring that communications are well-designed and that the campaign’s main messages are evidence-based can make achieving the ultimate aim more likely, but it does not always protect against unintended, often negative, consequences of the campaign.

To date in conservation there has not been enough robust evaluation of campaigns to measure the occurrence of unintended consequences, but evidence from other fields demonstrates the risk. In the field of health, the risk of unintended consequences is well-recognised. For example, multiple studies have found that campaigns aimed at reducing drug and alcohol consumption frequently create so-called ‘boomerang effects’, where the result is an increase in consumption rather than a decrease (Ringold, Reference Ringold2002). This extent to which this phenomenon may be occurring in response to demand-reduction campaigns for high-profile wildlife products is unknown, but the complexity of these markets and the use of conflicting messages by different groups may increase the risk. For example, the legal bear bile trade in China has been the focus of extensive campaigns by animal welfare organisations, with the ultimate aim of closing down all bear farms. While some campaigns use the ineffectiveness of bear bile as a medicine as the key message, others instead focus on the cruelty of the farms, or the health risks to consumers of using farmed bile, such as the 2012 Healing without Harm campaign (Watts, Reference Watts2012). While these messages may be intended to close down the market for bear bile, and with it the farms themselves, little is known about how regular consumers of bile – who believe that it is an effective treatment for a serious condition, such as liver cirrhosis – will react. For example, will these consumers switch to wild-sourced bear bile instead where it is available, or will they start using another product? Currently there is little evidence either way, making this a risky strategy for conservation. To mitigate this, campaigns should fully consider all potential consequences of their messaging and evaluate the risks of carrying out the campaign before it starts, drawing on existing evidence from other fields.

Another problem area lies in the way that illegal wildlife trade products are described by some NGOs, which is then repeated in the media. Products such as orchids, pangolin scales and rhino horns are often described as rare and hard to obtain by well-meaning organisations or researchers. However, in markets that often prize rarity, such messages can increase consumers’ desire for the forbidden item, the acquisition of which will demonstrate both their wealth and their ability to use their networks to obtain it. For example, specialist consumers of slipper orchids, all species which are on CITES Appendix I, have been found to be willing to pay more for a rare species (Hinsley et al., Reference Hinsley, Verissimo and Roberts2015). Although several of these species have already been collected to near extinction for trade (e.g. Paphiopedilum canhii: Rankou & Averyanov, Reference Rankou and Averyanov2015), highlighting their rarity is likely to be counter-productive. Similarly, mentioning high prices for wildlife products can raise awareness of their value among both consumers and traders, and organisations like TRAFFIC and Wildlife Conservation Society have drawn up clear internal guidelines for their staff, explaining why they should never discuss the black-market price of an illegal wildlife product.

17.8 Future directions for campaigns in conservation

Campaigning to bring about change is central to much of conservation action, and it is essential that the importance of a well-designed campaign is recognised and appreciated. There are numerous examples of campaigns that have brought about change, many that did not achieve their intended goals, and even more that have never been carefully evaluated. As described in this chapter, the most successful campaigns will undertake careful planning and tailor their messages to the specific aim and context to ensure that they engage the target audience effectively. Other important steps include clear goal-setting, development of indicators and means of verification; monitoring, and a comprehensive evaluation of outcomes.

Competition for donor funds or the support of the public can sometimes mean that collaboration and open dialogue between different conservation actors is not always a priority. However, partnerships between different NGOs can extend the reach of a campaign and provide new perspectives, and collaboration with academics can provide a strong scientific research base for its design. Possibly the most important action should be to share lessons learned from successes and failures, as this is an important way that campaigns can continue to improve and avoid the pitfalls described here. These steps are essential, as a good campaign cannot only prevent the waste of donor funds, but increase the likelihood of conservation delivering change for the common good.

Chapter Eighteen Behavioural insights for conservation and sustainability

Toby Park
The Behavioural Insights Team
18.1 Introduction

Many of society’s ailments and ambitions, from obesity and corruption to economic growth and conflict, are ultimately about human behaviour. Sustainability and conservation challenges are no different, and although legal, economic and engineering solutions will be key, so will a shift in individual actions around resource use and waste, diet, fishing and agricultural practices, wildlife consumption, tourism and beyond (Rowson & Corner, Reference Rowson and Corner2015). Policy-makers, educators and conservation NGOs are therefore unavoidably in the business of behaviour change, but the conventional toolkit of regulation, incentives and information provision is increasingly being recognised as incomplete, and too rooted in a rudimentary model of human behaviour (Shafir, Reference Shafir2013).

On the rise is a more realistic understanding of behaviour, drawing on the latest insights from behavioural economics, social marketing and cognitive and social psychology. By harnessing these new tools we can radically improve policy and campaign outcomes and achieve greater social impact (Halpern, Reference Halpern2015). The field is rapidly growing in some parts of the sustainability community, as well as in public health, international development and consumer finance, but conservationists have so far been slow to embrace the behavioural perspective (Reddy et al., Reference Reddy, Montambault and Masuda2017). This is now beginning to change, particularly among NGOs faced with explicitly human challenges such as poaching, corruption, the illegal consumption of wildlife and common pool resource depletion, including water and coastal fisheries.

In this chapter I provide an overview of behavioural insights for sustainability and conservation, aimed at readers with little prior expertise in the subject. I do this by first reviewing a conventional understanding of behaviour change, discussing its shortcomings and then presenting some additional strategies.

18.2 A flawed starting point – rational choice

In both economics and psychology the dominant models of behaviour have historically been rooted in the concept of subjective expected utility, describing individuals as making rational choices that maximise the benefits to themselves (Scott, Reference Scott, Browning, Halcli and Webster2000) (see also Darnton, Reference Darnton2008, for a review of behaviour-change models). The axioms underlying these models are first that behaviour is cognisant and deliberate; second, that we are self-interested in the sense that we maximise our own utility as defined by our preferences, typically construed as wealth, enjoyment or subjective well-being; and finally that the locus of decision-making is the individual, implying a degree of indifference to context (Becker, Reference Becker1976).

In economics, this account of behaviour is formalised in standard micro and macro models, and has long provided the dominant intellectual framework for policy, regulation and law, business and finance, international development, public health and natural resource management. Indeed, the economic concept of cost–benefit analysis is highly analogous to this understanding of behaviour, implying we make choices by carefully trading off pros and cons. Among environmental campaigners and educators the language draws more from the field of psychology, speaking of values and attitudes rather than preferences and utility, but the assumptions of intentional, reasoned and individual choice are usually still implicit.

With this conventional model of behaviour in mind, a suite of tools for behaviour-change emerge, and capture the bulk of government and NGO activity.

  1. 1. Regulation. Influencing our behaviour through the threat of sanction via bans, quotas or standards.

  2. 2. Economic levers. Self-interest is harnessed by making pro-environmental behaviours the more appealing option, typically through the provision of economic incentives including taxes, subsidies, fines, grants, or payments for eco-services.

  3. 3. Social marketing and attitudinal campaigns. An attempt to alter our preferences, values or attitudes by promoting greater environmental concern.

  4. 4. Information provision. Assuming pro-environmental values to be present, people cannot act on them if they have flawed beliefs or lack awareness of the environmental impact of their choices. This information deficit may be overcome through education, awareness-raising, guidance, or product labels and kite marks. In practice, the line between ‘merely’ providing information and attempting to influence our attitudes is often blurred.

18.3 Going beyond conventional wisdom

A great deal has been achieved through the above approaches. In particular, regulation and economic incentives can be highly effective, reflecting the fact that self-interest is a powerful driver of behaviour. Information provision can also be effective if information deficit is a major barrier – product labels can have powerful effects in otherwise shrouded markets, for example. Raised awareness is also often a critical step towards building public consent for big-ticket policy initiatives, such as a carbon tax or the banning of wildlife products (Marteau, Reference Marteau2017; Portney et al., Reference Portney, Hannibal and Goldsmith2018). In and of itself, however, awareness is often not enough to shift individual behaviour due to the dominance of other factors, such as competing motivations or practical and psychological barriers to action (Barr, Reference Barr2004; Olander & Thøgersen, Reference Thøgersen2014).

The wider criticism is that these tools, and the behavioural assumptions underpinning them, overlook important aspects of human nature. I highlight three insights below as particularly in need of greater focus, before outlining some additional tools that emerge from these insights.

18.3.1 The importance of context

By focusing on the individual as the locus of behaviour, rational accounts of behaviour fail to recognise the extent to which our actions are shaped by the social, physical, economic, political and cultural context (Shove, Reference Shove2009). Indeed, evidence suggests that interventions that alter the setting in which choices are made, by making the desired behaviour cheap, convenient, politically cultivated and socially normative, are often more effective than those which focus solely on individual beliefs, attitudes and choices (Thøgersen, Reference Thøgersen2014). They do, however, require fundamentally different levers than conventional information-provision approaches often relied upon by conservation NGOs, targeting not the individual’s unsustainable choice, but the socio-technical structures which encourage unsustainable practices to flourish.

18.3.2 The importance of non-conscious processes

This sensitivity to context is best explained by dual-process models of cognition, which define two parallel systems of mental activity. One is slow, reflective, cognisant and deliberative. This system most resembles rational choice, although more accurately is boundedly rational, operating under limited information and cognitive bandwidth, and usually aiming to satisfice (find a good enough solution) rather than to optimise (Simon, Reference Simon1972). The second system, which dominates more of our decision-making than we tend to realise, is fast, largely automatic and driven by intuitive processes such as ingrained habit, emotion and heuristics (mental shortcuts) (Kahneman, Reference Kahneman2011).

These fast-and-frugal processes are mostly unreflective responses to cues in our social and physical environment, and hence our great susceptibility to external influence. They also leave us susceptible to predictable errors of judgement, or cognitive biases, as we trade-off accuracy for cognitive efficiency. For example ‘choose the middle option’, ‘stick with the default and the familiar unless there is a strong reason to risk the unknown’ and ‘do what most people like me appear to be doing’ are all heuristics we instinctively adopt – serving us well enough most of the time without demanding much mental resource, but often leading us to err from optimal decisions (Kahneman, Reference Kahneman2011). Designing environments, and campaigns, which reflect these more automatic processes can be an effective strategy for enabling and encouraging more sustainable behaviour (Thaler & Sunstein, Reference Thaler and Sunstein2008).

