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      Rethinking entrenched narratives about protected areas and human wellbeing in the Global South



            Attempts to link human development and biodiversity conservation goals remain a constant feature of policy and practice related to protected areas (PAs). Underlying these approaches are narratives that simplify assumptions, shaping how interventions are designed and implemented. We examine evidence for five key narratives: 1) conservation is pro-poor; 2) poverty reduction benefits conservation; 3) compensation neutralises costs of conservation; 4) local participation is good for conservation; 5) secure tenure rights for local communities support effective conservation. Through a mixed-method synthesis combining a review of 100 peer-reviewed papers and 25 expert interviews, we examined if and how each narrative is supported or countered by the evidence. The first three narratives are particularly problematic. PAs can reduce material poverty, but exclusion brings substantial local costs to wellbeing, often felt by the poorest. Poverty reduction will not inevitably deliver on conservation goals and trade-offs are common. Compensation (for damage due to human wildlife conflict, or for opportunity costs), is rarely sufficient or commensurate with costs to wellbeing and experienced injustices. There is more support for narratives 4 and 5 on participation and secure tenure rights, highlighting the importance of redistributing power towards Indigenous Peoples and Local Communities in successful conservation. In light of the proposed expansion of PAs under the post-2020 Global Biodiversity Framework, we outline implications of our review for the enhancement and implementation of global targets in order to proactively integrate social equity into conservation and the accountability of conservation actors.

            Main article text


            In 2010, state parties to the Convention on Biological Diversity (CBD) agreed to increase protected areas (PAs) to 17% of terrestrial and inland waters and 10% of marine and coastal areas [1]. Significant advances have been made towards this target [2]. Support is coalescing around a global target for the post-2020 Global Biodiversity Framework of 30% protection by 2030 [3] while the ‘Nature Needs Half’ campaign has also gained considerable momentum [4]. Recent studies reinforce the global importance of well-managed PAs in protecting species richness and abundance [5] and maintaining wildlife populations [6]. However, it has long been recognised that while they may contribute to wellbeing at the global scale through the ecosystem services (ES) they deliver such as carbon sequestration and hydrological functions [7], PAs can also bring costs as well as benefits to local populations [8]. This is especially true for the rural inhabitants of the Global South, who can experience opportunity costs [9], damage from wildlife [10] and displacement through eviction and cultural exclusion [11]. Protecting 50% of the Earth is likely to impact more than a billion people [12].

            With the rise of the concept of sustainable development in the early 1980s and especially in the wake of the 5th World Parks Congress in 2003, the idea that conservation and development are interdependent became mainstream [13]. It is now well accepted that the global good of conservation should not be delivered in a way that harms local people, and should in fact respect and contribute to the realisation of human rights [14,15]. The Durban Accord developed at the 2005 World Park Congress goes further to state that PA management must strive to reduce, and in no way exacerbate, poverty [16]. CBD parties, in turn, have emphasised the need for PAs to be established and managed through equitable processes that recognise and respect the rights of indigenous peoples, local communities and vulnerable populations [1]. A suite of approaches such as ecotourism, compensation, alternative livelihood schemes, community-based natural resource management (CBNRM) and efforts to secure tenure rights aim to meet these commitments on the ground. Calls to decolonise conservation have become increasingly forceful in recent years, casting new light on debates around the rights of Indigenous Peoples and Local Communities, participatory processes, benefit-sharing, social justice and equity, not least through recognition of the neocolonial nature of many conservation interventions [17,18]. There is urgent need to identify conservation approaches most likely to strengthen synergies between social and ecological gains that encompass equity and justice.

            Studies examining the relationship between PAs and human wellbeing paint a rather mixed picture of how policies have worked in practice. Controversy over PAs has partly been fuelled by the variety and distribution of impacts, the different methods used to capture them, and the different types of governance and management in place [19]. Reviews of the social impacts of PAs (e.g., [20,21]) have usefully characterised the types of outcomes evidenced, but have not fully examined the processes through which different outcomes arise for different social groups. A number of quantitative studies have shown a generally positive impact of PAs on economic wellbeing (e.g., [22]). While averaged material indicators allow analysis over larger scales, they miss valued aspects of human wellbeing and ignore questions of equity. Recent approaches to the social dimensions of PAs have taken a multi-dimensional view of human wellbeing that looks beyond material circumstances, to a subjective evaluation of one’s own life, and a relational component that focuses on how people engage with others to achieve their goals [23]. Conceptualisations of equity have also expanded from looking at the distributional impacts to encompass recognition of rights and values, and procedural aspects [24].

            Despite sometimes polarised debate and contested evidence, attempts to link human development and conservation goals remain a constant feature of policy and practice related to PAs [13,25]. Underlying these approaches are stories or narratives that have persisted through time about the relationships between the wellbeing or actions of local communities and conservation outcomes. The power of such narratives lies in the way they simplify complex and uncertain situations, but can unhelpfully become ‘blueprints’ for interventions that are ineffective in particular contexts [26]. Simplified stories serve to make decision-making more manageable and stabilise assumptions, becoming embedded in funding structures and networks of power [27]. For example, in the case of Namibian conservancies, win–win narratives are important for ‘public showcasing of success’ by donors and non-governmental organisations (NGOs), making critique often unwelcome [28]. Acknowledging shortcomings and understanding complexities, however, is likely to ultimately improve the sustainability of interventions [29].

            In this paper we examine evidence for five common narratives that underlie and justify PA establishment or management. The first narrative is that because the poor are most dependent on ES, conservation interventions that protect ecosystems will alleviate poverty, that is, they will be ‘pro-poor’ [30]. On the flip side, the assumption that poverty reduction will reduce people’s reliance on natural resources and therefore support conservation has underpinned popular integrated conservation and development projects (ICDPs) since the 1980s [31]. Where harm to local populations is unavoidable, the notion that this can be sufficiently compensated for through economic schemes, has had material consequences, for example, many millions of dollars being spent to offset the damage caused by wildlife around the world [32]. Participation by local communities is a mainstream idea in PA governance on the basis that it leads to more effective conservation than top-down approaches ([33]: although in practice ‘participation’ ranges from largely rhetorical to genuine engagement). Finally, secure tenure rights over land and resources for communities are increasingly considered an important foundation for attaining positive conservation outcomes [34]. The five narratives are defined in Box 1.

            Box 1.

            Definitions of narratives

            N1. Conservation is pro-poor: Because poor people are disproportionately dependent on ES, PAs that protect or enhance those services will alleviate poverty

            N2. Poverty reduction benefits conservation: Because poor people are disproportionately dependent on ES, improving their material wellbeing will reduce pressure on PAs

            N3. Compensation neutralises costs of conservation: Unavoidable costs of PAs for local people can be adequately offset by providing appropriate compensation

            N4. Participation is good for conservation: Local participation in PA governance is a route to more effective conservation

            N5. Secure tenure rights for local communities support effective conservation: Secure and well-defined rights of tenure to land and resources underpin positive social and ecological outcomes in and around PAs

            The objective of this paper is to examine if and how each narrative is supported or countered by the evidence from low- and lower middle-income countries. We use a mixed-method synthesis combining a critical review of recent relevant peer-reviewed literature and expert key informant interviews. We aim to capture wellbeing and equity outcomes across social, economic and political dimensions. In the context of ambitious aims for expanding PAs, better understanding of the complex trade-offs and synergies across social and ecological outcomes will be vital in negotiating and managing how post-2020 targets are translated into governance structures and implemented on the ground. There is a growing recognition that conserved areas outside formally designated PAs, such as indigenous and community managed areas, and privately managed areas have a role to play in conservation [35]. In line with latest policy we encompass the full range of PAs [36], including these other conservation areas, in both terrestrial and marine systems.


