Introduction 1

‘Are you in?’ I was asked this in the email header from the World Wide Fund for Nature (WWF), 2 a big conservation organisation, with which I have collaborated over the years. ‘Do you care about a clean, healthy future for people and the planet?’, the mass mailing continued. The following section, ‘Our Pledge’, noted: ‘[W]e believe our future should be powered by nature’ and emphasised the need for ‘investments in clean and renewable energy’. It went on: ‘We choose to invest in solutions, not in problems’. The email’s message ended with: ‘Click “yes” to sign our plea: seize your power’. Such power could either be seized through Facebook, Twitter or Google+, revealing the social media version of ‘signing up’ to ‘good’ solutions spearheaded by nongovernmental organisations (NGOs).

Conservation NGOs, dedicated to biodiversity at large, today form a natural part of the institutional landscape and public space. The NGOs’ influence and presence grew exponentially in the years following the 1992 Earth Summit, leading to the expansion of field offices of Northern NGOs as well as the mushrooming of Southern conservation NGOs (Levine 2002). They have been particularly influential in shaping public opinion and policy in the North (Corson 2010) as well as in influencing policy terrains in the global South that harbour the highest concentrations of biodiversity.

Anthropologists have become increasingly active both in terms of working within and studying the work of conservation NGOs. First, conservation NGO projects are increasingly present in ‘ethnographic’ field settings because of the explosion of conservation initiatives across the globe. This has led to many projects hiring practising anthropologists. Second, conservation presence has led to tensions and dynamics with indigenous people and local communities, triggering various forms of anthropological critique. Third, a growing body of analysis has increasingly taken up conservation NGOs as an object of study in their own right. Anthropologists have portrayed local perspectives in which global narratives prevail. They have undertaken global event ethnographies (Brosius and Campbell 2010; Corson and MacDonald 2012), site-specific analysis (West 2006) as well as comparative work (Brockington and Scholfield 2010). The discipline is also at the forefront of ‘elucidating institutional developments and the forms of environmental surveillance and intervention it promotes’ (Brosius 1999: 50).

Nevertheless, rather than resulting in a concerted anthropological conservation agenda, such engagement is pointing to a number of contradictions. Not only has the biodiversity crisis deepened during the same period that NGO activity has mushroomed, but also the very solutions conservation organisations propose are questioned and, according to some, are even aggravating the problem (Igoe and Brockington 2007). Critical voices point to mainstream organisations, particularly big international nongovernmental organisations (BINGOs) that are dedicated to anodyne advocacy rather than activism. They observe technically framed solutions and compromise replacing politics, corporate partnerships substituting critique, narrow environmental policy and single issues predominating over broad-scale sustainability politics (Barker 2010; Chapin 2004; Holmes 2011; Levine 2002; MacDonald 2010). Furthermore, there have been attacks in the global South against international conservation NGOs, which are perceived as foreign enterprises that undermine rather than support national civil society organisations, whether through co-opting leadership or draining resources intended for local conservation work. Where problem analysis has long been part of the conservation toolbox and a source of NGO authority, critical voices insist that conservation NGOs are the problem.

The title of this chapter derives from the polemic nature of the debate. I suggest that many debates can be understood through the lenses of three master narratives that frame the significance of conservation NGOs’ activity. Such narratives, respectively, position NGOs as (1) doing good, (2) turning ugly or (3) acting pragmatically through what this author labels ‘Dirty Harry’ approaches. I consider these as master narratives given their meta-discursive role in delineating and defining (Bamberg 2005) how conservation NGOs are perceived and understood.

The first involves the ‘good conservationist’, a master narrative often apparent in foundation documents, public profiles and programmatic statements of conservation NGOs. ‘Doing good’, I contend, is an essential part of conservation NGO activity and legitimacy production where organisational identities and activities are framed as a matter of moral duty and grassroots intervention.

The second master narrative, ‘the ugly conservationist’, has become increasingly apparent in the last decade, reflecting the blurred boundaries between ‘good’ conservation and ‘bad’ states and corporations. This counternarrative stresses how conservation NGOs have ‘turned’ big and ugly, distanced themselves from local constituencies and sided with power.

The third master narrative, the ‘Dirty Harry’s of conservation emphasise pragmatic values and realism in response to the earlier critique. Partnerships and engagement with the ‘bad’ state and private sector are not considered problematic per se, but necessary to secure real-life change.

At a time when engagements, both within NGOs and critical analysis from the outside have blossomed, how do we address this narrative complexity? As a starting point, this chapter argues that such meta-narratives leave little analytical space to capture the complexity at stake. First, there are obvious risks with taking the ‘doing good’ discourse for granted by performing complicit analysis without fundamentally interrogating the institutional challenges and constraints at stake. Second, even though the ‘ugly conservationist’ critique offers a much-needed reality check of conservation NGOs, this arguably leads to an analytical impasse that is caught up in dichotomies of the ‘good’ intentions and an ‘ugly’ present. As such, they leave social science inadequately equipped to capture the shifting realities, roles and practises of actual NGO work. Third, ‘Dirty Harry’ narratives, although illustrative of evolving power dynamics and institutional strategy, easily displace or render critical analysis ‘disobedient’ (Igoe et al. 2010).

The resulting malaise suggests a need to revisit the role of anthropological analysis of conservation NGOs. This section is divided into three major parts. The first part debates master narratives and claims in the literature of conservation NGOs, respectively, doing good, turning ugly and operating as ‘Dirty Harry’s. Subsequently, the second part debates the analytical implications and limitations of this critique through a case study from the Peruvian Amazon. The third part offers a synthesis of the dispute that argues for the need to rethink anthropological counternarratives from a less dichotomous perspective.

Methodology

This analysis is informed by a reflexive exercise based on long-term involvement with(in) conservation NGOs as a practitioner of what might be labelled ‘conservation anthropology’, as well as an observer of them as part of a broader research into environmental governance based on ethnographic fieldwork in Peru. Assessments of specific conservation NGOs frequently reveal how realities are often more complex and diverse than what appears in critical narratives. Whereas the latter may emphasise situations of top-down design, dispossession and social exclusion, there are just as many counter examples of NGO actors establishing new forms of alliances, breaking new ground and advancing social agendas in instances where government inertia prevails. Wholesale dismissals of monolithic NGOs do not capture such complexity, prompting the need for rethinking anthropological analysis from the outside, together with constructive engagement from inside.