18.3.3 The importance of behaviour over values, attitudes and beliefs

Conservation campaigns typically attempt to raise awareness and elevate pro-environmental values, on the premise that greater concern for the planet, or a species or habitat, will drive financial support or more sustainable behaviour. However, it can be difficult to engage citizens in these issues. Research shows that pro-environmental information often has the intended impact only on those already sympathetic to the message, as we update our views asymmetrically, skewed towards the direction of our prior convictions (Sunstein et al., Reference Sunstein, Bobadilla-Suarez and Lazzaro2016). This observation is rooted in confirmation bias – our tendency to gravitate towards information which corroborates our existing views, while we discount, ignore or distort information which challenges us (Nickerson, Reference Nickerson1998).

That said, encouragingly, the battle for hearts and minds is slowly being won: pro-environmental attitudes are now common across much of Europe, for instance (Steentjes et al., Reference Steentjes, Pidgeon and Poortinga2017). This is helping to raise the policy agenda (Carrington, Reference Carrington2019). However, few citizens are independently giving up their cars, overseas holidays or beef burgers. It would also be naïve to expect fishers, farmers, poachers and loggers to compromise their livelihoods so willingly. Clearly, there is more to behaviour change than awareness and attitudes, highlighting the problem of a widely observed value–action gap (Kollmuss & Agyeman, Reference Kollmuss and Agyeman2002). The reasons for this gap are myriad and complex, although two broad categories are worth highlighting: insincerity of our values and barriers to acting on them.

First, pro-environmental values are frequently in tension with self-interest, creating cognitive dissonance and guilt for habits we are unwilling to forego. Guilt can be a powerful motivator for action, but we also have a tendency to resolve this dissonance not by curbing our unsustainable behaviour, but by ignoring the issue (wilful ignorance), or employing various acts of psychological fudging, including motivated reasoning (rationalising towards a convenient and ego-serving, rather than logical, conclusion), moral licensing (excusing ourselves the flight because we recycled) and biased social comparisons (inflated convictions that ‘I do more than most’ and deferring responsibility to government/industry/other countries) (Barkan et al., Reference Barkan, Ayal and Ariely2015). In other words, our behaviour reveals that our concern for cost, profit, convenience and enjoyment frequently outranks our concern for the planet, despite our ability to maintain sincere environmental values and a sense of integrity – the psychological equivalent of having our cake and eating it (Shalvi et al., Reference Shalvi, Gino and Barkan2015; Gino et al., Reference Gino, Norton and Weber2016).

Second, even where intentions are sincere, we may fail to act due to various psychological and practical barriers. These include hassle, a lack of options, lack of know-how, upfront cost barriers, lack of willpower, lack of self-efficacy (belief that we can make a worthwhile difference), procrastination, forgetfulness, ineffective planning, ingrained habit and various cognitive biases that favour a ‘do-nothing’ strategy, including loss aversion, present bias, uncertainty-aversion, inertia and risk-aversion. These factors constitute the second major element of the value–action gap (Webb & Sheeran, Reference Webb and Sheeran2006), and although they often seem trivial, they can be disproportionately impactful. They therefore deserve disproportionate attention when designing interventions and campaigns to help bridge the divide between good intentions and action. For example, helping people plan better to reduce food waste, removing the hassle of switching to a green energy tariff, providing easy substitutes to medicinal wildlife products, or providing timely reminders and tips for reducing water consumption are all strategies which can help turn green aspirations into green actions.

18.4 Effective strategies for promoting conservation behaviours

With the above points in mind, the most effective route to change, whether tackling wildlife crime, energy conservation, or the protection of common pool resources, is often a ‘twin-track’ approach (Burgess, Reference Burgess2016). The aim is to target both the individual (motivations, decision processes, habits, emotional engagement, attitudes and awareness) and the enabling environment (ensuring that policy, the built environment, social norms and incentives promote and facilitate the sustainable behaviour). These are often two sides of the same coin: the choices we make as individuals are often inseparable from the enabling environments in which we make them.

Below, I briefly outline four levers for change that span individual forces on behaviour and three key environmental dimensions: social, material and economic. Many of the examples given are drawn from other contexts where the behavioural mechanisms are relevant, acknowledging that the use of behavioural interventions is nascent within the field of wildlife conservation (Reddy et al., Reference Reddy, Montambault and Masuda2017).

18.4.1 Inner motives: ego, emotion and meaning

Two fundamental motivations influence our adoption of beliefs and attitudes: to construe our lives in a positive (ego-enhancing) fashion, and to construe them in a way which makes sense and is consistent (Chater & Loewenstein, Reference Chater and Loewenstein2016). Thus, we are rarely convinced by mere truth, but by narrative fidelity and self-enhancement: the extent to which something concords with our prior worldview and with the flattering autobiography we curate in our minds. We also tend to think automatically first (with emotion, intuition, gut instinct) and rationalise second. Thus, our reflective and deliberative faculties often act more as interpreters of our instincts than as executives guiding our judgement (Haidt, Reference Haidt2001).

Therefore, successful campaigns rarely pose cerebral facts or logical arguments, but cater to deeper emotional triggers, operating at the ‘human level’ we have evolved to think at, and are rooted in meaning, plot and personal relevance (Schiff, Reference Schiff2012). This largely explains the identifiable victim effect – our greater tendency to donate or make efforts to save an individual animal/ecosystem/community member than a statistical one (Jenni & Loewenstein, Reference Jenni and Loewenstein1997). It also explains why campaigns evoking guilt or anxiety can lead to disengagement, because these emotions undermine the ego and present uncomfortable truths, inviting psychological defence rather than engagement (particularly if giving up the unsustainable behaviours is difficult or unappealing). In contrast, research suggests that harnessing emotions with positive valance (intrinsic attractiveness), in particular anticipated pride from acting sustainably, can be more effective (Schneider et al., Reference Schneider, Zaval and Weber2017).

Recognising our tendency to find the ‘wiggle room’ to rationalise our self-interested actions also sheds light on wildlife crime. Evidence shows interventions that reduce the ease of rationalisation can be effective. For instance, we can highlight the prevalence of good behaviour to correct self-serving misconceptions that ‘everyone does it’ (see discussion on social norms below). We might also create less-malleable boundaries between acceptable and unacceptable behaviours to constrain our ability to re-frame dishonest actions as acceptable (e.g. we are less likely to steal money than do something which indirectly equates to us acquiring money dishonestly, such as by paying a lower price in cash to avoid taxes). Drawing people’s attention to their moral standards, through religious reminders or honesty commitments, can also be effective by reducing the level of dishonesty we are able to reconcile with our self-concept of integrity (Mazar et al., Reference Mazar, Amir and Ariely2008). Such strategies offer attractive alternatives to fines and punishment, particularly in remote situations where monitoring and enforcement are difficult.

Our social identity (the portion of self-concept expressed by membership of social groups or categories such as gender, race, or political beliefs) is also vital in shaping our beliefs, values and actions. We listen to and mimic people we identify with, like and perceive as credible, but may do the opposite of people in our perceived ‘out-group’ simply as a way of dis-identifying with them (Turner, Reference Turner1991). This is partly why the politicised nature of the environmental debate is so damaging, but also means certain messengers can be disproportionately effective – in the UK, the so-called ‘David Attenborough effect’, for instance (Haynes-Worthington, Reference Haynes-Worthington2018). In China, the efforts of Jackie Chan and other celebrities to campaign against shark-fin soup have led to dramatic reductions in consumption (WildAid, 2014).

The broader point through all of this is that we need to understand and cater to the underlying motivations of individuals involved in the depletion or consumption of wildlife and natural resources. We would be naïve to presume a message of sustainability will, for many people, prevail over potent drivers of self-advancement (e.g. in wildlife corruption or over-fishing), convenience (e.g. in air travel or disregard for environmental protections), pleasure and hedonism (e.g. in eating beef or hunting), status (e.g. in ivory ownership), self-expression (e.g. in car ownership) and so on. This demands pragmatism: sustainable outcomes need not be fought only on the basis of sustainability, restraint or moral duty if these more powerful motivations can be harnessed to good effect. Sometimes this is about choosing the right framing. For example, public health researchers have found that food explicitly sold as indulgent out-sells identical food sold as healthy, and although a niche market for health food surely exists, on average healthy connotations may harm sales even compared to entirely neutral, non-descriptive labels (Turnwald et al., Reference Turnwald, Boles and Crum2017). Similar findings are now emerging in the promotion of sustainable diets (Vennard et al., Reference Vennard, Park and Attwood2019). Other approaches include finding compelling ways to displace or supplant these competing motivations, for example by making sustainable travel significantly cheaper and more convenient than air travel; by tapping into identity and offering more sustainable avenues for self-expression; or by attempting to substitute ivory products with an alternative market for high-status jade carvings (e.g. Burgess, Reference Burgess2016).

18.4.2 Social dimension: peer-influence

The social dimension of our behaviour is particularly relevant to conservation issues because the protection of public resources, including fish stocks, rainforests, freshwater or clean air, frequently depends on collective action and the restraint of personal self-interests for communal benefit. Rational choice theory, painting us broadly as self-serving individuals, highlights the risk of a tragedy of the commons in such circumstances, and suggests taxes on externalities (Pigouvian taxes) or privatisation of resources are necessary to realign individual and collective interests (Ostrom, Reference Ostrom2000).

However, in reality we are deeply social creatures: we have the capacity to cooperate, a tendency to reciprocate and conform to social norms and to shun freeloaders and deviants (Trivers, Reference Trivers1971; Ostrom, Reference Ostrom2000). These are processes of evolutionarily ingrained peer pressure: feelings of social obligation, guilt and desire for public acceptance are the proximate drivers for deeper benefits of group cohesion and collaboration. For example, evidence suggests adherence to social norms, and the taboo of breaking them, has traditionally been enough to ensure sustainable harvesting practices in Madagascar (Jones et al., Reference Jones, Andriamarovololona and Hockley2008). Our objective is to harness and further strengthen these traits.

One effective approach is to highlight the prevalence of a desirable behaviour, harnessing our tendency for conformity, but also for reciprocity: the knowledge that others are contributing to a public good encourages us to do the same. For example, comparing householders’ energy use to their more efficient neighbours reliably reduces consumption by a few percent (Allcott, Reference Allcott2011), and telling hotel guests that most others re-used their towel led to 44% doing so, significantly more than with a conventional environmental message (Goldstein et al., Reference Goldstein, Cialdini and Griskevicius2008). Another strategy is to imply reciprocity more directly. For instance, the conservation charity Rare brokered agreements between downstream and upstream water users. Downstream users financed payments and materials for upstream users in the hope they would reciprocate and be stewards of upstream ecosystems, protecting 16,000 hectares of land in the watershed (Rodríguez-Dowdell et al., Reference Rodríguez-Dowdell, Yépez-Zabala and Green2014).