            The narratives were identified during a 2-day workshop through deliberative processes based on participants’ (conservation researchers and practitioners) knowledge. This involved identifying possible narratives in small groups, then discussing their importance and popularity in forming the basis for PA policy and practice based on participants’ experience and with reference to international conservation policy documents. The narratives were subsequently validated through a review of the websites of 169 conservation organisations operating in lower- and lower middle-income African countries and internationally (see Supporting Information, Conservation organisations; [37]) and through expert interviews (see below). One hundred and thirty-eight of these organisations employed at least one of the narratives in materials that described their work with more focus on N1 (118), N2 (108), N4 (84), than N3 (53) and N5 (39). Interviewees stated high levels of familiarity with the narratives especially N2, N4 and N5 (Supporting Information, Interview validation). We chose a mixed-methods approach to examine the complex relationships between PAs and human wellbeing within each narrative. We combined relevant elements of systematic reviews to select literature in a transparent and unbiased way [38] but limited the sample of papers in order to allow more depth of analysis, and carried out a narrative review more appropriate to capturing complexity, process and context [39,40]. On the principle that understanding complex conservation issues will benefit from a range of evidence from different sources [41], and recognising the value of expert knowledge and experience [42], we complemented the literature with key informant interviews with conservation researchers and practitioners.

            Literature search

            To search the literature on the social outcomes of PAs we combined two databases of evidence. First, we used a systematic map and database of 1043 studies published up to 2014 by McKinnon et al. [43] (available at https://natureandpeopleevidence.org), on the linkages between conservation interventions and human wellbeing in terrestrial and marine systems. We selected only peer-reviewed articles related to ‘area protection’ and/or ‘area management’ interventions in low- and lower middle-income countries only as designated by the World Bank (Supporting Information, World Bank Economies). We selected articles published after 2006 with a study date after 2003, to capture recent studies more reflective of people-centred approaches to PA conservation after the Durban Accord (2003) and the Millennium Ecosystem Assessment [44]. Our search resulted in a set of 285 relevant articles. These were screened on full text based on our exclusion criteria, reducing the set to 248 articles (Fig. 1; Supporting Information, Exclusion criteria).

            Figure 1

            Screening process and number of articles at each stage.

            Second, we updated the database beyond 2014 with our own systematic literature search. We used the same search terms as McKinnon et al. [43], but limited the intervention search terms to those related to PAs and other area-based conservation measures, drawing upon terms used in a systematic review by Pullin et al. [20] of protected areas and supplementing these with our own. Using Web of Science, we limited the search to English language, peer-reviewed articles, published after 2014 (Supporting Information, Search terms). The search retrieved 7096 articles. These were imported into an EPPI-Reviewer 4 and screened based on our exclusion criteria, first on title and abstract, and second on full text, reducing the articles to 207. These were combined with the 248 articles identified from McKinnon et al. [43]. Duplicates were removed and 10 papers were excluded due to poor transparency of methods, resulting in a final set of 437 articles.

            The 437 article abstracts (published between 2003 and 2017) were double screened for relevance to one or two narratives (with primary and secondary relevance agreed), resulting in 138 papers selected as relevant by two reviewers. Twenty papers were randomly selected from each set of papers per narrative for data extraction. Where fewer than 20 of the papers had primary relevance to one narrative, papers were selected from those that had secondary relevance. This was the case for N2 (one paper), N3 (one paper) and N5 (two papers). More papers were relevant to the Pro-poor (N1) and Participation (N4) narratives than to the remaining three narratives (Fig. 1). The location of PAs in the 100 papers were weighted towards Africa (63) and Asia (36), with only one paper from the Americas, and none from Oceania or Europe. This reflects both the disproportionate number of African and Asian countries categorised as low- and low middle-income (Supporting Information, World Bank economies), and publishing bias. Sixteen African countries and nine Asian countries are represented in the papers but with certain countries disproportionately represented: Tanzania (18); India (12); Nepal (10). Each paper was reviewed using a standard coding tool developed in Google Forms to extract and categorise the data relating to the study, PA, social outcomes and narratives (Supporting Information, Codebook).

            Expert interviews

            We carried out a total of 25 semi-structured interviews (either in person or on video call), including eight with academic researchers working on projects funded by the Ecosystem Services for Poverty Alleviation (ESPA) programme [45] and 17 with contacts of the authors working outside of academia. Interviewees were selected with the aim of achieving representation from different types of organisations across the globe, including international and in-country NGOs, state agencies and research organisations (Supporting Information, Non-academic interviewees) and for their experience in the governance of PAs and/or understanding their impacts. Interviewees were asked about their familiarity with each of the narratives and experience of their validity (Supporting Information, Interview questions). Interviews captured expert knowledge, long-term field experience and supported the identification and interpretation of key themes across the narratives.

            Narrative synthesis

            The publications that were randomly selected encompassed a range of designs, methods and data types (quantitative and qualitative), which was useful in exploring causal linkages, processes of change and contextual factors [46]. We assumed a level of quality through the peer-review processes of the journals, and used our expertise in the social sciences to assess the weight of evidence in support of the narratives in each paper which was categorised into strong (results fit the narrative with little deviation), partial (results are mixed or do not demonstrate the narrative in full) or none (results provide no support). Data from both the literature and interviews were combined in the analysis. A narrative synthesis aims to provide insight and deepen understanding rather than conventional systematic reviews which aim to answer specific questions [42]. We took a thematic synthesis approach [47], annotating and identifying themes within the extracted data and refining them in an iterative process. The findings are organised around these themes for each of the narratives in the text below and summarised in Table 1. The author carrying out the narrative review for each narrative reread the papers, extracted data, and interview transcripts, and the support categorisation and narrative text were discussed and agreed with the lead author.

            Table 1.

            Summary of evidence on the narratives

            Narrative shorthandSummary of evidence for the narrative
            N1: Conservation is pro-poorPAs can contribute to basic human needs and material poverty alleviation, but this is dependent on access. Due to exclusion, the poor commonly experience costs from PAs. Where multiple dimensions of wellbeing are included in studies, there are trade-offs and complexities in outcomes.
            N2: Poverty reduction benefits conservationFor improvements in wellbeing to benefit conservation, promoted changes must be suited to local values, linked to biodiversity and inclusive. Promotion of alternative livelihoods often leads to unintended negative social and ecological outcomes.
            N3: Compensation neutralises costs of conservationMaterial compensation is less relevant for supporting positive conservation outcomes than recognition of local social and cultural practices, and decision-making influence. Compensation schemes are also often hampered by low transparency and unequal impacts.
            N4: Local participation is good for conservationMeaningful participation, or more broadly the quality of governance, and extent of rights and control afforded to local communities, influence their motivation and capacity to conserve. Consultative participation or weak inclusion of marginalised groups hinders conservation.
            N5: Secure tenure rights support effective conservationSecure tenure rights can empower local communities to effectively conserve, but crucially this entails respect for customary and communal access systems. Conservation governance that only recognises formal property rights or causes tenure insecurity produces unequal impacts and weak local legitimacy.


            Narrative 1: Conservation is pro-poor

            This narrative asserts that as it is the poorest people who are most dependent on ecosystems for their livelihoods, biodiversity conservation through PAs can alleviate material poverty by securing provisioning ES such as food and fuel, and regulating services such as clean water [48,49]. This narrative would suggest that when there is loss of access to extractive uses economic benefits can come through tourism or payment mechanisms, for example, wildlife management areas (WMAs) are assumed to reduce poverty through increased income revenues from wildlife [50].