To effectively address and decipher the nature of NGO critiques and to compare them with the complexity of field realities, this research combines a literature review with an extended case study method. The literature review was used to identify common narratives and explanatory arguments appearing both in the moral justification of NGO action and to capture the discourses of its critics. This involved reviewing literature produced by conservation NGOs along with public discourse and academic analysis, where critiques have emerged within the last decade. The second methodological axis involved ethnographic methods, which have proven to be particularly productive in terms of capturing the slippery nature of NGOs as an object of study. The extended case study is based on ethnographic fieldwork stays in the Peruvian high jungle between 2007 and 2013 (Larsen 2015). For a long time, the area has been an established region for conservation efforts, offering a pertinent case study to explore evolving roles, practises and perceptions of NGO activity. Field data is based on participant observation, document analysis and semistructured interviews with NGO and local representatives.

The Good Conservationist and the Bad ‘Other’

A central master narrative among conservation NGOs couples public environmental good with wider narratives of biological crisis (Escobar 1998: 56). A useful example of such narratives of crisis and global action is the so-called ‘Morges Manifesto’—the founding document leading to the establishment of the World Wildlife Fund (WWF); it has since been renamed the World Wide Fund for Nature. Its title, ‘We Must Save the World’s Wildlife: An International Declaration’, speaks for itself (Morges Manifesto 1961). As the Manifesto stated, using war metaphors, there were ‘skilful and devoted men and admirable organisations … battling at this moment on many fronts’. It was an ‘emergency’ with a ‘vast number of fine and harmless wild creatures losing their lives, or their homes, in an orgy of thoughtless and needless destruction’.

In language resembling a humanitarian rescue mission, the ‘wildlife emergency’ stemmed from ‘ignorance, greed, and folly’. Animals were being ‘shot or trapped out of existence … drowned by new dams, poisoned by toxic chemicals, killed by poachers for game, or butchered in the course of political upheavals’. In response, the World Wildlife Fund was set up to offer the public ‘an effective simple means’ to save the world’s wildlife; it was to be a new organisation with ‘easy channels for all who want to help’ and ‘raise massive resources for the cause and distribute resources where they are most needed’. Advancing civilisation had to be stopped or as the title of 1969 album with the Bee Gees, the Beatles and others singing for the WWF went: ‘No One’s Gonna Change Our World’. On the album, the Beatles introduced ‘Across the Universe’. Cilla Black sang ‘What the world needs now is love’. Rolf Harris sang about the ‘Cuddly old Koala’, Lulu interpreted ‘I’m the Tiger’ and Bruce Forsyth presented ‘When I see an Elephant Fly’. Conservation NGOs were the moral guardians of the good in the ‘senseless orgy’ supported by the latest tunes of public culture. This Zeitgeist remains important to this day in the nature of conservation communication strategies.

Conservation NGOs are in many foundation narratives about the good against the ‘bad other’ that undermines the public environmental good. Now, I may be criticised for being unfair, even incorrect, in exemplifying the ‘good’ of NGOs with the emergency language from the late 1960s. The objectives and approaches of NGOs have evolved, it may rightfully be contended. Contemporary versions of the ‘good conservationist’ often are found no longer in the alarmist moral condemnation of civilisation and species loss, but increasingly in the positive techno-solution realm of sustainability guidance (Larsen 2013). In effect, conservation NGOs are in a constant process of (1) reinventing themselves, (2) redefining mission statements and (3) fine-tuning strategies into new forms of action. This author’s purpose is, not here at least, to enter the particular battlefields of what constitutes a good or bad conservation strategy. I argue, however, that it is essential to recognise the importance of the ‘good conservationist’ narrative as a moral constitution and an unwritten social contract between conservation NGOs and broader society. Conservation NGOs, in this meta-narrative, represent the good conservation cause against ‘bad reasoning’. It, as such, constitutes an existential reasoning based on moral grounds and values, on the one side, and technical competence and science on the other. This link was best articulated by the International Union for Conservation of Nature (IUCN) Secretary General Duncan Poore in 1977:

The Union is concerned with values more, I would say, even more than with science. For science should be the servant, not the master of mankind. Our strategy must be firmly based in realism, but it must move ahead with vision. We should be the architects of guided change (call it development if you will)—guided change in the direction of increasing the well-being of humankind—not only the standard of living but the good life, but (and the ‘but’ is all important) in such a way that the potential of the biosphere to support this good life is not diminished. (Holdgate 1999: 137)

Central to this narrative is not merely agency outside the realms of the state, but also more fundamentally the moral high grounds of technically sound agency above the temptations of real politik and short-termism. Corson (2010: 578), for example, speaks of conservation organisations capitalising through idealised visions of themselves as representatives of civil society countering private forces.

‘Good conservationist’ narratives are no longer only about conviction and identity, but they are tied to carefully designed branding operations (Rodríguez et al. 2007) and ‘the spectacle of capitalist conservation’ (Brockington and Duffy 2010: 473). Conservation NGOs have become ‘super brands’ with high levels of ‘consumer trust’ (Laidler-Kylander et al. 2007) leveraged by both the NGOs themselves and interested third parties, through partnerships and alliances by way of spectacular accumulation (Sachedina et al. 2010). ‘If you have the will, we will show you the way’, conservation NGOs tell the world through carefully orchestrated and competitive communication campaigns.

Such narrative positions justified the spectacular growth of sustainable development funding to conservation NGO work after the 1992 Earth Summit. Nongovermental organisations could deliver where states were absent, offering more efficient and competent solutions. Just as development NGOs experienced their heyday as alternatives to the failure and pitfalls of conventional development schemes, conservation NGOs initially thrived on the conservation boom of the 1990s. Nonetheless, where supporting conservation NGOs, like voting in a democracy, was a natural reflex of concerned citizens, arguably the picture has now changed somewhat.

The Ugly Conservationist

An increasingly common narrative portrays NGOs, no longer only as small, beautiful and ‘doing good’, but as turning big, ‘ugly’ and transnational. Public debate and a growing body of literature have within the last decade thrown into question the mandates, roles and effects of Northern NGOs. This critique has been launched particularly against the BINGOs. Such organisations, critics voice, do not thrive only on a moral mission and merit against all odds, but they increasingly rely on a capitalistic expansion of activities, public finance entanglements, and flawed corporate partnership projects that threaten what they set out to protect in the first place. Descriptions, mainly of BINGOs, have moved from portraying an idealist independent activity toward describing professionalised, managerial and internationally financed institutions. This has led to a shattering critique that erodes the moral premises of the ‘good conservationist’ narrative.

Why this change? The shift partially reflects a new empirical reality including the spectacular growth of conservation finance. Annual conservation funding is now estimated to be in the range of USD19.8 billion (Waldron et al. 2013). Today NGOs are not only among the biggest investors in conservation (Khare and Bray 2004), but also equally central in the management and spending of these resources. Contemporary NGO action cannot be understood outside this political economy. Challenging the idea that NGOs signal a strong civil society, wider analysis has pointed to the material pressures, institutional imperatives, insecurity and competition, which potentially can subvert NGO ideals (Cooley and Ron 2002).