The corollary is that advertising undesirable norms, often done inadvertently in an attempt to highlight the severity of a problem, can unintentionally license the undesirable behaviour. For example, a US national park suffering the theft of fossilised wood found that thefts increased in response to a sign which read ‘thousands of visitors are taking fossilised wood and deteriorating the natural environment’ (Cialdini, Reference Cialdini2003). Note the connection to an earlier point: we often rationalise selfish behaviours through convenient social comparisons, a form of social licensing through which freeloading can become normalised and resource extraction risks competitively escalating (Dimant, Reference Dimant2017).

Our tendency to adhere to norms is often strengthened by peer observation, because being watched adds real social cost to deviance (Argyle, Reference Argyle1957). Hence, we can promote cooperation in conservation contexts by making behaviours less anonymous and improving the mechanisms for communication, peer monitoring and self-governance within fishing and farming communities (Ostrom et al., Reference Ostrom, Gardner and Walker1994). Public league tables are one way of achieving this: taking an example from a different setting, UK government departments’ energy consumption dropped by up to 22% after publication in a ranked league table. Operating through similar principles of observability, a national park in Costa Rica found that donations were more likely to be made when they were public (Alpizar et al., Reference Alpizar, Carlsson and Johansson-Stenman2008). Making behaviour more observable doesn’t only leverage peer pressure to act pro-socially, but also helps build the perception of a social norm. For instance, solar panels installations have been shown to be ‘contagious’ – neighbours are more likely to install them if other houses nearby have them visibly installed (Plumer, Reference Plumer2015).

18.4.3 Material dimension: choice architecture, nudging and effort

The term ‘choice architecture’ refers to the presentation, setting, or framing of choices. This might include the manner in which ethical investments are presented to pension customers, the design of a plastic bottle return scheme, or the layout of a supermarket, restaurant menu or canteen. We can be greatly influenced by the minutiae of these choice environments, which can therefore be designed to gently promote more sustainable outcomes without precluding freedom of choice or relying on conventional incentives – this is the basis of nudging (Thaler & Sunstein, Reference Thaler and Sunstein2008). Nudges can take many forms, from the provision of timely prompts to the design of information and choice environments. Often they aim to address or directly harness a particular cognitive bias or trait, for example putting sustainable options first on menus in canteens. Such examples barely scratch the surface of the opportunities to use choice architecture, which are well-reviewed elsewhere (Johnson et al., Reference Johnson, Shu and Dellaert2012).

Two particular aspects of our choice environment are in particular worth highlighting: effort and timing. First, we are consummate effort minimisers, and in the words of Nobel prize-winning behavioural economist Richard Thaler, if you want to encourage a particular behaviour, ‘make it easy’ (Halpern, Reference Halpern2015). This has major implications for sustainable behaviours and conservation efforts which, even with good intentions, are often thwarted by minor hassle. Importantly, this goes beyond what might be considered rational, with small friction costs (seemingly trivial points of hassle) having a disproportionate impact on our behaviour and often leading us to act against our best interests or intentions (Behavioural Insights Team, 2014).

Removing or introducing small frictions is therefore a powerful and widely applicable intervention. For example, shaped bin lids that remove the friction of recycling, making it easy to see where to put bottles, cans and paper, have been shown to significantly increase recycling and reduce contamination (Duffy & Verges, Reference Duffy and Verges2009). Similarly, multiple studies have shown that removing the tray from canteens (but allowing plate refills) makes it slightly harder to take too much food, significantly reducing food waste by up to 40% (e.g. Thiagarajah & Getty, Reference Thiagarajah and Getty2013).

One of the most powerful ways to make something easy is to make it the default, in part because we often fail to make an active choice, and in part because defaults are often taken as implicit recommendations or safe/standard options. For instance, one study found a 10-fold increase in the uptake of a renewable energy tariff by making it the default (Ebeling & Lotz, Reference Ebeling and Lotz2015). Similarly, in 2012, UK auto-enrolment legislation changed private pensions from ‘opt in’ to ‘opt out’, leading to a dramatic 42% increase in the number of people saving for retirement, more effective than billions of pounds in subsidies (Department for Work and Pensions (DWP), 2017). Perhaps a natural progression from this success is for pension providers to make the default portfolio an ethical investment – a policy idea surely capable of pushing trillions into the green economy, considering the great majority of us never change our investment portfolio.

Second, timing really matters. We find some behaviours much easier at certain moments, and policies and campaigns should be targeted to harness this fact; for instance, promoting uptake of loft insulation among new home movers while the loft is empty. Similarly, evidence shows that we are more likely to adopt new transport behaviours after disruptions such as a house move or train strike, having been forced to break our usual habits and explore new options (Larcom et al., Reference Larcom, Rauch and Willems2017). This so-called ‘fresh-start effect’ was evidenced by the Behavioural Insights Team in the City of Portland, finding that promotions to use a bike-sharing scheme were nearly four times as effective among people who had just moved home (unpublished data, 2017).

Although some of these examples may seem removed from the field of conservation, the broader point is that it pays to understand the relevant micro-behaviours and processes, as there are invariably points at which default outcomes can be set, timely moments identified and frictions introduced or removed, often with surprisingly large impacts. This might include, for example, making it easier to accurately record fish-take, to apply for licences or land stewardship schemes, or to whistle-blow on poachers and ivory sellers. This approach embraces the concept of radical incrementalism, noting that multiple incremental changes, each targeting a small part of the problem, can sum to dramatic improvements in outcomes.

18.4.4 Economic dimension – incentive design

Incentives are often effective, and there is a large literature in economics devoted to this which I do not cover here. However, they can also have more subtle psychological consequences, and these factors should be considered to maximise their effect and minimise their risk of backfiring.

A key insight is that payments and fines embody meaning beyond their economic value, signalling the desirability of the behaviour and altering its social acceptability and thus interacting with our intrinsic motivation to do something. For example, Swiss residents were found to be less likely to support the construction of a nearby nuclear facility when offered compensation, as the payment implied risk (Frey & Oberholzer-Gee, Reference Frey and Oberholzer-Gee1997). Under such circumstances, common advice is to ‘pay enough, or don’t pay at all’ (Gneezy & Rustichini, Reference Gneezy and Rustichini2000). Similarly, pro-social activities such as volunteering are valuable to those who do them partly because they satisfy a feeling of virtue or duty, which payment can undermine (Ariely et al., Reference Ariely, Bracha and Meier2009). In such cases, non-financial rewards such as public recognition, which can amplify the value of virtue rather than crowd it out, can be more effective (Ashraf et al., Reference Ashraf, Bandiera and Jack2014; Gallus, Reference Gallus2016).

Several studies have similarly highlighted the risk that individual or community payments for conservation outcomes can backfire, crowding out intrinsic motivations. By creating the option of foregoing the payment, these incentives can unintentionally create a guilt-free route to ignoring the conservation agenda, as this is now an option you can ‘pay for’ (e.g. Vollan, Reference Vollan2008). In other words, the punishment becomes more tolerable and morally acceptable, compared to the guilt of breaking local norms, community trust and social obligation – these intrinsic motivators can be a potent form of enforcement.

The importance of self-governance and local norms must therefore be reflected in any outside regulation or incentive scheme, which should aim to support and augment (crowd-in) these intrinsic motivations, not supplant or undermine them (Vollan, Reference Vollan2008). This is not always easy to achieve by design or to predict. One good example from a disparate context is the UK’s £0.05 plastic bag charge, which has led to an 83% reduction in use (HMG, 2017). Such a large impact is implausible through price elasticity alone, but occurs because it reinforces intrinsic motivations by altering the choice architecture: the payment acts as a reminder; the default is now to forego a bag and social expectation of not using one is strengthened – no longer can we unthinkingly use a bag in wilful ignorance, but must proactively and publicly request to harm the planet.

A second cluster of research focuses on designing incentives to harness the heuristics and biases through which we think about costs and rewards. For instance, our tendency to steeply discount the future and bias our attention towards the present (Laibson, Reference Laibson1997) implies effective incentives should be front-loaded and costs delayed. Finance solutions may achieve this, for example to encourage home energy improvements where the reverse (high upfront costs and long-term benefits) is ordinarily a barrier. Similarly, simply redesigning product labels to highlight lifetime cost rather than only the price tag can nudge us towards more energy-efficient purchases (DECC, 2014).

Prospect Theory, an empirical account of our perception of gains, losses and risks (probabilistic outcomes), shows us to be loss-averse, i.e. more motivated to avoid a loss than receive an equivalent gain (Kahneman & Tversky, Reference Kahneman, Tversky, MacLean and Ziemba2013). Implementing this in a literal fashion may be contentious in some contexts but effective: giving teachers a bonus at the beginning of a year and then taking it back if they fail to meet certain performance standards has been found to be more effective than conventional payment on performance (Fryer et al., Reference Fryer, Levitt and List2012). Topical at the time of writing, this bias may prove useful in the UK if we transition from EU agricultural subsidies to a system of payments for conservation outcomes – farmers’ historic receipt of these payments will likely drive a stronger motivation not to lose them compared to new incentives being introduced.

Lotteries can also be a powerful tool. Despite being equivalent in expected utility, we tend to value a 1-in-a-million chance of £1m more than a guaranteed £1, while a guaranteed loss of £1 is preferable to a 1-in-a-million chance of losing £1m. Through the lens of rational choice, this equates to a biased over-weighting of small probabilities. A more intuitive psychological explanation is that we are willing to pay for the hope of winning, or the peace of mind of having no risk rather than some risk. Regardless, lotteries offer creative policy options and are widely usable in many contexts, although they have not yet been tested in a conservation context. In another context, one compelling example comes from China, where authorities introduced state lottery tickets on the back of retail receipts to reduce tax avoidance. The expected value was tiny due to very long odds, meaning an equivalent fixed incentive would be ineffective. However, the disproportionate value customers put on the lottery meant they asked for their receipt, putting the sale on record and making it harder for retailers to evade tax (Wan, Reference Wan2010).

To translate these insights to a sustainability context, imagine a plastic bottle deposit scheme which, rather than returning £0.10 per bottle, entered you into a lottery where every millionth returned bottle won £100,000 (this would yield 35 news-worthy winners per day based on current UK bottle use; House of Commons, 2017). Or – quite hypothetically to illustrate the point – would anyone dare use a plastic bag if rather than being charged £0.05, a spot fine of £1000 was levied on every 20,000th bag-user? Clearly, not all incentive designs are equal through the lens of behavioural science.