            Of the 20 selected papers, three provided strong support for the narrative, with five showing no support or providing evidence against, and a further 12 showing some support but with mixed (positive and negative) or weak effects (Fig. 2). Interviewees were divided in their support (Fig. 3). The explanation for these divergent results rests on several factors. First, the extent that PAs are pro-poor centres on people’s access to ES and their benefits, in turn dependent on the management system which can range from strictly protected to community-managed areas. Although some services can benefit all across a landscape (e.g., flood protection), the negative impact of exclusion for other services was evident in our sampled papers in both terrestrial [51,52] and marine PAs [53]. The poor living in and around PAs are also more exposed to ecosystem ‘disservices’ from wildlife such as crop-raiding [52,54] which can have wide-ranging and hidden impacts such as on psychological health and education [55].

            Figure 2

            Level of support shown by articles for each narrative.

            Figure 3

            Interview responses on the validity of each narrative. n = 22 as three interviewees chose not to answer these closed ended questions in the interviews.

            Nine of our interviewees questioned the logic of the narrative: the poor often do not benefit from ES from a PA, and in fact are more likely to lose out. The wealthy are better placed to benefit due to their higher capacity to capture resources and bypass access restrictions, especially if governance is weak. The papers that disaggregated data according to wealth supported this idea. For example, compared with poorer households, wealthy households participate more in Payment for Ecosystem Services (PES) schemes in PAs in Cambodia [56], benefit more in terms of food security from CBNRM in Tanzania [57] and access benefits from devolved forest management in Ethiopia [51]. Indigenous groups who are already socially marginalised are at particular risk of disproportionate harms if they are not given special protection, such as the Twa whose livelihoods and culture are intertwined with native forests in Rwanda [58]. The poorest and landless are more dependent on resources from PAs, and by necessity have to risk fines and imprisonment where there are legal restrictions [58,59]. Tourism benefits are also prone to elite capture without redistribution policies in place [55,56,60].

            Where poor local residents are not excluded from the benefits of conservation, the papers showed limited evidence that PAs are a pathway out of poverty, a message reflected in the literature on linkages between ES and poverty alleviation [48,61]. PAs more readily act as a social safety net preventing further poverty. For example, those most reliant on income from the Chiradzulu Forest Reserve, Malawi, are among the poorest, who have little education, more dependents, fewer assets and are more likely to be women [62]. The provision of forest products to the poor from Kibale National Park, Uganda protects them against desperation sales of farmland and thus sinking deeper into poverty [63]. One paper in our sample showed neutral impacts on food security [64], and Canavire-Bacarreza and Hanauer [65] show an average reduction in poverty in municipalities in Bolivia that have at least 10% of their areas covered by PAs. These papers represent a growing body of robust quantitative research providing evidence that some PAs in the Global South can reduce poverty or at least do not necessarily increase it especially where there is tourism and or the PA is not strictly protected (e.g., [22,66,67]) but do not look beyond objectively measured average material poverty and health.

            The papers in our sample that showed strong support for the narrative used variables and metrics centred on material wellbeing [62,63] with the exception of Canavire-Bacarreza and Hanauer [65], who measured average effects on a poverty index which incorporates education and health. Research that looked at changes in diverse aspects of wellbeing (e.g., non-use values, food security, empowerment) paints a more complex picture with gains in some variables and losses or no change in others [54,57,68]. Likewise, interviews suggested that the most important costs and benefits for wellbeing and local support for PAs may not be material, for example, cultural knowledge or a sense of autonomy. Gurney et al. [69] highlight this point: despite a positive impact on livelihood diversity and wealth from marine PAs in Indonesia, subjective wellbeing was negatively affected most likely due to increased conflict and unmet expectations.

            To fully understand the impacts of PAs, consideration must be given to the wider spatial, temporal and socio-economic context. The effect of PAs may be relatively limited where there are strong drivers of poverty or development related to market access, land policy and population changes [52,56]. Dawson and Martin [58] highlight how positive outcomes for biodiversity and wellbeing are in part dependent on the governance of the wider landscape outside of PAs and therefore provision of alternative vital resources. Studies that investigate impacts at different scales show that the validity of the narrative can change through time and space with trade-offs involved. Those closest to PAs or in more accessible areas tend to access benefits derived from ES such as income [62] or tourism infrastructure [70], but are also exposed to the damage from wildlife [55]. Temporal dynamics affect how benefits are realised: for example, benefits may be felt most during implementation when funding is available [69], or conversely may take time to be realised [57]. Positive benefits from long-term sustainability involve time-lags and in the case of mangrove protection, counteracted immediate losses of resources but with uncertain trajectories [71].

            Overall, our analysis suggests that it is possible for PAs to alleviate material poverty but the extent to which the PA will benefit the poor depends on a range of factors including restrictions to locally important ES (especially provisioning services), whether local people have the capability (related to wealth and status) to benefit from ES, and how the PA and wider landscape is governed.

            Narrative 2: Poverty reduction benefits conservation

            The idea that resource overexploitation is a response to poverty was first popularised amongst conservationists in the World Conservation Strategy of 1980 [72] and since then has formed the basis for an instrumental argument that poverty alleviation should be integral to conservation initiatives. This narrative, to varying extents, underpins ICDPs, alternative livelihoods and revenue sharing schemes from ecotourism. There are two principal rationales for such programmes: first, to provide economic substitutes that reduce reliance on natural resources and lessen environmentally damaging behaviours; and second, to increase local acceptance and support for conservation, creating positive change in attitudes and behaviours [73].

            There was mixed support for this narrative in our sampled literature and our interviewees were divided on its validity. Several papers did show how schemes designed to improve people’s material wellbeing positively influenced attitudes towards conservation (e.g., [74,75]), but this did not extend to strong evidence of change in behaviour or biodiversity outcomes. Those papers which studied behaviour showed some effects on reported extractive activities which were small and inconsistent [76] or reflected potential confounding factors [75]. Ecological outcomes were not maintained in the longer term [77] or were not clearly linked to social improvements [78]. The relationship between conservation attitudes and behaviour is not straightforward, and the evidence highlighted the need to understand not only attitudes towards conservation but towards PA staff and conservation organisations which can be instrumental in creating support [74].

            The experience of our interviewees suggests that the narrative is more valid when people perceive a direct link between the PA and benefits, they receive. This linkage can be achieved in two main ways; first where the livelihood intervention is materially dependent on effective conservation (ecotourism, agro-forestry and resource access), and second where there are economic incentives such as the conditionality of PES payments. In fact, the PES concept emerged as a counter-narrative to the assumption that support for local incomes automatically enhances conservation effectiveness, instead arguing that such support needs to be conditional on conservation performance [79]. Our sample included seven papers which looked at interventions in the former category, but positive effects were not more strongly evidenced than in other livelihood schemes. A case study provided by an interviewee documents one positive example: in the Amani Butterfly Project in northern Tanzania, successful butterfly farming relies on the existence of the PA natural forest and income from butterfly farming was positively associated with participation in forest conservation [80]. Farmers perceive a link between butterfly farming income and forest conservation, thus motivating behaviours such as tree planting and reporting of illegal activities. Although having a more logical basis, our interviewees suggested that in reality the socio-economic conditions conducive to such an arrangement are rare. The literature also suggests that these projects are no less susceptible to failures in implementation such as administrative delays, lack of technical support and unequal distribution of benefits which can all lead to erosion of trust and cooperation [81,82]. Our two sampled papers on PES, show that conditionality provides a better guarantee of positive environmental outcomes but impacts on poverty are dependent on the magnitude of payments which can often be small, and there is a tendency for benefits to be captured by elites [83,84].