Such phenomena are equally present in the conservation NGO field, the political economy of which is arguably distinct in at least two ways. On the one hand, NGOs have been prime receivers of post-Rio green financing, becoming convenient alternatives, or rather even outsourced flexible delivery mechanisms, to poor or downsized state arrangements. On the other hand, NGOs remain instrumental in setting up new funding schemes and shaping and channelling contemporary global conservation financing and flows. Both roles, as funding receivers or as gatekeepers, recently have been problematised, not the least being in the public space.

Naomi Klein and others have decried how ‘Big Green’ relies on capital investments in publicly traded securities in energy, materials and mixed assets. Environmental groups, she argues, have become ‘part-owners’ of industry, furthermore proposing ‘false solutions’ and dead ends under the banner of ‘constructive engagement’. Specifically, Klein listed conservation organisations as the Nature Conservancy with a USD1.4 billion endowment, trumping the Wildlife Conservation Society (WCS) with only a USD377 million endowment, and WWF US with a mere USD195 million. Klein’s message (2013) to Big Green is clear: ‘cut your ties with the fossils, or become one yourself’.

Reporter Oliver Steeds wrote about ‘Conservation’s Dirty Secrets’, whereas Canadian journalist Cory Morningstar spoke of the ‘non-profit industrial complex’ and ‘its role to undermine, marginalise and make irrelevant, the People’s Agreement’. 3 Alliances were being made with the powerful, not the dispossessed, his narrative goes. Morningstar ended by noting how ‘groups who continue to protect such interests must be considered complicit in crimes against humanity’. Mainstream conservation organisations were, noted by another observer, to be considered ‘perpetrators’ and ‘worst offenders’ not only limiting their work to trivialities but also in effect ‘legitimising plunder’ (Barker 2009). Critical voices from the global South equally see NGO power in opposition to people’s power. Arundhati Roy questioned the innocence of NGOs speaking of an ‘increasingly aggressive system of surveillance of increasingly hardening States’ (Roy 2012).

In Bolivia, NGOs have been accused of co-opting and making ‘hungry’ clients out of indigenous organisations and networks through soft dominance. The NGOs, the country’s Vice President argued, were not nongovernmental but organisations of other governments (Linera 2012: 30). The language used is remarkably forceful, stating it appears that green civil society was becoming uncivil, nongovernmental was becoming governmental or, even worse, corporate.

From this perspective, the acronym ‘NGO’ might be recast as ‘no good organisations’, ‘nongoverned organisations’, or even ‘nature-grabbing organisations’ after surveying the recent literature on green grabbing (Corson and MacDonald 2012; Fairhead et al. 2012). Moral resentment (Fassin 2013) that NGOs were siding with power, having ‘eaten of the forbidden fruit’, threatened the underlying ethical constitution of conservation NGOs. Their very social contract was under fire.

Critical scholarship equally has debunked the ‘doing good’ narrative, replacing it with less flattering depictions of bigger, bureaucratised and capitalised organisations (Brosius 1999; Escobar 1998). Where NGOs may challenge the state, they may equally offer convenient stop-gap measures to neoliberal policy change (Lewis and Kanji 2009: 18). Conservation NGOs in this vein of thought no longer offer a moral alternative, but they either are subdued by state operations or are caught up in mundane struggles over rights, property, accumulation and redistribution.

A prime example, a decade ago, came from anthropologist Mac Chapin (2004), who created a storm in the conservation community by publishing an article entitled ‘A challenge to conservationists’. It was a portrait of three conservation ‘giants’—that is, the WWF, Conservation International (CI) and The Nature Conservancy (TNC)—having grown ‘extremely wealthy and large’, while abandoning earlier commitments to collaborate with indigenous people. The attitude of conservationists was, Chapin (2004: 21) noted, that ‘they have the money and they are going to call the shots’. He described the spectacular growth of NGO funding, money dependence and the creation of NGO ‘gatekeepers’.

The anthropologist, in a sense, spoke truth to power, a position normally occupied by NGOs themselves. The WWF responded that Chapin’s analysis was ‘peppered with inaccuracies’, yet also resolved to take corrective measures (Roberts and Hails 2005). A member of CI spoke of the article as being ‘fraught with errors and unsubstantiated assertions’. Nonetheless, it pointed to friction and tensions arguably omnipresent across the NGO scene.

Such critiques undermined narratives of conservation NGOs as vectors of the good (against power), to portrayals of NGOs as creatures of power and hegemony (Corson 2010). Several NGOs were no longer only local and popular but global and elitist according to Holmes (2011). Such ‘grown-up’ NGOs have, put in somewhat colloquial terms, moved away from the innocence of green youth to become seasoned business-driven and political, if depoliticised, movers and shakers. Igoe and Brockington (2007: 439), for example, note how big conservation NGOs control ‘billions of dollars, employing tens of thousands of people worldwide, and adopting increasingly corporate strategies, organisation and cultures’. The moving of professionals from NGOs to corporate or governmental jobs are, in these narratives, orders of purity and danger and considered conspicuous. As Holmes (2011: 1) notes, conservation elites interact at conferences and ‘the roles of NGOs, corporations, and the state are increasingly indistinguishable’.

The NGOs are considered to be part of ‘inter-state and/or national power structures’, and ‘act increasingly like a morph between trans-national corporations and government development agencies’ (Jepson 2005: 516). They have become part of a ‘transnational capitalist class’ (MacDonald 2010: 542). Their failure to achieve conservation on the ground is perceived as a result of their ‘generalised global approaches’ (Rodríguez et al. 2007: 755). In particular, the critique is made in connection with market-based (‘neoliberal’) conservation approaches (Igoe et al. 2010). Nonetheless, other ‘scaling up’ and landscape approaches also are considered as a means of domination, further thriving in a neoliberal environment where conservation NGO boards are increasingly populated by corporate representatives (Corson 2010: 581; Holmes 2011: 6–7).

The argument goes even further in terms of capitalist penetration. Rather than producing alternatives, the ‘conservation mode of production’ produces images, enclosures and commodities ready for capitalist uptake. Conservation is no longer the bulwark against neoliberalism and the penetration of market ideology, but intimately tied to it (Corson 2010; Igoe and Brockington 2007). Brockington and Scholfield (2010: 554) thus argue about how conservation NGOs are ‘constitutive of, and central to, the workings and spread of capitalism in sub-Saharan Africa’. According to them, CI essentially has been involved in displaying how conservation has been capitalised and corporatised in terms of expertise networks, linkages with capital institutions and penetration.