In this chapter I have only scratched the surface of what behavioural science can offer the field of conservation, but the key lessons are this: there are myriad influences on our behaviour, many of them contextual and operating through subtle, non-conscious processes. Effective interventions must consider these forces alongside a conventional understanding of regulation, incentives, information and awareness. In doing this, entirely novel approaches are often revealed. Other times, conventional tools can be made more effective. Ultimately, however, the most effective intervention will not be the one which draws upon the most novel finding from behavioural science, but the one which addresses the relevant barriers and motivations. As such, none of these strategies are ‘one-size-fits-all’, but should be brought to bear through a grounded and empirical understanding of the nature of the problem among the population of interest. Sometimes, this may be as simple as making things a bit easier or a bit cheaper.

Chapter Nineteen Social marketing and conservation

Robert J. Smith
Durrell Institute of Conservation and Ecology
Gabby Salazar
Imperial College London
Joseph Starinchak
US Fish and Wildlife Service
Laura A. Thomas-Walters
Durrell Institute of Conservation and Ecology
and Diogo Veríssimo
University of Oxford and San Diego Zoo Global
19.1 Introduction

Most conservation issues stem from people’s actions and choices, so halting biodiversity loss depends on changing human behaviour (Schultz, Reference Schultz2011). The two main approaches traditionally used to achieve such behaviour change are based on education, where people are encouraged to understand and appreciate the natural world, and legislation, where people are punished for breaking rules and laws designed to protect nature (Rothschild, Reference Rothschild2000). Both approaches have advantages, but evidence suggests they are often ineffective because increasing awareness is rarely sufficient to change behaviour (Waylen et al., Reference Waylen, McGowan and Group2009; Chapter 18) and effective conservation legislation in the face of opposing social norms depends on costly enforcement (Cooney et al., Reference Cooney, Roe and Dublin2017). This is why conservation scientists and practitioners increasingly recognise the value of approaches based on social marketing, which seeks to change people’s behaviour for the benefit of wider society by using techniques originally developed in the business world to sell products and services (Smith et al., Reference Smith, Veríssimo, MacMillan, Leader-Williams, Adams and Smith2010; Wright et al., Reference Wright, Veríssimo and Pilfold2015). This link to commercialism makes many conservationists queasy. However, the current extinction crisis shows we need to move outside our comfort zone and consider new techniques with proven success. In this chapter we discuss the use of social marketing in conservation, beginning with definitions of the terms and an explanation of how it differs from conservation education. We then briefly review how social marketing has been used in community-based natural resource management, demand reduction and flagship species fundraising, and end by discussing lessons that relate more broadly to conservation.

19.2 Defining marketing and social marketing

Marketing is widely used in the private sector and is defined as ‘the process of planning and executing the development, value, promotion and distribution of products, services, and ideas to create exchanges that are mutually beneficial’ (Silk, Reference Silk2006). It is an important component of most successful businesses, so it was probably inevitable that other sectors would apply marketing techniques to their work. In particular, this led to the development of social marketing, defined as ‘the systematic application of marketing along with other concepts and techniques to achieve specific behavioural goals for a social good’ (French et al., Reference French, Dip and Blair-Stevens2006). It should be noted that while social media is often used in social marketing, they are not the same thing. Instead, social media is just one type of communication channel, with other examples including radio, billboards and street theatre.

In the behaviour change field, social marketing is seen as one of four approaches (Rothschild, Reference Rothschild2000; Santos et al., Reference Santos, Simões and Atalaia2011). Two of the others, education and law, are widely recognised in conservation. The fourth is technical intervention, which is defined as those aspects of technology, infrastructure or equipment that are critical to enable behaviour change to take place. The appropriateness of these four approaches in a particular context can then be defined based on three components: a person’s ability, opportunity and motivation to change their behaviour. These three components determine whether a person is prone, unable or resistant to behaviour change (Figure 19.1a), and hence which combinations of approaches should be used in response (Figure 19.1b). Law-based approaches should be used when people lack motivation, education-based approaches when they lack the ability and technical intervention-based approaches when they lack opportunity (Figure 19.1b). In contrast, marketing-based approaches are useful in a much wider range of circumstances, because they are designed to overcome a lack of all three components. Moreover, while social marketing and education campaigns are often confused, there are other fundamental differences between the two approaches. In particular, social marketing focuses on exchange, with both sides willing to engage in the transaction and happy with the outcome, whereas conservation education depends on people changing their behaviour for the greater good. In addition, while both approaches are designed with a target audience in mind, this is fundamental in social marketing, and involves identifying and defining the target audience based on factors that relate to their relevant values and interests (Wright et al., Reference Wright, Veríssimo and Pilfold2015).

Figure 19.1 Diagram showing how a person’s ability, opportunity and/or motivation determines (a) whether they are prone, unable or resistant to change and (b) the appropriateness of the four different behaviour change approaches of education, law, marketing and technical intervention (TI) under these different conditions.

(adapted from Rothschild, Reference Rothschild2000; Santos et al., Reference Santos, Simões and Atalaia2011)

Social marketing has been used for over 50 years in areas such as health, development, financial literacy and transportation (Lefebvre, Reference Lefebvre2013) and is now represented by a number of practitioners and professional bodies. These groups came together to develop a broader definition, stating: ‘Social Marketing practice is guided by ethical principles. It seeks to develop and integrate marketing concepts with other approaches to influence behaviours that benefit individuals and communities for the greater social good. It seeks to integrate research, best practice, theory, audience and partnership insight, to inform the delivery of competition sensitive and segmented social change programmes that are effective, efficient, equitable and sustainable’ (iSMA et al., 2013). A key component is the application of a systematic, step-by-step process that is described and illustrated in Box 19.1.

Box 19.1. Bonaire parrot campaign

In 1998, a social marketing campaign was launched on the Caribbean island of Bonaire to help save the yellow-shouldered Amazon parrot (Amazona barbadensis), known locally as the lora (Figure 19.2). This species was threatened by habitat loss and illegal capture because, despite laws to protect the lora, enforcement was sporadic and they were commonly kept as pets. A survey at the start of the campaign estimated that 300 loras remained in the wild on Bonaire and conservationists were concerned the species would become extinct without a change in local attitudes and behaviours. To address this, they took a new approach.

Figure 19.2 The lora or yellow-shouldered Amazon parrot (Amazona barbadensis) that was the focus of a social marketing campaign on the Caribbean island of Bonaire.

The conservation organisation Rare had already run social marketing campaigns on other Caribbean islands, which were based on creating national pride in a target species to shift attitudes and behaviours towards that species (Scholtens & Butler, Reference Scholtens and Butler1999). Conservationists on Bonaire approached Rare and together formed a committee of local organisations to plan a year-long social marketing campaign to ‘Save the Lora’. Following social marketing theory, the campaign included the following six core concepts (ESMA, 2017):

  1. 1. Setting of explicit social goals. The first step is identifying the behaviour the campaign is trying to influence and setting clear, quantifiable goals related to that behaviour. On Bonaire, the goal was to reduce the number of people purchasing loras as pets and so, ultimately, reduce the number of these parrots removed from the wild.

  2. 2. Citizen orientation and focus. In social marketing programmes, citizens should be engaged in the process of identifying issues and developing solutions. On Bonaire, a consortium of environmental organisations, government departments, media companies and volunteers was created to plan and implement the campaign. Before the campaign, the committee conducted a formative evaluation to understand citizens’ knowledge of and attitudes towards the lora. To do this, they distributed a questionnaire to approximately 4% of the island’s population. The data they collected helped inform the campaign message and provided baseline information for measuring the campaign’s impact.

  3. 3. Highlighting target audience benefits via a mix of marketing interventions. Social marketing campaigns ask people to exchange a detrimental behaviour or value for a more desirable one. On Bonaire, the campaign asked people to exchange the opportunity cost of having a pet lora for a new symbol of collective national identity. The campaign sought to reframe the lora, which was traditionally seen as a pet, as a symbol of national pride. This ‘product’ was sold using a mix of marketing interventions, including radio broadcasts, songs and pamphlets. Volunteers also dressed in a giant lora costume to emphasise the species’ role as a national mascot.

  4. 4. Theory, insight, data and evidence informed audience segmentation. Social marketing is based on the idea that a one-size-fits-all approach rarely works. Instead, it is important to spend time and resources identifying, understanding and selecting which parts of the population (known as ‘segments’) should be the focus of subsequent campaigns. Following the Rare Pride Campaign model, the group on Bonaire developed campaign materials to target different audiences. They used formative research to help identify the most popular news sources on the island and produce radio shows, music videos and articles to reach different segments of the population. For example, they created a song about the lora to reach school children and a religious sermon to reach church congregations.

  5. 5. Competition/barrier and asset analysis. Social marketing programmes also seek to identify and remove barriers that could keep their target audiences from adopting or sustaining positive behaviours. On Bonaire, keeping loras as pets had become a social norm, so the Rare campaign focused on reframing this species as a wild animal that should stay in the wild. The campaign also worked with local newspapers and radio stations to inform citizens of the illegality and consequences of keeping this parrot in captivity.

  6. 6. Critical thinking, reflexivity and being ethical. To be effective and ethical, social marketing campaigns require flexibility and an understanding of the local context. When the campaign started on Bonaire, hundreds of loras were estimated to be in captivity, making it impossible to confiscate all illegal pets. Instead of confiscating the birds, which would have resulted in animal welfare issues, the campaign focused on creating a context in which no new pet loras would be acquired.

Following this campaign, there has been a long-term increase in the lora population on Bonaire. Recent research suggests the campaign played a role in this conservation success by helping shift social norms around keeping loras as pets and increasing support for the enforcement of existing laws and regulations (Salazar, Reference Salazar2017).

19.3 Social marketing in conservation

The application of social marketing in conservation is relatively new compared to sectors like health and development, although its role in fundraising goes back decades (Nicholls, Reference Nicholls2011). More recently, a number of conservation scientists and practitioners have recognised the approach’s value, and social marketing is becoming a more common component of the conservation toolbox (Wright et al., Reference Wright, Veríssimo and Pilfold2015). To illustrate this, we briefly outline how social marketing has been used in three different aspects of conservation practice.