            Providing benefits is not a guarantee of attitude and behaviour change. In many cases, especially where time is not a limiting factor, these livelihoods will supplement rather than substitute resource extraction. Where there are big risks associated with conservation such as human–wildlife conflict, these may be a barrier to changing attitudes even where people are benefiting [85]. On the other hand, where there are large economic gains from alternatives, they may have the unintended consequence of exacerbating pressure on PAs by encouraging in-migration or reinvestment [86,87]. Livelihood decisions are driven by a range of factors beyond economic costs and benefits. Projects implemented with little regard to local community needs or cultural identities which may be closely tied to resource-dependent livelihoods such as fishing are more likely to fail [88]. In marine PAs in the Philippines, where economic expectations are not being met, this has led to negative attitudes towards conservation. Chaigneau and Brown [89] suggest in this case that it is more realistic and sustainable to emphasise non-material bequest and aesthetic values which also produce positive attitudes and action against illegal fishing.

            Another key consideration is the differentiated nature of resource users. Although the poorest may be more dependent on natural resources, the wealthiest may be the heaviest extractors [90] and able to circumvent access restrictions [91]. As one interviewee pointed out, this creates a tension between strategies that will have the best outcomes for biodiversity and for poverty alleviation. Similarly, high natural resource dependency and lower social status for those in poverty restrict their ability to participate in poverty reduction programmes [81,92]. There are often larger forces at work in creating conservation problems at multiple organisational levels. Targeting only the livelihoods of local communities does not address wider drivers of unsustainable extraction such as fluctuating prices and political instability [90].

            Livelihood-based interventions continue to attract significant donor funding [93]. While improving livelihoods is a good thing in its own right, and can foster improved relationships and trust between communities and conservationists [94], there is a lack of evidence that this will inevitably result in improved ecological outcomes. In designing these projects, there is a need to understand the drivers of unsustainable resource extraction, the livelihood profiles of communities and the priorities of resource users. In theory, projects that link livelihoods to biodiversity and local people and/or involve conditionality are more likely to succeed in terms of ecological outcomes, but this may involve trade-offs with poverty alleviation.

            Narrative 3: Compensation neutralises costs of conservation

            This narrative accepts that there are unavoidable local costs to conservation in the form of access restrictions and human–wildlife conflict and assumes that these can be effectively offset thus fulfilling the ‘do no harm’ principle [95]. Compensatory approaches such as payments for harm caused by wildlife, resettlement, revenue sharing and development schemes, are driven not only by social justice concerns but also by efforts to reduce conflict and create positive attitudes towards conservation [96,97]. Increasingly, conservation is funded by major international donors who have explicit commitments to safeguard against negative social impacts and compensate for economic losses [98].

            None of the reviewed literature was strongly supportive of this narrative, with only five papers providing some evidence that compensation is supported by local communities and at least partially offsets costs. The reasons related to both the compensation itself and the way in which schemes are implemented. First, the assumption that material compensation is commensurate with losses incurred from PAs is problematic. Compensation is often considered insufficient and not reflective of market values. In our sampled literature this was the case for compensation provided for a range of impacts including livestock loss [99,100], constraints on forest activities [101] and crop-raiding [102]. Material compensation is incommensurate with cultural losses. For example, although Twa communities received material benefits from revenue sharing from the Bwindi National Park, they have lost social freedoms and cultural heritage associated with hunting [103]. In Madagascar, many older households would be unwilling to stop the practice of swidden agriculture (tavy) in exchange for compensation, due to its socio-cultural value [104].

            Material and monetary compensation is often provided for restricted access to land and displacement by PAs but may not account for material and non-material wellbeing losses. For example, land in resettlement villages was not perceived to be of comparable quality or quantity to that lost due to displacement from Suklaphanta Wildlife Reserve in Nepal, causing increased workloads, limited social interactions and reduced subjective wellbeing [105]. Land has cultural meaning, and places are intertwined with a sense of security, belonging, spirituality and identity that cannot be substituted [106,107]. Nevertheless, if community needs and aspirations are met, it is possible that resettlement can be carried out in a way that does not undermine people’s rights and wellbeing. For example, due to declining pastoral productivity and conflict with tigers, resettlement was the preferred option for the Gujjars in Nepal if it was associated with enhanced benefits including larger resettled land sizes, strengthened property rights and improved housing [108].

            Although there was a mixture of views among our interviewees on the validity of this narrative, those that agreed were cautious in their support due to the difficulties in quantifying the meaning that livelihood practices hold, the practical challenges in administering compensation and unfulfilled promises made by government agencies. But several respondents explained how compensation can play an important role and provide a level of legitimacy for PA interventions, where there are tangible losses such as to livestock and agriculture. In a human–wildlife conflict compensation scheme in India, despite numerous shortcomings, respondents still supported a reformed compensation approach where conflict cannot be avoided [100]. The prevalent view amongst our respondents was that although not sufficient as a standalone approach, appropriate and timely compensation can be an important element of conservation if reinforced with greater engagement and recognition of costs. This should involve commitment that goes beyond the provision of one-off payments to include, for example, preventative measures to reduce human–wildlife conflict. However, two respondents raised the point that the whole idea of compensation removes power and incentives away from communities to manage ecosystems sustainably.

            Even if compensation can work in theory, in practice schemes are often poorly implemented and administered. The process of claiming compensation can be long and tedious involving elaborate paperwork [99] and high transaction costs [100]. Where development projects are implemented, there can be a temporal mismatch whereby costs from resource access restrictions are immediate, but the benefits take time to emerge [101]. Limitations on the wildlife species included in compensation schemes or inappropriate methods to estimate compensation result in insufficient compensation [109]. Governments may fail to honour their commitments where compensation is not enshrined in policy or is associated with problems of corruption [100]. Inadequate or delayed compensation can develop deeply held grievances resulting in retaliatory killing of wildlife [110].

            There is significant evidence of distributional inequity in compensation programmes. Development programmes may not reach those experiencing the greatest costs from PAs, but instead cluster around village and tourist centres, exacerbating economic inequalities [101,111]. There are often barriers to the most vulnerable groups accessing compensation. Households receiving compensation tend to be larger and wealthier [100], more food secure, better socially connected and live in more accessible areas [112]. Women and the poor face greater difficulty in accessing compensation as they lack official title to land, awareness of schemes, literacy, time and familiarity with bureaucratic procedures [100,105]. Even where monetary compensation reaches the poor, they may not have the capacity to reinvest in buying land and restoring livelihoods [113]. The result is that marginalised groups receive the least from compensation, if anything at all, even in cases where safeguarding procedures are in place to ensure the contrary [112].

            In summary, the evidence rejects the idea that compensation as implemented is enough to substitute for experienced costs that often encompass non-material aspects of wellbeing and injustices. This does not mean that compensation is unnecessary, but it is rarely sufficient or commensurate. In addition, compensation mechanisms often do not work in practice, undermining social justice and support for conservation. Furthermore, our review suggests that there are situations in which compensation will never be commensurate with the loss incurred, thereby demanding greater openness to culturally appropriate alternatives.

            Narrative 4: Participation is good for conservation

            There are two inter-linked reasons why participation is assumed to be instrumental to effective conservation. Firstly, participation can empower local communities to govern resources sustainably, an argument that owes much to research into governing commons [114] and the value of local knowledge [115]. Secondly, participation may motivate local support and stewardship by providing economic and non-economic benefits [33]. In other words, this narrative holds that participation can provide both the opportunity and the motive for communities to support conservation.