MacDonald (2010: 535–36), for example, emphasises how institutional enclosures have resulted in NGOs ‘visibly and legibly aligning … activities, capacities and objectives with the ideological and material interests of the dominant actors’. Corson (2010: 579), furthermore, argues how this relies on a separation of financing for conservation abroad from the driving forces of consumption back home. Not only are market mechanisms rendered unproblematic but also partnerships with businesses are deemed essential to effective conservation. Organisations, from this perspective, are dependent on and ultimately shaped by resource allocation from an external environment driven by neoliberal premises. Because this challenges the founding narratives of ‘doing good’, the poor reception is not surprising (Igoe et al. 2010).

Still, have such critiques been overdone? Has critique of the ‘ugly’ conservationist become comfortably radical, potentially misinterpreting and, in some cases, even closing or undermining potential spaces for social change prompted by NGOs? It is thought-provoking that radical critique may appear side by side with government attacks on the NGO sector. The increasingly restrictive regulatory frameworks put in place to curtail NGOs’ action in several countries are a real political challenge. How then do we prevent anthropological analysis from becoming stuck in a wholesale post-developmental critique of ugly conservation, not to say misreading NGO tactics? Need we not broaden the scope of critical analysis? Can the answer be found in the pragmatism of what this chapter’s author labels the ‘Dirty Harry’ narrative, often highlighted in the line of defence by conservation organisations?

The ‘Dirty Harry’ of Conservation

Because the environmental issues facing humanity are massive and complex, we believe that the most effective way to find solutions is to work with other organisations, including corporations, governments and other NGOs. It is simply not sufficient to throw stones from the sidelines; we must work together to address the needs of a rapidly growing global population that is dependent on a fragile and already overstressed environment. (Seligmann 2011)

The preceding quote by Peter Seligmann, CEO and cofounder of Conservation International, is from a blog post entitled ‘Partnerships for the planet: Why we must engage corporations’. Whereas the ‘ugly conservationist’ narrative portrays organisations caught up in big finance, corporate engagement and neoliberal flirtations, what I call the ‘Dirty Harry’ narrative, stresses pragmatic conservation operators in a world of money and power. In reference to the famous detective film starring Clint Eastwood, the criminologist Carl Klockars (1980) conceptualised the ‘Dirty Harry problem’ as the ‘moral dilemma’ of whether to use ‘dirty means’ for ‘good ends’. Whereas Dirty Harry, a San Francisco cop, tracks down a serial killer sniping random victims, the ‘Dirty Harry’ of conservation has become the conservationist transgressing the moral codex of the ‘good conservationist’ to secure effective conservation results.

The credo of the ‘Dirty Harry’ narrative is that effective conservation requires discreet engagement, adequate resourcing and positive solutions. From a pragmatic conservationist perspective, increasing funds is a necessity in real-world conservation. Where campaigners remain stuck in green utopia, the ‘Dirty Harry’s of conservation get their hands dirty by managing big budgets and remaining on speaking and operational terms with both government and industry.

The question is no longer about ideological identification with good conservation values, but how to get the job done. Gone are the NGOs as the rebellious outsiders revolting against the system, yet without the means, connections and sagesse to make any real change happen. ‘Yes, there is money involved’ and ‘yes, there are contacts with corporate and government financing’, conservationists may retort. ‘Yes, conservation involves professionals and technical debates by professional staff members, rather than only volunteers’, they might add. What one on hand, may appear as a huge amount of resources as per observations of a ‘conservation industry’ is, from this perspective, a question of inadequate conservation finance dwarfed by other budget lines.

David Cleary, an anthropologist working with The Nature Conservancy, characterised Chapin’s (2004) early critique as ‘incomplete, naive, and overstated caricature of a complex reality’. Instead, he argued, conservation organisations need big budgets to scale-up activities and operate against power behind the scenes, passing intelligence to campaigners, rather than aligning themselves with the poor in public. 4 Should anthropology, in this sense, not get over its structural naiveté and come to terms with the contemporary realities of the ‘Dirty Harry’s of conservation?

Many anthropologists have, indeed, pursued this pragmatic strategy through intimate engagements within conservation NGOs from local-level conservation board membership to active involvement as staff or advisors. Some have contributed to public debates around conservation policy and practise, while others have remained involved in ‘internal’ discussions. Ranging from critique at the margins to mainstream policy support, pragmatic engagements in practise reveal high levels of complexity, problematising not only what NGOs do but equally how they engage with the state and corporate actors.

In effect, NGOs may support or substitute governments and the corporate sector because they may be financed, resisted or prohibited by them. They may be curtailed or co-opted as they wrestle from within the system. Working around state control of them is part and parcel of smooth NGO operations in many places. Doane (2014) offers a convincing portrayal of the ups and downs of an NGO-supported community conservation initiative Mexico confronted with decentralised authoritarianism of state agencies working against autonomy-inspired conservation. Language and activities often are tailored and constrained to fit distinct spaces of action, not reflect buy-in altogether. States may accept and allow NGO activity in noncontroversial fields, while restricting action in others (Gunte and Rosen 2012).

At stake, from this perspective, is a different NGO culture, not co-opted by capital but involving pragmatic operators working the system and market-based dynamics to build solutions from within rather than shining brightly from the outside. Nonetheless, such pragmatism comes with a cost. Still, rather than jumping to conclusions about ‘nature unbound’, of natural relations subjected to market dynamics, what studies in fact reveal are how growing organisations are being unbound and increasingly subject to the marketplace of conservation finance. This, in part, appears as legitimacy framed as ‘value for money’ rather than only value per se.

As former Director of the WWF, Jim Leape, noted in a 2012 public lecture in Geneva, organisations like the WWF ‘help crack the challenges, they [governments] can’t crack alone’. He mentioned how his brother, reportedly working for Greenpeace, would complain about how they would ‘open the door and WWF would enter’. 5 When campaign organisations stand on the grounds of conservation values, mainstream organisations get their hands dirty to get the job done. Engagement is framed by many environmental organisations as a prerequisite for being effective in today’s world (Jepson 2005: 517; MacDonald 2010). Such pragmatism—shifting from protest and activism to professionalism and advice—has long been a trend in mainstream conservation. As a 1976 Editorial in the IUCN Bulletin noted:

While it may be repugnant for conservationists to divert their precious energies from conservation proper, or to be involved in development at all. … [U]nless we are involved much (if not all) that we have achieved in the past and hope to achieve during the coming years, will be destroyed by the efforts to survive of millions of poor and hungry—helped only by biologically prodigal development on the one hand and socially naive conservation on the other, and therefore not helped at all. 6

As the initial Morges Manifesto (1961: 2–3) noted, ‘success would depend … on winning the respect and backing of other interests, which must not be overlooked or antagonised’. Indeed, from Rio and onward, the sustainability ‘bond’ cemented NGOs as partners of action in a new pledge: ‘No development without sustainability; no sustainability without development’ (Sachs 2010: 28). From going against development, conservation NGOs had become efficient vehicles to achieve it.