19.3.1 Community-based natural resource management

Increasing the sustainability of natural resource management by local communities is perhaps the most widespread use of social marketing in conservation (DeWan et al., Reference DeWan, Green and Xiaohong2013; Green et al., Reference Green, DeWan and Balcázar Arias2013). For example, the US Fish and Wildlife Service created the ‘Stop Aquatic Hitchhikers’ campaign to empower recreational waterway users to help prevent the spread of aquatic invasive species (Larson et al., Reference Larson, Phillips-Mao and Quiram2011; Figure 19.3). These species are a major threat to global biodiversity and have important economic impacts (Gallardo et al., Reference Gallardo, Clavero and Sánchez2016), but often remain forgotten because they are underwater and thus out of mind. The campaign used social marketing to make the issue more salient among groups such as boaters, anglers, rafters, kayakers, sailors and waterfowl hunters who inadvertently transport aquatic invasive species across waterways on their equipment. As most of these activities require licensing or registration, the Fish and Wildlife Service represented not only an important source of information about the profile of its target audience, but also active partners to promote the appropriate cleaning of recreational equipment. Using branding, the campaign leveraged the links between natural resources and the identity of communities who live on or near the water. They instilled a sense of stewardship in recreational users, so that the target audience was willing to exchange old behaviours for new ones to keep the rivers clean for the benefit of themselves and others (Ries & Trout, Reference Ries and Trout1982). The support of local businesses and other government agencies was vital, as they not only acted as key influencers but also created additional visibility and salience for the message around the need for more thorough cleaning of equipment.

Figure 19.3 Promotional material encouraging boat owners in the Greater Yellowstone Area to adopt practices that will reduce the spread of invasive species.

19.3.2 Demand reduction

One of the earliest uses of social marketing in conservation was to reduce demand for wildlife and wildlife products, based on campaigns to discourage people from buying selected species as pets (as detailed in Box 19.1). More recently, increases in the illegal wildlife trade has created wider recognition of the value of social marketing for demand reduction, as a way to tackle the resultant threats to biodiversity, public health, local livelihoods and effective governance (Veríssimo et al., Reference Veríssimo, Challender and Nijman2012). One example is the Chi Initiative, which was launched in 2014 and seeks to reduce rhino horn consumption in Vietnam by targeting wealthy businessmen (Offord-Woolley, Reference Offord-Woolley2017). The campaign messaging built on the Vietnamese concept of Chi, or ‘strength of will’, and emphasised that masculinity and good fortune come from an individual’s character, not from products purchased on the market. Thus, they sought to create conditions in which taking rhino horn is seen as a sign of weakness, so that business men are willing to exchange this behaviour for one that does not support the illegal wildlife trade. This campaign pioneered the use of social marketing techniques to tackle the illegal wildlife trade, but also illustrates some of the difficulties. In particular, it shows how hard it can be to measure campaign impacts in the context of dynamic rhino horn demand (TRAFFIC, 2017) and multiple ongoing demand reduction efforts in Vietnam. This should become easier in the future, though, as the number of demand-reduction interventions has grown in the last decade (Veríssimo & Wan, Reference Veríssimo and Wan2018), increasing the amount of research and monitoring of market trends and interventions.

19.3.3 Conservation flagships

There is a long history of organisations using particular species for fundraising and awareness-raising. Traditionally, flagship status was seen as an intrinsic characteristic, failing to recognise that flagship species are actually marketing tools. This has changed, with a new definition of a flagship as ‘a species used as the focus of a broader conservation marketing campaign based on its possession of one or more traits that appeal to the target audience’ (Veríssimo et al., Reference Veríssimo, MacMillan and Smith2011). Viewing flagship species through this lens implies that these campaigns should adopt core social marketing concepts, including setting explicit social goals at the beginning of the process (ESMA, 2017). This is important because people generally prefer species that are large, brightly coloured and/or have human-like traits (Gunnthorsdottir, Reference Gunnthorsdottir2001; Barua et al., Reference Barua, Gurdak and Ahmed2012; Borgi & Cirulli, Reference Borgi and Cirulli2015). Thus, setting goals helps guide actions towards the species most needing conservation (Veríssimo et al., Reference Veríssimo, Vaughan and Ridout2017), rather than those that are most popular with the target audience (Smith et al., Reference Smith, Veríssimo and Isaac2012). Emphasising that it is the species’ traits that are important, rather than the species itself, also suggests the flagship approach can be applied to broader aspects of biodiversity. For example, Conservation International’s biodiversity hotspots (Mittermeier et al., Reference Mittermeier, Robles-Gil and Hoffmann2004) have been described as a new type of flagship, designed to appeal to a target audience of international donors by emphasising traits based on endemic biodiversity, return on investment and scientific credibility (Smith et al., Reference Smith, Veríssimo, MacMillan, Leader-Williams, Adams and Smith2010). The main aim of this campaign was to raise funds rather than change people’s behaviours, meaning it cannot be defined as social marketing. However, the creation of this new type of flagship did have wider social marketing impacts, by building local pride in countries containing these hotspots, leading to new conservation policies and wider civil society engagement (Visseren-Hamakers et al., Reference Visseren-Hamakers, Leroy and Glasbergen2012).

19.4 Broader lessons from social marketing

Social marketing is a structured and systematic approach for achieving positive conservation outcomes and so many of its fundamental principles are shared with other aspects of conservation decision science and implementation. However, it provides a number of specific insights that have broader relevance for conservation, which we highlight below.

1. Acknowledging ethical issues

Some critics are uneasy about the ethical issues underpinning social marketing, partly because of its links with capitalism and consumerism (Smith et al., Reference Smith, Veríssimo, MacMillan, Leader-Williams, Adams and Smith2010). One accusation is that campaigns are a form of ‘brainwashing’, so it should be stressed that social marketing is always based on choice and mutually beneficial exchange. A more fundamental issue comes from campaign development, as while the social marketing definition states the approach ‘is guided by ethical principles’ (iSMA et al., 2013), it does not specify whose ethics should do the guiding. This is a key concern, because marketing need is often identified by external actors with world views and priorities that differ from those of the target audience (Adams & Mulligan, Reference Adams and Mulligan2003). Obviously, this issue applies to all behaviour change initiatives and, by focusing on choice and beneficial exchange, social marketing might be better at producing locally supported solutions than approaches based on education and legislation. However, social marketers should always be mindful of the power imbalances involved and be open to outside scrutiny and criticism.

2. The importance of evaluation

It is almost universally agreed that monitoring and evaluation should be core parts of any conservation activity (Sutherland et al., Reference Sutherland, Pullin and Dolman2004), although their relative rarity shows that conservationists often fail to dedicate the necessary time and resources (Lindenmayer & Likens, Reference Lindenmayer and Likens2010). This is less of a problem in business, where learning how to increase effectiveness pays for itself, and helps explain why evaluation is a fundamental component of marketing. This focus on effectiveness is probably why social marketing campaigns were some of the first behaviour-change projects to systematically evaluate their work (Jenks et al., Reference Jenks, Vaughan and Butler2010), as an important way to understand their target audience and adapt their campaigns to increase impact. Just as importantly, social marketers recognise that behaviour change projects can have a range of unintended consequences, including negative impacts. For example, a campaign based in Dominica, similar to that used in the lora project, raised the profile of the flagship species but created a negative association with another parrot species (Douglas & Winkel, Reference Douglas and Winkel2014). Examples such as this illustrate why social marketers are obliged to learn from their actions and improve.

3. Changing behaviour is not easy

While social marketing offers many valuable opportunities for achieving conservation goals, behaviour change can often be slow and expensive. This is illustrated by campaigns from other sectors, such as public health, which have been working on behaviour changes for decades with varying success. Many of these campaigns failed to make any impact, or even had the opposite of the intended effect. For example, one of the US government’s flagship programmes to reduce teen substance abuse actually led to an increase in adolescent drug use in certain contexts (Rosenbaum & Hanson, Reference Rosenbaum and Hanson1998). Such findings have contributed to the results of a recent systematic review on the effectiveness of global health programmes, which found the majority had no positive behavioural results, although success increased with the quality of the campaign (Firestone et al., Reference Firestone, Rowe and Modi2017). Thus, caution is needed when describing the potential gains from social marketing in conservation, especially because funding for such work is likely to be relatively small compared to the health sector. However, evidence from interventions like ‘Save the Lora’ suggests behaviour change is possible, especially when campaigns influence societal norms and allow governments to improve regulation and enforcement (Salazar et al., Reference Salazar, Mills and Veríssimo2019).

4. The myth of ‘the general public’

A fundamental insight from marketing is that the ‘general public’ is an empty concept when communicating with people. This is why audience segmentation is a core concept in social marketing (Box 19.1), based on categorising people into relatively homogeneous subgroups, so that the resultant campaigns can be tailored for maximum impact. Demographic factors like age and income can play a role in defining these groups, although psychographic factors like attitudes, interests and beliefs are often more important (Wright et al., Reference Wright, Veríssimo and Pilfold2015). More broadly, conservationists should recognise the audience-specific nature of their messages, rather than broadcasting them to as many people as possible. For example, while messages based on ‘ecosystem services’ have been successful at highlighting the financial value of nature to government bureaucrats, they have created possibly avoidable tension when aimed at people who value nature for other reasons (Jones, Reference Jones2018).

5. Value is more than a financial metric

The huge profits of some companies can be viewed as illustrations of all that is wrong with marketing, where advertising campaigns lead people into buying over-priced goods and services. However, it also reveals a fundamental marketing premise: a product’s value is neither fixed nor dependent on its manufacturing costs (Sutherland, Reference Sutherland2019). This insight also underpins social marketing in conservation, where people change their behaviour because campaigns foster stronger, more positive links with specific species, ecosystems and actions. Thus, for example, the ‘Stop Aquatic Hitchhikers’ campaign empowered people to reduce their negative impacts on the places they love and the ‘Save the Lora’ campaign built local pride in an endemic species. In each case this increase in value was not measured financially, although the target audience may now be more willing to fund and support activities to conserve these species and habitats.

In conclusion, in this chapter we have discussed how social marketing has been used in conservation and highlighted its strengths and weaknesses. However, benefiting from these strengths involves accepting uncomfortable truths: many conservationists are uneasy about learning from the corporate world or accepting that their reasons for loving nature are not universally shared. However, we can only stem biodiversity loss by engaging with the widest possible range of people, and social marketing is one of the better ways of understanding these multiple audiences and working with them to increase how they value nature.