            Such a narrative has ensured that participation became a central tenet of mainstream PA governance policy [16]. In international law it has also been clarified that procedural rights (access to information, participation in decision-making and access to justice) need to be respected in the designation and management of PAs [15]. The participation narrative has not gone completely unchallenged: a counter-narrative emerged around the turn of the century, questioning the effectiveness of participatory and community-based conservation [25]. In development studies some proclaimed participation a ‘new tyranny’ that served to reinforce unequal power relations and state control [116].

            In our sample of 20 articles, 18 were judged to support the narrative although only three showed a strong link between participation and ecological outcomes. This was reflected by the interviews, where all respondents agreed with the narrative, except two who remained neutral. This body of research largely confirms that participation contributes to both motivation and capacity to support conservation, but also qualifies this in terms of the range of benefits that can motivate local people and the quality of participation that is required to empower people. Motivations for participation appear to vary across cases, and across different social groups. Participation can be motivated by expected livelihood benefits [117119], but there are also several cases in which participatory conservation fails to deliver livelihood benefits yet is still valued for other reasons such as improved social capital [120], and sense of control [121]. According to one study, material motives are more important to men, whilst social motives are more important to women [122]. Whilst women may value participation for non-economic reasons, they are often less able to participate, due to constraints on their time or social barriers to taking on public roles [117,119,123125]. As confirmed by interviewees, participation can thus impose a social cost due to lost time or livelihoods that outweigh the benefits of participating, so transaction costs need to be minimised. On balance, the evidence confirms that the opportunity to participate in PA management is widely valued by local communities.

            The studies reviewed show us that the linkage between participation and effective conservation is not contingent on delivering livelihood benefits but can arise from either satisfying other needs and interests and/or triggering community capacity to control resource use. For example, a forest co-management programme in Malawi was found to have no short- or medium-term effect on household incomes, but participating households still cleared less forest than non-participants [126]. Similarly, participatory forest management in Tanzania did not provide measurable gains in wellbeing but forest governance was improved by reviving the community’s capacity to exclude outsiders [121]. Whilst community rights may be sufficient to unlock local capacity to manage resources, a study of marine fisheries in Kenya found that community co-management rights only led to positive ecological outcomes in conjunction with the establishment of no-take marine reserves highlighting the need for conducive socio-economic conditions and institutional capacities of communities [127].

            The reviewed studies show that local contexts lead to variation in what motivates participation and what communities can achieve with rights to participate. One finding that is consistent across all of the studies and confirmed in interviews, is that the quality of participation is crucial in determining both motive and capacity for conservation [128]. Participation is often tokenistic and superficial, and this is recognised by communities as constraining what they can achieve. Interviewees highlighted that meaningful participation means having the power to effect change regarding ecosystem governance. In a survey in the Taita Hills, Kenya, 33% of respondents identified the superficiality of participation as the greatest constraint on forest conservation [122]. In both of the negative cases in our sample, the quality of participation is a key factor in undermining benefits to communities although there is evidence that ecological outcomes are positive at least in the short-term due to access restrictions [129,130]. Four papers that were categorised as partially supportive showed that superficial participation had negative implications for sustainability. In the study of WMAs in Tanzania, participation was manipulative, disempowering and went hand in hand with demonstrable harm to local livelihoods [129]. However, as highlighted in the interviews, participation is an evolving process, and one that needs sufficient time and resources to allow people to build relationships and negotiation skills, a point evidenced in the broader literature [131,132].

            Our interviewees highlighted that the time, capacity and resources required for effective participatory processes often require the support of external agencies who can share the costs. For example, multi-community partnerships in marine PA sites in the Comoros, involving networks of communities, government and NGO actors, facilitated cooperation in fishery management ensuring all communities cooperated in fishery management on an equal footing [128]. Similarly, participation in marine PA sites in Indonesia was more extensive if management groups were supported by external institutions, such as through partnership with NGOs, academia and other community groups [133]. However, internal power structures will affect how participation takes place. Working through established customary governance arrangements is an effective route to establishing participatory conservation, but without mediation to steer negotiations towards inclusive governance, minority interests may get sidelined with repercussions for long-term sustainability [134].

            In summary, this narrative is supported by our review, although there is limited evidence linking participation to ecological outcomes. Based on our findings we would qualify the narrative somewhat, such that participation supports PA effectiveness where it genuinely empowers communities and provides benefits that are locally valued and equitably distributed.

            Narrative 5: Secure tenure rights for local communities support effective conservation

            Secure tenure rights are increasingly considered an important foundation for attaining positive conservation outcomes as they may increase the local legitimacy of and participation in conservation governance, promote the sustainable use of resources and foster local environmental stewardship against internal and external pressures [34,135]. The scope of legitimate tenure rights is not limited to individual property rights, which are often afforded greater legal status. Prominent theories, frameworks and international policy guidance defining tenure specifically include multiple types of tenure, and pivotally for conservation practice this includes customary and communal regimes and institutions [136], which are often side-lined as they comprise ‘informal arrangements’ and ‘unwritten customs and practices’ [137]. Increasing attention to security of tenure rights in conservation policy has resulted in the enhanced inclusion of areas managed by local communities within the global PA network [35]. Indigenous peoples already manage more than a quarter of the world’s land area but may struggle to protect these areas due to weak rights [138]. Clear and secure tenure rights are also pivotal for policy instruments such as PES or Reducing Emissions from Deforestation and forest Degradation (REDD+) to determine who is eligible to receive benefits and who is responsible for meeting contractual obligations [139]. Although absent in the Millennium Development Goals, tenure rights appear in five of the Sustainable Development Goals [140].

            Of the 20 sampled articles addressing this narrative, none provide opposing evidence while 11 provide strongly supportive evidence. Six of those show evidence of a positive association whereby recognition of tenure rights leads to enhanced social and ecological outcomes, whereas five exhibit a negative association through which violation of or insecurity caused to local communities’ tenure rights through externally driven conservation interventions produces negative social and ecological outcomes. A further eight studies provide partial support for the narrative but assume the positive or negative social impacts promote or harm conservation, respectively, without providing specific evidence. The one remaining study suggests that secure individual property rights enhance conservation, although without paying any attention to other forms of tenure or potential social impacts of favouring a formal, individual tenure system [141]. Interviewees were also largely supportive of this narrative.

            This set of cases highlights the pivotal importance of both tenure security based on customary and communal systems and of the scope of local influence in governance processes. At the most basic level, negative associations tend to occur when conservation interventions negate user rights with no regard for local needs or customary and communal institutions. In this situation, when a hegemonic model of conservation overrides existing systems through which rights are allocated among local communities, imposed structures may have negligible legitimacy and be entirely disregarded so that conservation goals are not met [142144]. For example, where conservation interventions recognise only legal or individual property rights as compatible with conservation rules and override customary and communal local institutions, this may favour more powerful local or non-local actors to the detriment of vulnerable groups including the poor, women and cultural minorities. Those requiring access to support livelihoods or engage in cultural practices may act in defence of their needs and rights by seeking to establish an alternative to exclusive conservation rules, often through negotiation with alternate authorities such as sympathetic local government officials, as described by Rahman et al. [145] in Bangladesh. Such a situation can open the door to elite collusion and capture because the conservation intervention triggers a renegotiation of tenure rights, threatening ecological integrity both outside of and within PAs [146,147]. Instances of negative social and ecological outcomes resulting from imposed tenure regimes were also evidenced through contemporary governance approaches such as REDD+ [148,149].