Nonetheless, whether such nonantagonism ultimately is successful or in practise undermines NGO independence and conservation impact is under constant debate. Interestingly, as global trends of NGO engagement with the corporate sector have increased, CEOs reportedly perceive a declining significance of NGOs as trendsetters. 7 Whereas 27% of CEOs in 2007 listed NGOs among their top three in terms of stakeholder groups influencing approaches to sustainability, this had fallen to 15% in 2013. Is the agenda-setting edge ability of NGOs eroding while they have grown in terms of size, budgets and power? Answering this question is beyond the scope this chapter. Yet, clearly part of the answer will rely on careful assessments of the shifting politics and practises of conservation NGOs (Robinson 2012). The following section explores such questions through a case study of conservation NGO activity in the Peruvian Amazon.

Doing Good in the Peruvian Amazon

‘We are like Don Quixote’, a conservationist exclaimed following yet another meeting about setting up a biosphere reserve in the central jungle area of Peru in early 2008. In the context of massive development pressures, he joked about the group of conservation players around the table on a noble quest to change the world. The image had a ring to it. The tireless group attempted to promote a biosphere reserve project, question the expansion of the electricity grid into a municipal nature reserve and otherwise get green issues on the agenda. Whereas Don Quixote regains sanity, these conservationists arguably pursued high goals and ideals against challenging development odds. They were, in the narrative sense, agents of the ‘good’. Many were NGO employees, others former ones. They were, I would argue, not merely acting through personal conviction, but also reenacting NGO identity narratives of environmental avant-gardism and commitment to the public good.

A quarter of a century prior to his critique of conservation NGOs, Mac Chapin, then a Latin American advisor at United States Agency for International Development (USAID), facilitated one of the agency’s first social and environmental impact assessments of a development project. Civil society critique, from anthropologists to indigenous organisations and their supporters had thrown into question government plans for road expansion and frontier settlements in the Peruvian Amazon (Smith 1982). The USAID financing and conditionalities eventually led to protected area creation, land titling and sustainable forest management projects. This reoriented project space, with only nominal state support, carved out a distinct managerial vacuum ready for NGO support. The Fundación Peruana para la Conservación de la Naturaleza (FPCN)—that is, the Peruvian Foundation for the Conservation of Nature, later recognised as ProNaturaleza (created in 1984) 8 —was the first national conservation NGO founded by key Peruvian conservationists 9 in response to the limitations of state action (Husock 1997). Protected area financing was not a public funding priority, and conservationists set up the foundation to receive international donor support. Whereas foreign support for conservation in the late 1970s was ‘never more than 8% of state contributions’ (Dourojeanni and Ponce 1978: 19), these figures would be reversed in the coming decades.

Shawn Miller (2007: 194) spoke of ‘Latin American nature’ generating ‘an unusually large share of first-world environmental anxiety’. Such anxieties after Rio translated into a managerial reconfiguration of problems as ‘technical’, centred around renewable resources (Chatterjee and Finger 1994; Hajer 1995), consolidating the role of NGOs as mediators between the resource-rich North and the biodiversity-rich South. The NGOs were among the key supporters, fundraisers and beneficiaries of the managerial paradigm and new finance mechanisms.

Whereas debt swaps and international finance during the late nineteenth century had fuelled the agricultural frontier in the Peruvian jungle, a century later Northern finance would (attempt to) render the region green. 10 The FPCN ‘became the means for international donors … to give meaning to Peru’s protected areas’ (Husock 1997: 4). Tropical forests predominated hotspot lists, and Oxapampa fit the bill, forming part of the tropical Andes—‘the richest and most biodiverse hotspot on earth … the global epicentre of biodiversity’ (Mittermeier et al. 1999: 69).

The NGO actions, during this period, were about filling the gap of an absent state. The FPCN’s aim was to become a ‘centre of excellence’ in conservation programmes and biodiversity projects (Husock 1997: 3). Founding logics were, in the language of this analysis, based on ‘doing good’ in technical terms by initially replacing the absent state by providing protected area management. It was not an activist NGO, but a foundation structure managed by conservation professionals and former government staff, essentially developing a kind of parallel public structure. Peruvian industrialists were soon to be members of the board (Husock 1997: 5). Not only did the NGO itself manage parks, but it also organised training and workshops on management planning. Although no formal mandate was given, FPCN initially had a ‘gentleman’s agreement’ and later, through donor pressure, obtained a ‘compact of cooperation’ (1986–1989), becoming like a de facto state-protected area authority (Ibid: 4–5).

One of its first major operations, with USAID and TNC support, was the direct management of the Yanachaga National Park in 1987. By 1990, the NGO was administering all the protected areas in the province. A few years later, the NGO supported three-quarters of the national protected area system, specifically in charge of 15 of them. 11 The FPCN even cosponsored the incorporation of a chapter on natural resources in the 1993 Constitution. 12 Obviously, this was much more than ‘doing good’.

It was NGO governance par excellence, replacing the state yet without having to deal with cumbersome national politics. Like many other NGOs, expansion relied heavily on a project economy, eventually becoming part of the multi-country ‘Parks in Peril’ 13 TNC flagship programme ‘transforming “paper parks” into functional protected areas’ (González and Martin 2007: Foreword). The TNC had, by then, grown from a small group of ecologists in 1950 to a major conservation player. By 2005, TNC had more than USD3.7 billion in assets and an annual revenue of USD800 million (Birchard 2005). For the Peruvian NGO, this entailed the emergence of a specific process of priority-setting that reflected managerial prerogatives of the organisation. In the Selva Central, this went from park-oriented support in the period from 1991 to 1997 to a second phase supporting two other protected areas in the province.

Although much of the preceding, in isolation, illustrates the emergence of a conservation NGO doing good fuelled by international support, there was more to the story. Global conservation finance fuelled NGO-driven problem analysis rendering conservation systems the locus of environmental problem solving. In the following years, a series of projects around biological diversity, forests and fauna nurtured a distinct green vision of Oxapampa and its management needs. This led to an emphasis on natural forest management and protected areas, with less emphasis on agricultural production, soil conservation and contamination issues.

The Ugly Conservationist?