Footnotes

Chapter Sixteen Citizens and science: media, communication and conservation

Chapter Seventeen Campaigning to bring about change

Chapter Eighteen Behavioural insights for conservation and sustainability

Chapter Nineteen Social marketing and conservation

References

References

Altheide, D. L. 1994. An ecology of communication: toward a mapping of the effective environment. The Sociological Quarterly, 35, 665683.Google Scholar
Besley, J. C. & Nisbet, M. 2013. How scientists view the public, the media and the political process. Public Understanding of Science, 22, 644659.Google Scholar
Besley, J. C. & Tanner, A. H. 2011. What science communication scholars think about training scientists to communicate. Science Communication, 33, 239263.Google Scholar
Castells, M. 2013. Communication Power. Oxford: Oxford University Press.Google Scholar
Cottle, S., Sambrook, R. & Mosdell, N. 2016. Reporting Dangerously: Journalist Killings, Intimidation and Security. London: Palgrave Macmillan.CrossRefGoogle Scholar
Courier Mail. 2016. Climate change is destroying our reefs. We must phase out coal. Courier Mail. 21 April. Brisbane. Available from www.climatecouncil.org.au/reefstatementGoogle Scholar
Cox, R. 2012. Environmental Communication and the Public Sphere. Los Angeles, CA: Sage.Google Scholar
Cox, R. & Schwarze, S. 2015. Strategies of environmental pressure groups and NGOs. In Hansen, A. & Cox, R., editors, The Routledge Handbook of Environment and Communication (pp. 7385). Abingdon: Routledge.Google Scholar
Deuze, M. 2012. Media Life. Cambridge: Polity Press.Google Scholar
Dewey, J. 1916. Democracy and Education. New York, NY: Courier Corporation.Google Scholar
Dryzek, J. S. 2013. The Politics of the Earth: Environmental Discourses. Oxford: Oxford University Press.Google Scholar
Dudo, A. & Besley, J. C. 2016. Scientists’ prioritization of communication objectives for public engagement. PLoS ONE, 11(2), e0148867.Google Scholar
Dunwoody, S. 2015. Environmental scientists and public communication. In Hansen, A. & Cox, R., editors, The Routledge Handbook of Environment and Communication (pp. 6372). Abingdon: Routledge.Google Scholar
Foxwell-Norton, K. 2018. Environmental Communication and Critical Coastal Policy: Communities, Culture and Nature. London: Routledge.Google Scholar
Foxwell-Norton, K. & Konkes, C. 2019. The Great Barrier Reef: News media, policy and the politics of protection. International Communication Gazette, 81(3), 211234.Google Scholar
Foxwell-Norton, K. & Lester, L. 2017. Saving the Great Barrier Reef from disaster, then and now. Media, Culture & Society, 39, 568581.Google Scholar
Fraser, N. 2007. Transnationalizing the public sphere: on the legitimacy and efficacy of public opinion in a post-Westphalian world. Theory, Culture & Society, 24(4), 730.Google Scholar
Habermas, J. 1989. The Structural Transformation of the Public Sphere, trans. Burger, Thomas. Cambridge, MA: MIT Press.Google Scholar
Hall Jamieson, K. 2017. The need for a science of science communication: communicating science’s values and norms. In Hall-Jamieson, K., Kahan, D. & Scheufele, D. A., editors, The Oxford Handbook of the Science of Science Communication. Oxford: Oxford University Press.Google Scholar
Hoegh-Guldberg, O. 2015. Coal and climate change: a death sentence for the Great Barrier Reef. The Conversation, 20 May.Google Scholar
Hutchins, B. & Lester, L. 2015. Theorizing the enactment of mediatized environmental conflict. International Communication Gazette, 77, 337358.Google Scholar
International Whaling Commission. 2018. https://iwc.int/history-and-purpose (accessed 14 December 2018).Google Scholar
Kahan, D. M., Scheufele, D. A. & Hall Jamieson, K. 2017. Introduction: why science communication? In Hall-Jamieson, K., Kahan, D. & Scheufele, D. A., editors, The Oxford Handbook of the Science of Science Communication. Oxford: Oxford University Press.Google Scholar
Konkes, C. 2018. Green lawfare: environmental public interest litigation and mediatized environmental conflict. Environmental Communication, 12, 191203.Google Scholar
Lester, L. 2014. Transnational publics and environmental conflict in the Asian century. Media International Australia, 150(1), 167178.Google Scholar
Lester, L. 2016. Containing spectacle in the transnational public sphere. Environmental Communication, 10, 791802. doi:10.1080/17524032.2015.1127849.Google Scholar
Lester, L. 2017. Environment and human rights activism, journalism and ‘The New War’. In Tumber, H. & Waisbord, S., editors,The Routledge Companion to Media and Human Rights (pp. 268276). Abingdon: Routledge.CrossRefGoogle Scholar
Lester, L. 2019. Global Trade and Mediatised Environmental Conflict: The View from Here. Switzerland: Palgrave Macmillan.Google Scholar
Maxwell, R. & Miller, T. 2012. Greening the Media. Oxford: Oxford University Press.Google Scholar
McCalman, I. 2013. The Reef: A Passionate History from Cook to Climate Change. Brunswick: Viking/Penguin Books.Google Scholar
McHendry, G. F. Jr 2012. Whale Wars and the axiomatization of image events on the public screen. Environmental Communication: A Journal of Nature and Culture, 6, 139155.Google Scholar
McKnight, D. 2012. Rupert Murdoch: An Investigation of Political Power. Sydney: Allen & Unwin.Google Scholar
Murphy, P. 2017. The Media Commons: Globalization and Environmental Discourses. Champaign, IL: University of Illinois Press.Google Scholar
Peters, H. P. & Dunwoody, S. 2016. Scientific uncertainty in media content: introduction to this special issue. Public Understanding of Science, 25, 893908.Google Scholar
Redclift, M. 2005. Sustainable development (1987–2005): an oxymoron comes of age. Sustainable Development, 13, 212227.Google Scholar
Shannon, C. E. & Weaver, W. 1949. A Mathematical Model of Communication. Champaign, IL: University of Illinois Press.Google Scholar
Simis, M. J., Madden, H., Cacciatore, M. A., et al. 2016. The lure of rationality: why does the deficit model persist in science communication? Public Understanding of Science, 25, 400414.Google Scholar
Singer, J. B. 2018. Transmission creep: media effects theories and journalism studies in a digital era. Journalism Studies, 19, 209226.Google Scholar
Volkmer, I. 2014. The Global Public Sphere: Public Communication in the Age of Reflective Interdependence. Hoboken, NJ: John Wiley & Sons.Google Scholar

References

Breaking the Brand. 2016. How Much Is Spent On Rhino Horn Demand Reduction Campaigns? Available from https://breakingthebrand.org/how-much-is-spent-on-rhino-horn-demand-reduction-campaigns/?doing_wp_cron=1534087399.6144099235534667968750Google Scholar
Christiano, A. & Neimand, A. 2017. Stop Raising Awareness Already. Stanford Social Innovation Review. Available from https://ssir.org/articles/entry/stop_raising_awareness_alreadyGoogle Scholar
Fundraising Regulator. 2016. The Code of Fundraising Practice. Available from www.fundraisingregulator.org.uk/wp-content/uploads/2018/05/Code-of-Fundraising-Practice-v1.7–25052018.pdf accessed May 2018Google Scholar
Greenpeace. 2010. Success! You made Nestlé drop dodgy palm oil! Available from https://greenpeace.org.uk/success-nestle-palm-oil/Google Scholar
Grubbs, R. D., Carlson, J. K., Romine, J. G., et al. 2016. Critical assessment and ramifications of a purported marine trophic cascade. Scientific Reports, 6, 20970.Google Scholar
Hill, D. 2010. Emotionomics: Leveraging Emotions for Business Success. London: Kogan Page.Google Scholar
Hinsley, A., Verissimo, D. & Roberts, D. L. 2015. Heterogeneity in consumer preferences for orchids in international trade and the potential for the use of market research methods to study demand for wildlife. Biological Conservation, 190, 8086.Google Scholar
IUCN. 2016. Informing decisions on trophy hunting. A Briefing Paper for European Union Decision-makers regarding potential plans for restriction of imports of hunting trophies. April 2016. Available from www.iucn.org/downloads/iucn_informingdecisionsontrophyhuntingv1.pdfGoogle Scholar
Jacquet, J. & Pauly, D. 2007. The rise of seafood awareness campaigns in an era of collapsing fisheries. Marine Policy, 31, 308313.Google Scholar
Mackenzie-Mohr, D. 2011. Fostering Sustainable Behavior: An Introduction to Community-Based Social Marketing. Toronto: New Society Publishers.Google Scholar
National Aquarium Baltimore. 2016. Cownose Rays in the Chesapeake Bay: What do we know? Final Report of a workshop hosted on October 22nd 2015 by the Chesapeake Bay Program’s Sustainable Fisheries Goal Implementation Team. National Aquarium Baltimore, Maryland. Available from www.chesapeakebay.net/channel_files/23141/cnr_workshop_report_final_1–29-16.pdfGoogle Scholar
Neslen, A. 2017. Nestlé, Hershey and Mars ‘breaking promises over palm oil use’. The Guardian. Available from www.theguardian.com/environment/2017/oct/27/nestle-mars-and-hershey-breaking-promises-over-palm-oil-use-say-campaigners (accessed June 2018).Google Scholar
Nuno, A. & St John, F. A. V. 2015. How to ask sensitive questions in conservation: a review of specialized questioning techniques. Biological Conservation, 189, 515.Google Scholar
Project Seahorse. 2018. Conservation Programmes: Trade and Policy. Available from www.projectseahorse.org/action-programs#tradeGoogle Scholar
Rankou, H. & Averyanov, L. 2015. Paphiopedilum canhii. The IUCN Red List of Threatened Species 2015: e.T191858A2009477. Available from http://dx.doi.org/10.2305/IUCN.UK.2015–2.RLTS.T191858A2009477.enGoogle Scholar
Rawlinson, K. 2017. Michael Gove ‘haunted’ by plastic pollution seen in Blue Planet II. Available from www.theguardian.com/environment/2017/dec/19/michael-gove-haunted-by-plastic-pollution-seen-in-blue-planet-iiGoogle Scholar
Ringold, D. J. 2002. Boomerang effects in response to public health interventions: some unintended consequences in the alcoholic beverage market. Journal of Consumer Policy, 25, 2763.Google Scholar
Roberton, S. I. 2014. Has demand for rhino horn truly dropped in Vietnam? National Geographic, 3 November 2014. Available from https://blog.nationalgeographic.org/2014/11/03/has-demand-for-rhino-horn-truly-dropped-in-vietnam/Google Scholar
Two Million Tusks. 2017. Ivory: the grey areas. A study of UK auction house ivory sales – the missing evidence. Available from www.twomilliontusks.org/Google Scholar
Veríssimo, D. & Wan, A. K. 2018. Characterising the efforts to reduce consumer demand for wildlife products. Available from https://osf.io/preprints/socarxiv/642pbGoogle Scholar
Watts, J. 2012. End Chinese bear-bile farming, says UK animal rights activist. The Guardian, 9 January 2012. Available from www.theguardian.com/environment/2012/jan/09/china-bear-bile-farming-animal-rightsGoogle Scholar
Wedel, M. & Kamakura, W. A. 2000. Market Segmentation: Conceptual and Methodological Foundations. New York, NY: Springer US.Google Scholar