            The evidence suggests that to establish appropriate tenure security and sufficient rights to foster effective local stewardship, locally supported institutions that may have formed over long timescales need to be embedded within conservation structures that give sufficient confidence they will endure. Clear positive examples among the sample studies of recognising rights by embedding local tenure institutions within conservation included the Kasigau Corridor REDD+ project in Kenya that recognised communal forest tenure regimes [150], and the engaged stewardship and mobilisation of resistance to unsustainable logging in Cambodia [151]. Where secure tenure supports local livelihoods and fosters effective local stewardship it can be particularly important to protect those governance structures. For example, weakening of rights for betel nut growers in Soppinabetta forests in the Western Ghats of India to control resource use on their land led to many selling it for extractive development [152].

            It is also important to consider the extent of rights granted to different groups of people, looking beyond basic user rights to address rights of control and authority that determine who has power to make decisions about resource allocation and influence governance structures [153]. Provision of use rights alone may not be enough to prevent tenure insecurity arising, because if people fear those rights are likely to be removed or overruled and they lack any power to block those decisions, positive feedbacks for conservation may be foregone, as exemplified by Davis [154] for Maasai pastoralists impacted by a WMA in Tanzania. Indeed, three interviewees highlighted difficulties for pastoralist groups whose dynamic and seasonal customary systems of land and resource rights may be threatened through tenure formalisation processes. To nuance these findings further, several studies highlight the dangers of romanticising local institutions and their ability to govern natural resources adaptively and inclusively, particularly because management capacity and local cohesion may be lacking in the face of numerous drivers of social and institutional change at the local level [144,155].

            Our review also revealed the need to explore not just tenure systems but perceptions about the security of tenure rights, which can be a key determinant of behavioural change, even when tenure arrangements appear stable. Local perceptions of tenure security can be highly influenced by past experiences of policies enacted by states or colonial powers, and conservation interventions can be perceived as extensions of them [156,157]. Even if conservation authorities are trusted, perceived tenure security may be weak where the central government has a record of overriding them, for example, through the proliferation of land concessions for commercial, infrastructure and extractive industries in Cambodia [151].

            In summary, secure tenure rights can empower communities to sustainably manage resources and participate in effective ecosystem governance. However, respect for customary and communal access systems, and trust in the governance arrangements are critical for success.


            Our review shows that, in their simplest forms, commonly employed narratives linking protected areas to human wellbeing are not borne out in practice and a range of factors add complexity to the narratives. Crucially, our review illustrates that the model of conservation that is legitimated by simplistic versions of these narratives can inhibit the attainment of both the wellbeing of Indigenous Peoples and Local Communities and, ultimately, effective nature conservation. The findings suggest those involved in conservation need to critically examine the political nature of the ideas they adhere to, the way they are used to justify interventions and their means of implementation and serve to obscure local voices and experiences. Reductionist approaches to poverty alleviation, participation, benefit sharing and tenure all fall short of supporting rights, avoiding harms and in many cases of producing positive social and ecological outcomes. Our review findings are in line with a transformation towards decolonised and justice centred forms of conservation [158,159] and highlight ways in which the post-2020 biodiversity conservation strategies need to more explicitly and proactively integrate social equity, restorative justice, human rights and appreciate the social–cultural contexts and political histories of PA sites. We note points of progress in addressing social equity concerns in the draft of the post-2020 Global Biodiversity Framework [3], but the findings from our evidence synthesis also highlight significant gaps that continue to impede progress towards more equitable conservation that respects the rights of Indigenous Peoples and Local Communities in practice. Below we suggest how the 21 targets could be enhanced as well as interpreted and implemented at national and local levels (Table 2).

            Table 2.

            Implications of the narrative evidence review for the application of the post-2020 Global Biodiversity Framework

            Narrative shorthandImplication of the review for conservation practice and the application of post-2020 CBD targetsRelated goals and targets in draft post-2020 Global Biodiversity Framework [3]
            N1: Conservation is pro-poor
            • The full range of material and non-material costs and benefits PAs can have for local communities should be explicitly acknowledged, identified, assessed and addressed for conservation governance of any form

            • Ensure rights of access to local communities for sustainable resource use and cultural practices (see also narrative 5)

            • Proactive measures to ensure the poor and marginalised are represented and access benefits (e.g., redistribution of tourism income)

            • Restorative justice approaches to agree appropriate ways to redress historical and continuing harms

            • Ensure benefits, especially for the most vulnerable

            • Integrate biodiversity into poverty reduction strategies

            • Respect rights of IPLCs over resources

            N2: Poverty reduction benefits conservation
            • Poverty reduction strategies must consider local definitions of poverty and deprivation beyond income

            • Role of biodiversity in subsistence and meeting basic needs to be valued and safeguarded

            • Any benefits should be culturally appropriate

            • Interventions and programmes should aim to support local institutions and practices, not replace them

            • Ensure benefits, especially for the most vulnerable

            • Sustainable management of production systems

            • Benefit sharing from traditional knowledge

            • Integrate biodiversity into poverty reduction strategies

            • Ensure traditional knowledge guides decision-making

            N3: Compensation neutralises costs of conservation
            • Harms should be a last resort due to difficulties in making compensation fair or commensurate in practice

            • Where harms are unavoidable, ensure compensation attends to non-material and cultural losses as well as economic losses

            • Compensation schemes require equitable governance in the long-term, as benefits achieve little without empowerment and respect for local knowledge and institutions

            • Specific attention to the poorest, most marginal groups including women because elite capture should be expected

            • Ensure benefits, especially for the most vulnerable

            • Benefit sharing

            • Reform harmful incentives

            N4: Local participation is good for conservation
            • Focus on the extent and quality of participation (or of governance more broadly) rather than its occurrence

            • Establish and uphold standards for the continual influence and control of Iocal communities, from design stages, and a central role for local knowledge and institutions in governance

            • Decision making through locally legitimate authority, maximising inclusion especially for women

            • Establish relationships, trust between communities and non-local organisations, through conflict resolution as precursor to decision-making where necessary

            • Ensure traditional knowledge guides decision-making

            • Equitable participation in decision-making

            • Integrate biodiversity into poverty reduction strategies

            N5: Secure tenure rights support effective conservation
            • Define tenure to include customary and communal aspects, beyond individual, legal property rights

            • All signatory nations to CBD and authorities for any conservation programme should report on the assessment and inclusion of Indigenous Peoples and Local Communities’ communal and customary tenure systems

            • Establishment of new PAs or restoration programmes should build upon local traditional knowledge and institutions, and legitimise and support local tenure systems

            • Particular attention required to include the poor and marginalised social groups for whom land and resource access can be temporary, rented and undocumented tenancy

            • Targets for restoration and PA area extent

            • Ensure benefits, especially for the most vulnerable

            • Sustainable management of production systems

            • Nature-based solutions

            • Integrate biodiversity into poverty reduction strategies

            • Reform harmful incentives

            • Ensure traditional knowledge guides decision-making

            • Respect rights of IPLCs over resources

            Our analysis was based on a relatively small number of papers, and these were biased towards certain regions, and are certainly not representative of all PAs in the Global South. The studies also capture likely publishing bias against results of no impact. We counterbalanced this bias through interviews with experts with a variety of perspectives and experiences relating to PAs around the world including in the Americas. However, further research would be needed to discern how the narratives may play out differently in Latin America which is underrepresented in our study. Overall, our aim was to focus less on how common certain outcomes are but on how the narratives are complicated by realities to provide insights into how the relationships between PAs and wellbeing can be strengthened. We also recognise that there are other narratives underpinning conservation practice. The five we selected were deemed to be common and fundamental to interventions, but others are likely to exist, and likewise need to be critically examined.