The fuelling of green managerial power had social effects. The prior tying together conservation and social rights, which had mobilised protests and enabled protected area creation in the first place, was being undone. Indigenous communities, which had fought against logging and road expansion, were distanced from protected area management. Where indigenous organisations and their supporters had supported indigenous communal reserves, conservationists put a greater emphasis on conventional state-driven management responses (Larsen 2015). The NGO staff channelled the bulk of the funding to the uninhabited national park. ‘We had to prioritise’, as one conservationist explained (pers. comm.). As a result, NGO priorities shifted in 1997 when the government reclaimed direct management of the park. The state agency laid off all forest guards hired by the NGO, triggering a shift in role and perspective.

As the state focussed all its energy on the park, it left a residual project space for the NGO, by then renamed ProNaturaleza. Project attention was shifted to other protected areas from which the state still remained ‘absent’. The NGO initiated capacity-building support and studies in the San Matías-San Carlos Protection Forest and the Yanesha Communal Reserve. As Steven Sampson (2002) noted, ‘project life is a world with a premium on abstract knowledge, by which power accrues to those best able to manipulate key symbols and concepts’. Just like capital ventures are expected to generate yearly profits, conservation initiatives are expected to generate added value and success stories (Sachedina et al. 2010: 25). New capacity-building roles, and, most important, new projects were defined to target community organisations and local authorities. Nonetheless, this project economy, like many others, also had unintended consequences.

By 2006, ProNaturaleza, promoting the idea of a ‘Central Selva Biosphere Reserve’, had lobbied to place the proposal on the agenda of a decentralised Ministerial Council meeting. Even though it received support from Alejandro Toledo, the country’s president, alternative proposals stressing the need for more emphasis on the indigenous perspective emerged, eventually leading indigenous organisations to withdraw support. 14 ‘ProNaturaleza received a lot of money, dollars, in our name’, one informant mentioned. ‘Money was not invested here, where it should have been, it went to another site. … [T]hey would continue as usual, with millions of dollars … [but] our situation wasn’t changing’, another added (pers. comm.). Mistrust went beyond an individual project and was echoed by both indigenous leaders and local authorities on multiple occasions.

Although NGO work was appreciated and solicited, NGOs doing conservation good were seen equally as reaping benefits from environmental problems and leaving little behind. Critique was not the least rehearsed and was mobilized as part of local politics. The NGOs were easy targets and scapegoats for action, but equally visible manifestations of deep-running inequities. ‘The NGOs see us as children’, one indigenous leader stated. ‘You [indigenous] aren’t able to talk directly to the state … and the state equally thinks that as indigenous peoples, we aren’t yet civilized. … The NGOs and the church should be in charge, so that the indios get civilised’, he continued. One indigenous comunero (i.e., commoner) even criticised his own leaders using this image of NGOs: ‘[T]he presidents live big style, they have converted themselves into another ProNaturaleza’. Some NGOs representations featured four-wheel drive project vehicles, high salaries and office space. They were, in one sense, ‘ugly’ victims of their project success.

In the meantime, international support for conservation in the region was dwindling. Major projects came to an end, people were laid off and office facilities left at their bare minimum. The organisation had gone through a major financial crisis. Funding was gone, except for some minor projects, and the NGO was no longer offering big-scale solutions to forest and protected area management. Big conservation, it seemed, was only a shadow of its past. The NGO advisors, instrumental in supporting protected areas, had become consultants for local authorities, moved elsewhere or joined other institutions. Furthermore, despite long-standing criticism, indigenous organisations were busy setting up their own NGOs. By 2013, the indigenous federation of the Yanesha, the Federacion Comunidades Nativas Yanesha (FECONAYA), had set up its own organisation. Whereas indigenous political organisations relied on voluntary involvement, NGOs required ‘professionals’, mirroring the evolution of the national NGO culture during the 1980s and 1990s.

Another indigenous organisation, Asociación para el Manejo y Conservación de la Reserva Comunal Yanesha (AMARCY), with a protected area comanagement mandate for the Yanesha Communal Reserve, was equally contemplating formal recognition as an NGO. As Yanesha leaders went from critique of NGOs to setting up their own, it was all about activating the power of a social form they had experienced. It also involved adopting practises and language of the ingenieros (i.e., engineers), characterised by ambitious project proposals, reporting and PowerPoint presentations. As one Yanesha expressed it: ‘[I]f an NGO can fetch one million soles without consultation. … It’s time to turn the page and undertake direct negotiations’. Another Yanesha told this author, ‘We want our own NGO’.

One of their first sources of funding had been project development resources from an oil company. Yet leaders also were coming to terms with the ‘ugly’ side of project funding and power politics. An indigenous leadership crisis erupted in 2013 around the management of project resources. Funding from the oil company remained a major source of contention. Management of the NGO was at the heart of the matter and dynamics were strikingly similar to the narrative of ‘ugly conservation’. Still, the case also illustrates the limitations of stereotypical dichotomies between big conservation and local communities. Whereas ‘ugly conservationist’ elements appeared at different moments, use was transitory, rhetorical and part of complex local politics. Rather than a stable property of conservation NGOs, it even reappeared in the context of indigenous NGO creation. At stake were complex interplays between state politics, indigenous representative organisations, corporate players and shifting funding schemes.

Is ‘Dirty Harry’ in the Amazon?

Through our role as a technical advisor, we aim for efficient socio-environmental management allowing for spaces of communication between the local population and the executing companies of extractive and construction activity. – ProNaturaleza (Dourojeanni et al. 2012: 195, translated from Spanish)

During return visits to Central Selvl in 2010 and 2013, earlier project activities by ProNaturaleza had been sharply reduced. Nevertheless, programme activities in other parts of the country had grown considerably. The NGO was increasingly active in supporting environmental monitoring programmes for the oil and gas bonanza in the Peruvian Amazon (Finer et al. 2008). In 2001, ProNaturaleza had already begun to organize a community-based monitoring programme in the Camisea gas fields. The schemes were considered successful in terms of early detection of problems and preventing local conflicts in a ‘silent and routine form’ (Dourojeanni et al. 2012: 152). In a decade, such schemes had grown to become a major programme activity.

By 2013, the NGO was under contract to work on community monitoring with seven companies (five oil and two mining). The organisation described itself as a ‘technical advisory body’ defining one of its four strategic lines of activity as ‘searching for conservation and good land use in places where energy and road infrastructure projects are implemented through the reconciliation of corporate and local community interests’ (ProNaturaleza 2013: 9). Monitoring was the technical means to achieve this. Such win–win language around the effectiveness of technicality illustrated a distinct NGO positionality ‘outside’ the political battlefield. The director of the NGO would present the objective of involvement in monitoring as securing high standards of environmental quality in extractive projects, reducing levels of social conflict, maintaining fluid communication along with knowledge transfer and empowerment of communities (Dourojeanni et al. 2012: 7).