References

Allcott, H. 2011. Social norms and energy conservation. Journal of Public Economics, 95, 10821095.Google Scholar
Alpizar, F., Carlsson, F. & Johansson-Stenman, O. 2008. Anonymity, reciprocity, and conformity: evidence from voluntary contributions to a national park in Costa Rica. Journal of Public Economics, 92, 10471060.Google Scholar
Argyle, M. 1957. Social pressure in public and private situations. The Journal of Abnormal and Social Psychology, 54, 172.Google Scholar
Ariely, D., Bracha, A. & Meier, S. 2009. Doing good or doing well? Image motivation and monetary incentives in behaving prosocially. American Economic Review, 99, 544555.Google Scholar
Ashraf, N., Bandiera, O. & Jack, B. K. 2014. No margin, no mission? A field experiment on incentives for public service delivery. Journal of Public Economics, 120, 117.Google Scholar
Barkan, R., Ayal, S. & Ariely, D. 2015. Ethical dissonance, justifications, and moral behavior. Journal of Personality and Social Psychology, 74, 6379.Google Scholar
Barr, S. 2004. Are we all environmentalists now? Rhetoric and reality in environmental action. Geoforum, 35, 231249.Google Scholar
Becker, G. S. 1976. The Economic Approach to Human Behavior. Chicago, IL: University of Chicago Press.Google Scholar
Behavioural Insights Team. 2014. EAST: four simple ways to apply behavioural insights. Available from www.bi.team/wp-content/uploads/2015/07/BIT-Publication-EAST_FA_WEB.pdfGoogle Scholar
Burgess, G. 2016. Powers of persuasion? Conservation Communications, Behavioural Change and Reducing Demand for Illegal Wildlife Products. Paris: OECD.Google Scholar
Carrington, D. 2019. Public concern over environment reaches record high in UK. The Guardian. Available from www.theguardian.com/environment/2019/jun/05/greta-thunberg-effect-public-concern-over-environment-reaches-record-high (accessed 7 June 2019).Google Scholar
Chater, N. & Loewenstein, G. 2016. The under-appreciated drive for sense-making. Journal of Economic Behavior & Organization, 126, 137154.Google Scholar
Cialdini, R. B. 2003. Crafting normative messages to protect the environment. Current Directions in Psychological Science, 12, 105109.Google Scholar
Darnton, A. 2008. An Overview of Behaviour-change Models and Their Uses. Government Social Research, Knowledge Review.Google Scholar
DECC (UK Department of Energy and Climate Change). 2014. Evaluation of the DECC/John Lewis energy labelling trial.Google Scholar
Dimant, E. 2017. On peer effects: contagion of pro-and anti-social behavior and the role of social cohesion. Discussion Papers 2017–06, The Centre for Decision Research and Experimental Economics, School of Economics, University of Nottingham.Google Scholar
Duffy, S. & Verges, M. 2009. It matters a hole lot: perceptual affordances of waste containers influence recycling compliance. Environment and Behavior, 41, 741749.Google Scholar
(DWP) Department for Work and Pensions. 2017. Automatic Enrolment Review 2017: Analytical Report.Google Scholar
Ebeling, F. & Lotz, S. 2015. Domestic uptake of green energy promoted by opt-out tariffs. Nature Climate Change, 5, 868.Google Scholar
Frey, B. S. & Oberholzer-Gee, F. 1997. The cost of price incentives: an empirical analysis of motivation crowding-out. The American Economic Review, 87, 746755.Google Scholar
Fryer, R. G. Jr, Levitt, S. D., List, J., et al. 2012. Enhancing the Efficacy of Teacher Incentives through Loss Aversion: A Field Experiment (No. w18237). Cambridge, MA: National Bureau of Economic Research.Google Scholar
Gallus, J. 2016. Fostering public good contributions with symbolic awards: a large-scale natural field experiment at wikipedia. Management Science, 63, 39994015.Google Scholar
Gino, F., Norton, M. I. & Weber, R. A. 2016. Motivated Bayesians: feeling moral while acting egoistically. Journal of Economic Perspectives, 30, 189212.Google Scholar
Gneezy, U. & Rustichini, A. 2000. Pay enough or don’t pay at all. The Quarterly Journal of Economics, 115, 791810.Google Scholar
Goldstein, N. J., Cialdini, R. B. & Griskevicius, V. 2008. A room with a viewpoint: using social norms to motivate environmental conservation in hotels. Journal of Consumer Research, 35, 472482.Google Scholar
Haidt, J. 2001. The emotional dog and its rational tail: a social intuitionist approach to moral judgment. Psychological Review, 108, 814.Google Scholar
Halpern, D. 2015. Inside the Nudge Unit. London: Random House.Google Scholar
Haynes-Worthington, S. 2018. The Attenborough effect: searches for plastic recycling rocket after Blue Planet II. Resource. Available from https://resource.co/article/attenborough-effect-searches-plastic-recycling-rocket-after-blue-planet-ii-12334 (accessed 24 July 2018).Google Scholar
House of Commons Environmental Audit Committee. 2017. Plastic bottles: Turning Back the Plastic Tide. First Report of Session 2017–19.Google Scholar
Jenni, K. & Loewenstein, G. 1997. Explaining the identifiable victim effect. Journal of Risk and Uncertainty, 14, 235257.Google Scholar
Johnson, E. J., Shu, S. B., Dellaert, B. G., et al. 2012. Beyond nudges: tools of a choice architecture. Marketing Letters, 23, 487504.Google Scholar
Jones, J. P., Andriamarovololona, M. M. & Hockley, N. 2008. The importance of taboos and social norms to conservation in Madagascar. Conservation Biology, 22, 976986.Google Scholar
Kahneman, D. 2011. Thinking, Fast and Slow. London: Macmillan.Google Scholar
Kahneman, D. & Tversky, A. 2013. Prospect theory: an analysis of decision under risk. In MacLean, L. C. & Ziemba, W. T., editors, Handbook of the Fundamentals of Financial Decision-Making (pp. 99127). Singapore: World Scientific.Google Scholar
Kollmuss, A. & Agyeman, J. 2002. Mind the gap: why do people act environmentally and what are the barriers to pro-environmental behavior? Environmental Education Research, 8, 239260.Google Scholar
Laibson, D. 1997. Golden eggs and hyperbolic discounting. The Quarterly Journal of Economics, 112, 443478.Google Scholar
Larcom, S., Rauch, F. & Willems, T. 2017. The benefits of forced experimentation: striking evidence from the London underground network. The Quarterly Journal of Economics, 132, 20192055.Google Scholar
Marteau, T. M. 2017. Towards environmentally sustainable human behaviour: targeting non-conscious and conscious processes for effective and acceptable policies. Philosophical Transactions of the Royal Society A, 375(2095), 20160371.Google Scholar
Mazar, N., Amir, O. & Ariely, D. 2008. The dishonesty of honest people: a theory of self-concept maintenance. Journal of Marketing Research, 45, 633644.CrossRefGoogle Scholar
Nickerson, R. S. 1998. Confirmation bias: a ubiquitous phenomenon in many guises. Review of General Psychology, 2, 175.Google Scholar
Ölander, F. & Thøgersen, J. 2014. Informing versus nudging in environmental policy. Journal of Consumer Policy, 37, 341356.Google Scholar
Ostrom, E. 2000. Collective action and the evolution of social norms. Journal of Economic Perspectives, 14, 137158.Google Scholar
Ostrom, E., Gardner, R. & Walker, J. 1994. Rules, Games, and Common-Pool Resources. Ann Arbor, MI: University of Michigan Press,Google Scholar
Plumer, B. 2015. Solar power is contagious: installing panels often means your neighbors will too. Available from www.vox.com/2014/10/24/7059995/solar-power-is-contagious-neighbor-effects-panels-installationGoogle Scholar
Portney, K. E., Hannibal, B., Goldsmith, C., et al. 2018. Awareness of the food–energy–water nexus and public policy support in the United States: public attitudes among the American people. Environment and Behavior, 50, 375400.Google Scholar
Reddy, S. M., Montambault, J., Masuda, Y. J., et al. 2017. Advancing conservation by understanding and influencing human behavior. Conservation Letters, 10, 248256.Google Scholar
Rodríguez-Dowdell, N., Yépez-Zabala, I., Green, K., et al., editors. 2014. Pride for ARAs: A Guide to Reciprocal Water Agreements for People and Nature. Arlington, VA: Rare.Google Scholar
Rowson, J. & Corner, A. 2015. The Seven Dimensions of Climate Change: Introducing a New Way to Think and Talk and Act. London: RSA & Climate Outreach and Information (COIN).Google Scholar
Schiff, B. 2012. The function of narrative: towards a narrative psychology of meaning. Narrative Works: Issues, Investigations and Interventions, 2, 3347.Google Scholar
Schneider, C. R., Zaval, L., Weber, E. U., et al. 2017. The influence of anticipated pride and guilt on pro-environmental decision making. PLoS ONE, 12(11), e0188781.Google Scholar
Scott, J. 2000. Rational choice theory. In Browning, G., Halcli, A. & Webster, F., editors, Understanding Contemporary Society: Theories of the Present. Browning (pp. 126138). London: SAGE.Google Scholar
Shafir, E., editor. 2013. The Behavioral Foundations of Public Policy. Princeton, NJ: Princeton University Press.Google Scholar
Shalvi, S., Gino, F., Barkan, R., et al. 2015. Self-serving justifications: doing wrong and feeling moral. Current Directions in Psychological Science, 24, 125130.Google Scholar
Shove, E. 2009. Beyond ABC: climate change policies and theories of social change. Environmental and Planning, 42, 12731285.Google Scholar
Simon, H. A. 1972. Theories of bounded rationality. Decision and Organization, 1, 161176.Google Scholar
Steentjes, K., Pidgeon, N. F., Poortinga, W., et al. 2017. European Perceptions of Climate Change (EPCC): Topline Findings of a Survey Conducted in Four European Countries in 2016. Cardiff: Cardiff University.Google Scholar
Sunstein, C. R., Bobadilla-Suarez, S., Lazzaro, S. C., et al. 2016. How people update beliefs about climate change: good news and bad news. Cornell Law Review, 102, 1431.Google Scholar
Thaler, R. & Sunstein, C. 2008. Nudge. New Haven, CT: Yale University Press.Google Scholar
Thiagarajah, K. & Getty, V. M. 2013. Impact on plate waste of switching from a tray to a trayless delivery system in a university dining hall and employee response to the switch. Journal of the Academy of Nutrition and Dietetics, 113, 141145.Google Scholar
Thøgersen, J. 2014. Unsustainable consumption: basic causes and implications for policy. European Psychologist, 19, 8495.Google Scholar
Trivers, R. L. 1971. The evolution of reciprocal altruism. Quarterly Review of Biology, 46, 3557.Google Scholar
Turner, J. C. 1991. Social Influence. Milton Keynes: Open University Press.Google Scholar
Turnwald, B., Boles, D. & Crum, A. 2017. Association between indulgent descriptions and vegetable consumption: twisted carrots and dynamite beets. Journal of the American Medical Association, 177, 12161218.Google Scholar
Vennard, D., Park, T. & Attwood, S. 2019. Encouraging Sustainable Food Consumption By Using More-Appetizing Language. Washington, DC: World Resources Institute.Google Scholar
Vollan, B. 2008. Socio-ecological explanations for crowding-out effects from economic field experiments in southern Africa. Ecological Economics, 67, 560573.Google Scholar
Wan, J. 2010. The incentive to declare taxes and tax revenue: the lottery receipt experiment in China. Review of Development Economics, 14, 611624.Google Scholar
Webb, T. L. & Sheeran, P. 2006. Does changing behavioral intentions engender behavior change? A meta-analysis of the experimental evidence. Psychological Bulletin, 132, 249268.Google Scholar
WildAid. 2014. Evidence of Declines in Shark Fin Demand, China. San Francisco, CA: WildAid.Google Scholar