            The simple assumption of N1 that ‘conservation is pro-poor’ can be mis-used to legitimise exclusionary PAs and systems of governance that are too often harmful for the wellbeing of communities. The pro-poor narrative is bolstered by the assumption that any costs to the poor can be suitably compensated for (N3). The counterclaim found in our review is that if conservation is to be genuinely pro-poor it will need to embrace a model that prevents harms rather than seeking to compensate for them. Instead any human rights restriction arising from PAs and subsequent compensation should be seen as a last resort. We also found N2 ‘poverty reduction benefits conservation’ to be a problematic narrative, in particular where this assumes that efforts to support livelihoods will lead to conservation effectiveness.

            There was more support for narratives 4 and 5 on participation and secure tenure rights, respectively, especially among our interviewees, pointing to the redistribution of power towards communities as important for conservation success over improvements and compensation in material poverty on their own. Although conservation can succeed in its ecological aims through enforcement [160] and participatory arrangements are far from being a panacea [161], the ethical basis for ensuring equity in conservation is well-accepted [16]. Recent research outside our sample tends to confirm that participation by local people can help to deliver both ecological and social objectives of PAs [21,162165]. It is striking, however, that even in so-called participatory forms of governance and tenure reform there is a tendency for elite capture and costs for the most marginalised. This highlights the vital importance of meaningful participation that genuinely empowers people to effect change through iterative and culturally appropriate processes, with benefits being distributed equitably, and the recognition of customary tenure rights that give authority and control to communities [166].

            Our review of evidence urges caution about the proposed expansion of PAs under the current draft of the post-2020 framework. At a superficial level, the 21 draft targets [3] appear to cover the multiple dimensions of equity or justice (distribution of costs and benefits, decision-making procedures and recognition of values, knowledge systems and institutions), through which the concerns of Indigenous Peoples and Local Communities and the poorest among them are often articulated [24]. The targets go slightly beyond previous principles by stating that systems of customary sustainable use should be protected (Target 9), and that communities, especially the most vulnerable, should receive equitable benefits from conservation, including nutrition, food security, medicines and livelihoods (Targets 9 and 13). Equitable and effective participation in decision-making and free prior and informed consent are explicitly targeted (Targets 13, 20 and 21), while respect for traditional knowledge and practices (Targets 13 and 20) and rights over land, territories and resources, for Indigenous Peoples and Local Communities as well as women, girls and youth (Target 21) appear to also be safeguarded [3]. Yet gaps remain between those principles and the nuanced issues highlighted through our evidence review (see Table 2). In general, the targets highlight Indigenous Peoples and Local Communities, women, youth and the vulnerable primarily as potentially impacted parties and a group of actors to be considered stakeholders, whereas phrasing should more proactively endorse their empowerment in PA governance and recognise the essential role their cultural values, customary institutions and stewardship actions play in conservation. Proposed targets do enshrine the importance of local community participation, yet ensuring the quality of participation remains the challenge. Genuine and enforceable procedural standards are needed, informed by the understanding that participation is an iterative process requiring time, resource, mutual learning, trust-building and respect for local forms of knowledge and decision-making [14].

            To foster meaningful inclusion and empowerment, attention must be specifically directed to the past experiences of displacement, disruption of knowledge systems and cultural practices, and political marginalisation suffered by many through colonisation, market-driven development and previous conservation interventions, which influence current relationships, expectations and the implementation of any current or future conservation initiative [11]. This has profound implications for the processes required to build the requisite trust for inclusion of the most vulnerable and marginalised, and to develop intercultural understanding for collaboration between plural knowledge systems. Such processes may entail conflict resolution or restorative justice approaches to attend to any historical and continuing effects on people’s wellbeing, their institutions, tenure security and rights, relationships and agency [116,129].

            In reality, while principles of equity have been espoused in global environmental agreements for at least 20 years [167], many national legal and political frameworks simply do not support the rights, cultural practices and institutions or empowered political influence of Indigenous Peoples and Local Communities, and consequently neither do many conservation interventions [159]. This persistent barrier to equitable conservation in practice means that the Global Biodiversity Framework must look beyond the principles themselves to focus more attention to the way those social and governance standards are to be implemented. Of importance here is the cursory reference under section J paragraph 18 to ‘responsibility and transparency…… in implementation of the framework’ [3]. The approaches for ensuring rights of access and tenure, territorial integrity and equitable and effective participation have seldom been monitored, reported or reviewed at any level in the past, resulting in an absence of accountability if social standards are not met [168]. These governance issues and the pathways to address them should be explicitly articulated. Governance quality, particularly an emerging focus on equity and rights, is receiving increasing attention within conservation policies [167], multi-stakeholder processes [169] and assessment tools [170], with potential to expose the flaws of conservation based on external assumptions about local communities and promote more nuanced approaches.

            Our research does not suggest that we should abandon attempts to link improvements in biodiversity and human wellbeing, but highlights the need for certain governance qualities, such as inclusiveness and adaptability. Dynamics for a given location fundamentally shape the relationships posited in the narratives, undermining the application of any kind of blue-print model for successful conservation and assumed synergies with local wellbeing, regardless of context. Conservation policy and practice therefore needs to reorient towards theories of change and types of governance more integrally structured around local knowledge and perspectives [171]. At the same time, conservationists need to recognise that communities invariably embody power dynamics allowing the well-placed to benefit from any intervention or change at the expense of the less well-placed. Women in particular tend to lose out in conservation processes, and gendered approaches to governance and impact evaluation are needed [172,173].

            Evidence across all the narratives reviewed highlights the importance of understanding wellbeing from the ground up rather than assuming people’s priorities and motivations [174]. This understanding must go beyond material dimensions to account for aspects of people’s lives that they value, and extend to ideas of justice, culturally specific relations with nature, customary tenure regimes and livelihoods. The evidence suggests that despite qualitative data on perceptions often being dismissed as ‘unscientific’ in the conservation literature [175], understanding local values and viewpoints such as perceived tenure security is vital in creating synergies between ecological and social outcomes. All too often, impact assessments of conservation focus on financial and material outcomes to the exclusion of social and cultural impacts [176]. Lack of attention to local values partly explains unfulfilled expectations, poor motivation and lack of local legitimacy, a thread running through the evidence base. For example, compensation should include consideration of immaterial damage affecting Indigenous Peoples and Local Communities’ subsistence and spiritual connection with their territory [177].

            The packaging of PAs as win–wins for biodiversity and human wellbeing downplays the inevitable trade-offs that occur in conservation and highlighted by our review between social and ecological outcomes, aspects of wellbeing, groups of people and different scales [178]. Acknowledgement of trade-offs supports more realistic acceptance of losses and opens up negotiation over choices and novel ideas about what success means and how to reduce or eliminate trade-offs, or what may not be appropriate to ‘trade-off’ [179,180]. In achieving the proposal to integrate biodiversity values into planning and development processes, governance structures must allow local participation in deliberations over wellbeing priorities, how they may link to biodiversity and the ecological realm, with recognition given to place-based knowledge about nature [181].

            Our review also highlights the value of taking a broader perspective beyond the boundaries of PAs, local communities and the present. Broader structural issues such as non-local resource demand and government policies are often the underlying cause of overexploitation of resources, poverty and changes in local management institutions and values [182,183]. Perhaps because of the difficulties of challenging these issues, conservationists have long focused on local ‘threats’ and individual agency [184]. Social justice approaches make imperative the need to shape broader drivers, requiring political engagement at multiple scales of governance on longer timescales. For example, historical injustices and land tenure policies that create insecurity must be redressed to build trust in current projects. Likewise, people’s priorities and conceptions of wellbeing will change within dynamic systems that shape people’s needs and desires, necessitating both adaptive governance systems and attention to the shifting broader socio-economic and political factors that may influence unsustainable practices.