Participatory and community-based monitoring schemes were evaluated as ‘overwhelmingly beneficial’ in terms of offering ‘additional guarantees’, empowerment and an increased understanding (Ibid: 147). Companies were even considered to benefit ‘more’ from the scheme in terms of ‘avoiding conflicts, and to their own surprise, help them in avoiding otherwise grave accidents’ (Ibid: 151). Whereas the NGO in its early years aimed at transforming paper parks into effective management, the role in extractive industry monitoring increasingly involved becoming a trusted, efficient and competent service provider (Ibid: 186).

Had conservationist practise gone from civil society influencing state practise to become part of corporate project governance? Was it ‘Dirty Harry’ conservationism in practise? The monitoring scheme, practitioners argued, specifically involved empowering indigenous communities to set up their own monitoring bodies. Protests and denunciations were, from the NGO perspective, seen as ‘exaggerations’ and distortions provoked by special or ideological interests such as the nationalist left (Dourojeanni et al. 2012: 16). ‘Doing good’ was not about open campaigning and advocacy against oil in certain areas and alternative land use, but about demonstrating that the job could be done ‘properly’. It was about getting hands dirty to secure clean technologies.

In Oxapampa, where ProNaturaleza had been a major conservation pioneer, oil exploration was taking place within or next to the protected areas the organisation had established. Local authorities were confronted with major challenges to respond effectively to potential social and environmental impacts (Larsen 2011; Larsen and Gaspar 2012). Yet, despite having a national programme on oil monitoring, the NGO remained surprisingly silent on the topic of exploration activities compared to other NGOs and protected area authorities. Lack of project funding appeared to be the major reason, illustrating the fragile nature of NGO positioning on major development challenges. The NGO staff were well aware of the conflicts at stake; however, they also operated in project economy finance monitoring interventions elsewhere. Independent opinion was not absent per se, but it was channelled through and, in some respects, replaced by positionality determined by the political economy of project funding and was framed as technically sound project advice. Because NGOs are made up of various undertakings, projects in some respects made up the public face of NGOs de facto determining positionality.

While this chapter was being reviewed, the NGO (described as an ‘environmental consultancy’ by one observer) was hired by the oil company, Pluspetrol, to work in the neighbouring Concession 108 to set up a monitoring programme and citizen environmental vigilance programme. The USD200,000 project reported on the NGO website aimed to initiate a programme with ‘adequate local representation’ contributing to ‘improving the compliance of Pluspetrol in relation to commitments made in the environmental management plan’. 15 In a controversial and politicised exploration operation triggering significant protests, indigenous leaders and NGO staff, who previously challenged corporate oil, now offered local community members technical training to monitor operations and ‘improve compliance’.

The point here is that careful analytical attention is needed to consequences and the social effects of ‘Dirty Harry’ approaches to explore the conditions and implications of engagement. This challenges analysts to look beneath the narratives of strategy documents, and to work with a more fluid notion of NGO action crafted around actual practises of engagement and real-life project economies.

Discussion: Approaching NGO Complexity

ProNaturaleza and other NGOs have at different moments been viewed as doing good, representing the ugly and engaged in ‘Dirty Harry’ practises. Creation of NGOs was, for example, largely framed around ‘doing good’ by substituting or supporting an absent state. Fuelled by international finance, the NGOs grew rapidly, yet not without reactions. Local criticisms of NGO projects and distance to communities echoed the master narrative of ‘ugly conservation’. Finally, NGO repositioning as a technical advisory body to extractive industry projects evoked the master narrative of ‘Dirty Harry’ conservation. Still, such master narratives provide only a very partial picture of the complex dynamics involved.

First, the historical perspective planned in the Peruvian case study revealed major organisational changes within a short timespan. Conservation NGOs are rapidly evolving rather than stable organisations and fields of activity. Even though it is well recognised that NGOs are diverse (Igoe et al. 2010: 6), far more attention needs to be paid to (1) the internal heterogeneity, (2) the highly unstable terrains of conservation NGOs, and (3) the evolving conditions over time.

Second, the case points to the significance of changing waves of donor finance. The NGOs’ roles were closely tied to evolving conditions from levels of government involvement, resource politics and specific finance opportunities. The NGOs may indeed be conceived not as self-contained, but as entities that rely on external environments: ‘It is this dependence on an external environment that not only makes the control of organisational behaviour possible but almost inevitable as NGOs need to be appropriately responsive to that environment to assure continued access to the resources they need to survive’ (MacDonald 2010: 534).

Nongovernmental organisations are, in this sense, not organisations with a predefined agendas, but rather made up of embedded projects with implicit normative positioning. This raises questions not just about what NGOs do but also fundamentally about what they are. As Pinzas et al. (1997: 6) has noted: ‘Many of the NGOs are actually not organisations, but rather a loose collection of projects run by a single agent which are not interlinked or mutually supportive—if one fails, the remainder continue; the unsuccessful die and the successful grow’.

Although much attention is directed at NGOs themselves, this suggests the need for far more analytical attention to the surrounding social and political processes constraining or enabling specific forms of action. This is arguably at the heart of the literature situating NGO practise in the wider context of a political economy framed around neoliberalism as well as literature emphasising the determining role of donor priorities. Despite that, this also needs to go beyond the totalising gaze of neoliberal critique and to address the broader picture of contextual dynamics and politics.

Third, the case reveals the relevance of tracking NGO positionalities and relationships, both over time and across space, so as to capture their situational and contingent nature. Narratives stressing powerful NGOs tied into the corporate-status nexus reveal only one side of the coin. Brockington and Scholfield (2010), for example, note how conservation NGOs only support 15% of the protected area network in sub-Saharan Africa, influence being unevenly distributed among specific regions, countries and definite sites. Changing relations of cooperation, partnership and competition are central features of NGO activity (for the Guatemalan example, see Grandia 2010). Most NGOs are in a constant process of transforming associations and repositioning themselves in relation to internal or external factors such as international funding priorities (Grandia 2009). Rather than merely denouncing (lack of) interaction as ‘ugly conservation’ or displaying ‘Dirty Harry’ strategies, the question is whether and how strategies of ‘rapprochement’ are transforming conservation priorities and dynamics.