References

Adams, W. M. & Mulligan, M. 2003. Decolonizing Nature: Strategies for Conservation in a Post-colonial Era. Abingdon: Earthscan.Google Scholar
Barua, M., Gurdak, D. J., Ahmed, R. A., et al. 2012. Selecting flagships for invertebrate conservation. Biodiversity and Conservation, 21, 14571476.Google Scholar
Borgi, M. & Cirulli, F. 2015. Attitudes toward animals among kindergarten children: species preferences. Anthrozoös, 28, 4559.Google Scholar
Cooney, R., Roe, D., Dublin, H., et al. 2017. From poachers to protectors: engaging local communities in solutions to illegal wildlife trade. Conservation Letters, 10, 367374.Google Scholar
DeWan, A., Green, K., Xiaohong, L., et al. 2013. Using social marketing tools to increase fuel-efficient stove adoption for conservation of the golden snub-nosed monkey, Gansu Province, China. Conservation Evidence, 10, 3236.Google Scholar
Douglas, L. R. & Winkel, G. 2014. The flipside of the flagship. Biodiversity and Conservation, 23, 979997.Google Scholar
ESMA. 2017. Global Consensus on Social Marketing Principles, Concepts and Techniques. Monksferry: European Social Marketing Association.Google Scholar
Firestone, R., Rowe, C. J., Modi, S. N., et al. 2017. The effectiveness of social marketing in global health: a systematic review. Health Policy and Planning, 32, 110124.Google Scholar
French, J., Dip, H. E. & Blair-Stevens, C. 2006. From snake oil salesmen to trusted policy advisors: the development of a strategic approach to the application of social marketing in England. Social Marketing Quarterly, 12, 2940.Google Scholar
Gallardo, B., Clavero, M., Sánchez, M. I., et al. 2016. Global ecological impacts of invasive species in aquatic ecosystems. Global Change Biology, 22, 151163.CrossRefGoogle ScholarPubMed
Green, K. M., DeWan, A., Balcázar Arias, A., et al. 2013. Driving adoption of payments for ecosystem services through social marketing, Veracruz, Mexico. Conservation Evidence, 10, 4852.Google Scholar
Gunnthorsdottir, A. 2001. Physical attractiveness of an animal species as a decision factor for its preservation. Anthrozoös, 14, 204215.CrossRefGoogle Scholar
iSMA, ESMA, AASM. 2013. Consensus Definition of Social Marketing. International Social Marketing Association, European Social Marketing Association and Australian Association of Social Marketing.Google Scholar
Jenks, B., Vaughan, P. W. & Butler, P. J. 2010. The evolution of Rare Pride: using evaluation to drive adaptive management in a biodiversity conservation organization. Evaluation and Program Planning, 33, 186190.Google Scholar
Jones, J. P. G. 2018. How can we communicate all that nature does for us? Available from http://theconversation.com/how-can-we-communicate-all-that-nature-does-for-us-94761 (accessed 17 June 2018).Google Scholar
Larson, D. L., Phillips-Mao, L., Quiram, G., et al. 2011. A framework for sustainable invasive species management: environmental, social, and economic objectives. Journal of Environmental Management, 92, 1422.Google Scholar
Lefebvre, R. C. 2013. Social Marketing and Social Change: Strategies and Tools For Improving Health, Well-Being, and the Environment. San Francisco, CA: Jossey-Bass.Google Scholar
Lindenmayer, D. B. & Likens, G. E. 2010. The science and application of ecological monitoring. Biological Conservation, 143, 13171328.Google Scholar
Mittermeier, R. A., Robles-Gil, P., Hoffmann, M., et al. 2004. Hotspots Revisited: Earth’s Biologically Richest and Most Endangered Ecoregions. Mexico City: Cemex.Google Scholar
Nicholls, H. 2011. The art of conservation. Available from www.nature.com/articles/472287a (accessed 16 June 2018).Google Scholar
Offord-Woolley, S. 2017. The Chi Initiative: a behaviour change initiative to reduce the demand for rhino horn in Viet Nam. Pachyderm, 58, 144147.Google Scholar
Ries, A. & Trout, J. 1982. Positioning: The Battle For Your Mind. New York, NY: McGraw-Hill.Google Scholar
Rosenbaum, D. P. & Hanson, G. S. 1998. Assessing the effects of school-based drug education: a six-year multilevel analysis of project D.A.R.E. Journal of Research in Crime and Delinquency, 35, 381412.Google Scholar
Rothschild, M. L. 2000. Carrots, sticks, and promises: a conceptual framework for the management of public health and social issue behaviors. Social Marketing Quarterly, 6, 86114.Google Scholar
Salazar, G. R. 2017. A qualitative impact evaluation of a conservation social marketing campaign. MSc thesis, Imperial College, London.Google Scholar
Salazar, G., Mills, M. & Veríssimo, D. 2019. Qualitative impact evaluation of a social marketing campaign for conservation. Conservation Biology, 33, 634644. https://doi.org/10.1111/cobi.13218Google Scholar
Santos, C., Simões, A. M., Atalaia, J., et al. 2011. Melhorar a Vida – Um Guia de Marketing Social. Alverca: Fundação CEBI.Google Scholar
Scholtens, E. & Butler, P. 1999. Learning About the Lora: A Campaign to Promote Pride in Bonaire’s Yellow Shouldered Parrot. Arlington, VA: Rare.Google Scholar
Schultz, P. W. 2011. Conservation means behavior. Conservation Biology, 25, 10801083.Google Scholar
Silk, A. 2006. What Is Marketing? Harvard, MA: Harvard Business Press.Google Scholar
Smith, R. J., Veríssimo, D., Isaac, N. J. B., et al. 2012. Identifying Cinderella species: uncovering mammals with conservation flagship appeal. Conservation Letters, 5, 205212.Google Scholar
Smith, R. J., Veríssimo, D. & MacMillan, D. C. 2010. Marketing and conservation: how to lose friends and influence people. In Leader-Williams, N., Adams, W. M. & Smith, R. J., editors, Trade-offs in Conservation: Deciding What to Save (pp. 215232). Oxford: Wiley-Blackwell.Google Scholar
Sutherland, R. 2019. Alchemy: The Surprising Power of Ideas That Don’t Make Sense. London: WH Allen.Google Scholar
Sutherland, W. J., Pullin, A. S., Dolman, P. M., et al. 2004. The need for evidence-based conservation. Trends in Ecology & Evolution, 19, 305308.CrossRefGoogle ScholarPubMed
TRAFFIC. 2017. Chi Briefing Paper. World Rhino Day 2017. Available from www.trafficj.org/publication/17_Briefing_CHI-World_Rhino_Day.pdf.Google Scholar
Veríssimo, D., Challender, D. & Nijman, V. 2012. Wildlife trade in Asia: start with the consumer. Asian Journal of Conservation Biology, 1, 4950.Google Scholar
Veríssimo, D., MacMillan, D. C. & Smith, R. J. 2011. Towards a systematic approach for identifying conservation flagships. Conservation Letters, 4, 18.Google Scholar
Veríssimo, D., Vaughan, G., Ridout, M., et al. 2017. Increased conservation marketing effort has major fundraising benefits for even the least popular species. Biological Conservation, 211, 95101.Google Scholar
Veríssimo, D. & Wan, A. K. Y. 2018. Characterising the efforts to reduce consumer demand for wildlife products. Open Science Framework. Available from https://osf.io/tu4jy/ (accessed 27 May 2018).Google Scholar
Visseren-Hamakers, I. J., Leroy, P. & Glasbergen, P. 2012. Conservation partnerships and biodiversity governance: fulfilling governance functions through interaction. Sustainable Development, 20, 264275.Google Scholar
Waylen, K. A., McGowan, P. J. K., Group, P. S., et al. 2009. Ecotourism positively affects awareness and attitudes but not conservation behaviours: a case study at Grande Riviere, Trinidad. Oryx, 43, 343351.Google Scholar
Wright, A. J., Veríssimo, D., Pilfold, K., et al. 2015. Competitive outreach in the 21st century: why we need conservation marketing. Ocean & Coastal Management, 115, 4148.CrossRefGoogle Scholar
Figure 0

Figure 17.1 Model showing differences between behaviour-change and awareness-raising campaigns developed by Nature Needs More Ltd for its Breaking The Brand RhiNo Campaign.

(Breaking The Brand, 2016)
Figure 1

Figure 19.1 Diagram showing how a person’s ability, opportunity and/or motivation determines (a) whether they are prone, unable or resistant to change and (b) the appropriateness of the four different behaviour change approaches of education, law, marketing and technical intervention (TI) under these different conditions.

(adapted from Rothschild, 2000; Santos et al., 2011)
Figure 2

Figure 19.2 The lora or yellow-shouldered Amazon parrot (Amazona barbadensis) that was the focus of a social marketing campaign on the Caribbean island of Bonaire.

Figure 3

Figure 19.3 Promotional material encouraging boat owners in the Greater Yellowstone Area to adopt practices that will reduce the spread of invasive species.

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