Critical questions are under what conditions and with what results, conservation NGOs engage with the corporate sector, government and international finance. This presents NGO studies with the challenge of capturing how shifts in financing and projects enable or foreclose specific NGO positions and their ability to actually influence change. The rise and fall of NGO power, staffing and field presence over time, because of changing flows of finance, are fundamental dynamics in this respect. In a recent review, Robinson (2012: 975) found little empirical evidence of NGO engagements with the corporate sector leading to better conservation results, even concluding not to ‘rely on corporations to meet conservation goals’. Portraying the variety of relations from dialogue to philanthropy and collaboration, his analysis specifically challenges win–win optimism based on voluntary measures and Corporate Social Responsibility (CSR).

Concluding Remarks: Rethinking the Anthropology of Conservation NGOs

Academic attention to the nature and the role of conservation NGOs is growing in parallel with the growth and transformation of the organisations themselves. Conservation anthropology has long interrogated the ‘local’ slot of conservation practise through problem analysis, field activities and policy work. The anthropology of conservation NGOs in turn has proved to be a productive reality check that stresses the power and politics of conservation practise. Critical analysis, for example, points to the growing importance of corporate partnerships and state imbrications of NGOs forming part of sustainability problems and power fields, rather than merely observing challenges from the outside. The discrepancies between NGO self-representation, and the tactics of professionalised bureaucracies of the big and capital-intensive conservation machineries, is a constant source of societal interrogation; need anthropological critique stop there? Has such critique of power become comfortably radical and, at times irrelevant, for the complex set of social battlefields making up nongovernmental conservation action?

Critical analysis may be more or less welcomed by the organisations themselves (Benjaminsen and Svarstad 2010; Igoe et al. 2010); however, it is arguably essential to foster a constructive debate about the role and contribution of civil society in addressing the daunting environmental challenges of our times. How is a critique of conservation NGOs maintained without throwing the baby, that of nongovernmental or civil society action, out with the bathwater? How is anthropology neither comfortably radical at a distance, nor comfortably operational from within the ‘social slot’? How are critical tools and findings better mobilized within conservation organisations to challenge working assumptions and modalities?

This chapter argues that master narratives around the good, the ugly or the ‘Dirty Harry’s of conservation continue to frame the contours of the debate, yet provide only partial insights into the complex realities of conservation NGOs. Between ‘the more NGO activity the better’ and a wholesale critique, a critical middle ground of anthropological analysis is emerging. This middle ground is fundamental both to capture problematic spaces and to alter institutional forms and practise worthy of anthropological exploration (Lockyer and Veteto 2013). This may avoid the traps of meta-narratives equalling BINGOs with big, bad and business-minded or, conversely, idealising small and beautiful Southern conservation efforts.

The problematisation of NGOs has opened new avenues of investigation into the changing conditions, uneven nature and evolving practises at stake. Conservation NGOs, like many other NGOs (Lewis and Kanji 2009), face choices about who to engage with, where to prioritise activities and how to engage with the wide range of stakeholders impacting and benefitting from conservation. In practise, a panoply of ‘hybrid’ conservation NGOs, defying conventional dichotomies, are found with varying degrees of international financing, local ownership and corporate involvement. This also concerns everyday decisions about how capacity-building is undertaken, how collaboration is built, and the extent to which vibrant local institutions are bolstered (Rodríguez et al. 2007: 756). The question is no longer whether NGOs (can) make a difference, but indeed ‘what’ difference they make as well as when, where and how they can make it.

What in one context might appear as professionalisation, bureaucratisation and monolithic power is countered by changing transformative politics, local alliances and internal heterogeneity in other cases. This entails a less essentialist and more dynamic notion of NGOs rather than attributing specific properties to them. Critical analysis need not limit itself to denouncing global power, corporate board membership and partnership language, but it might further explore the detailed trajectories of conservation impact, policy influence and long-term effects of such engagements. Considering that data on the effectiveness conservation and development NGOs often is scarce (Lewis and Kanji 2009; Robinson 2012), anthropological descriptions that pay attention to evolving NGO trajectories and shifting terrains of intervention, and their social effects, are among the most critical building blocks not only to the field of NGO studies but equally so for NGO practise at large.

Notes

  1. 1.

    This chapter was first presented as a paper at a panel entitled “The Anthropology of Conservation NGOs”, held in Chicago in December 2013. Thanks to other participants for stimulating discussions as well anonymous peer reviewers for insightful comments and suggestions.

  2. 2.

    Group mail received on 5 June 2013.

  3. 3.

    http://wrongkindofgreen.org/about-us/

  4. 4.

    http://www.thefreelibrary.com/more+responses+to+%22A+Challenge+to+Conservationists%22.-a0130057621. Accessed on 14 November 2013.

  5. 5.

    ‘Sustainable Development: The Agenda After Rio+20’, Conference given at IHEID, October 9, 2012.

  6. 6.

    Editorial Comment IUCN Bulletin, New Series 7(1), January 1976.

  7. 7.

    http:/www.theguardian.com/global-development-professionals-network/2013/sep/20/ngos-no-longer-set-agenda-development. Accessed on 10 May 2014.

  8. 8.

    In Peru, Pro Defensa de la Naturaleza (PRODENA) was the first NGO to deal with environmental matters particularly regarding natural resource management. Several successive splits from this organisation gave birth to Fundacion Peruana para la Conservacion de la Naturaleza (known as ProNaturaleza), Asociacion Peruana para la Conservacion de la Naturaleza (APECO) Asociacion de Ecologia y Conservacion (ECO) and other organisations that triggered the development of the environmental movement (Soria unpublished).

  9. 9.

    The three founders, Marc Dourojeanni, Carlos Ponce and José Rios were all La Molina Agrarian University faculty in the 1970s. Dourojeanni and Ponce had held key positions in the Directorate of Flora and Fauna.

  10. 10.

    Where the indebted Peru in the nineteenth century had offered British bondholders land in the Oriente, twentieth-century debt swaps offered to the German government and other protected area designation and management plans.

  11. 11.

    http://www.pronaturaleza.org/pronaturaleza-cumple-25-anos/. Accessed on 10 January 2011.

  12. 12.

    By 1995, FPCN had become ProNaturaleza, who cosponsored the constitutional element with an environmental lawyer NGO (Sociedad Peruana de Derecho Ambiental, SPDA).

  13. 13.

    This, mainly USAID, funded the TNC programme covering Latin America and the Caribbean ran for 17 years with projects for some USD104 million.

  14. 14.

    The biosphere reserve proposal, later renamed the Oxapampa Ashaninka Yanesha Biosphere Reserve, would eventually take off again with greater involvement and protagonism of the indigenous federations. Largely supported by NGO actors in the province, it would be approved in 2010.

  15. 15.

    http://pronaturaleza.org/wp-content/uploads/2013/nuestro-trabajo/promocion-de-la-responsabilidad-socio-ambiental/Pasco-Junin.pdf. Accessed on 27 April 2015.