            The conservation community have increasingly acknowledged the importance of considering local peoples’ experiences of and agency in conservation. But current proposals for meeting ambitious targets for protection post-2020 (e.g., [185,186]) need greater clarity on key issues such as governance qualities and how costs to local communities should ideally be mitigated, if unavoidable. The focus within global biodiversity policy debates on what proportion of the Earth to conserve, rather than how it is to be conserved, threatens to downplay the importance of addressing deficiencies in governance and equity outcomes from existing PAs as well as the broader drivers of unsustainable resource extraction. Our review suggests that future approaches should draw upon just and democratic forms of conservation that put local actors at the centre of decision-making and recognise their rights to land and resources and ensure conservation actors are accountable for upholding governance and equity standards. However, the lessons from 15 years of literature exploring the relationships between local people and protected areas and the experiences of practitioners highlights the complex building of collaboration and progressive political change this requires.


            This research was funded with support from the Ecosystem Services for Poverty Alleviation (ESPA) programme ‘Issues and Myths in Protected Area Conservation: Trade-offs and Synergies (IMPACTS)’ NE/P008097/1. The ESPA programme was funded by the Department for International Development (DFID), the Economic and Social Research Council (ESRC) and the Natural Environment Research Council (NERC). Natural Environment Research Council NE/P008097/1.


            We would like to thank the following people for contributing their ideas in two project workshops: Viola Belohrad, Neil Burgess, Gaby Gonzalez Cruz, Dipesh Joshi, James Kairo, Richard Kapere, Helen Schneider, Muhammad Waseem, and to the conservation researchers and practitioners who we interviewed. We are also grateful to students on the MSc in Conservation Science at Imperial College London for their research exploring the existence of the narratives in the work of conservation NGOs.

            Author contributions

            All authors contributed to the conception of this paper. CB and PB carried out the literature search and review; CB, EW, KH, ND, AM, JPGJ carried out the expert interviews; EW led the drafting of the paper; ND, AM, CB and PB wrote sections of the narrative review. All authors critically reviewed drafts of the paper and gave final approval for publication

            Open data and materials availability statement

            The datasets generated during and/or analysed during the current study are available in the repository: https://doi.org/10.5522/04/17153291.

            Declarations and conflict of interest

            Research ethics statement

            Ethical approval was granted by the Departmental Research Ethics Committee of University College London’s Anthropology Department.

            Consent for publication statement

            The authors declare that research participants’ informed consent to publication of findings – including photos, videos and any personal or identifiable information – was secured prior to publication.

            Conflicts of interest statement

            The co-author Elisa Morgera is an Editorial Board Member of this journal the article is published in, UCL Open: Environment, and the article went through the journals standard open peer review processes – all open peer review reports can be read freely online by following the DOI link of this article https://doi.org/10.14324/111.444/ucloe.000050. All other authors declare no conflicts of interest.


            1. CBD. The Strategic Plan for Biodiversity 2011–2020 and the Aichi Biodiversity Targets. 2010. Accessed 30 November 2020 www.cbd.int/doc/decisions/cop-10/cop-10-dec-02-en.pdf

            2. UNEP-WCMC, IUCN & NGS. Protected Planet Live Report 2020. Cambridge, UK; Gland, Switzerland; Washington, DC: 2020

            3. CBD. First Draft of the Post-2020 Global Biodiversity Framework. 2021 Accessed 14 September 2022 https://www.cbd.int/doc/c/abb5/591f/2e46096d3f0330b08ce87a45/wg2020-03-03-en.pdf

            4. Wilson EO. Half-Earth: Our Planet’s Fight for Life. New York: Liveright. 2016

            5. Gray CL, Hill SLL, Newbold T, Hudson LN, Boïrger L, Contu S, et al.. Local biodiversity is higher inside than outside terrestrial protected areas worldwide. Nat Commun. 2016. Vol. 7(1):1–7. [Cross Ref]

            6. Barnes MD, Craigie ID, Harrison LB, Geldmann J, Collen B, Whitmee S, et al.. Wildlife population trends in protected areas predicted by national socio-economic metrics and body size. Nat Commun. 2016. Vol. 7(1):1–9. [Cross Ref]

            7. Cumming GS. The relevance and resilience of protected areas in the Anthropocene. Anthropocene. 2016. Vol. 13:46–56. [Cross Ref]

            8. Balmford A, Whitten T. Who should pay for tropical conservation, and how could the costs be met? Oryx. 2003. Vol. 37(2):238–50. [Cross Ref]

            9. Poudyal M, Jones JPG, Rakotonarivo OS, Hockley N, Gibbons JM, Mandimbiniaina R, et al.. Who bears the cost of forest conservation? PeerJ. 2018. Vol. 2018(7):e5106. [Cross Ref]

            10. Green JMH, Fisher B, Green RE, Makero J, Platts PJ, Robert N, et al.. Local costs of conservation exceed those borne by the global majority. Glob Ecol Conserv. 2018. Vol. 14:e00385. [Cross Ref]

            11. Lele S, Wilshusen P, Brockington D, Seidler R, Bawa K. Beyond exclusion: alternative approaches to biodiversity conservation in the developing tropics. Curr Opin Environ Sustain. 2010. Vol. 2(1–2):94–100. [Cross Ref]

            12. Schleicher J, Zaehringer JG, Fastré C, Vira B, Visconti P, Sandbrook C. Protecting half of the planet could directly affect over one billion people. Nat Sustain. 2019. Vol. 2(12):1094–6. [Cross Ref]

            13. Roe D. The origins and evolution of the conservation-poverty debate: a review of key literature, events and policy processes. Oryx. 2008. Vol. 42(4):491[Cross Ref]

            14. Morgera E. Dawn of a new day? The evolving relationship between the Convention on Biological Diversity and international human rights law. Wake Forest Law Rev. 2018. 691–712. [Cross Ref]

            15. UN. Framework Principles on Human Rights and the Environment. 2018 Accessed 30 November 2020 https://undocs.org/A/HRC/37/59

            16. IUCN. Benefits Beyond Boundaries. Proceedings of the Vth IUCN World Parks Congress. Gland, Switzerland: IUCN. 2005

            17. Aini J, West P. Communities matter: Decolonizing conservation managementPlenary Lecture, International Marine Conservation Congress; 24–29 June; Kuching, Malaysia. 2018 Accessed 30 November 2020 https://paige-west.com/2018/07/28/decolonizing-conservation/

            18. Trisos CH, Auerbach J, Katti M. Decoloniality and anti-oppressive practices for a more ethical ecology. Nat Ecol Evol. 2021. Vol. 5:1205–12. [Cross Ref]

            19. Brockington D, Wilkie D. Protected areas and poverty. Philos Trans R Soc Lond B. 2015. Vol. 370(1681):20140271. [Cross Ref]

            20. Pullin AS, Bangpan M, Dalrymple S, Dickson K, Haddaway NR, Healey JR, et al.. Human well-being impacts of terrestrial protected areas. Environ Evid. 2013. Vol. 2(1):1–41. [Cross Ref]

            21. Oldekop JA, Holmes G, Harris WE, Evans KL. A global assessment of the social and conservation outcomes of protected areas. Conserv Biol. 2015. Vol. 30(1):133–41. [Cross Ref]

            22. Andam KS, Ferraro PJ, Sims KRE, Healy A, Holland MB. Protected areas reduced poverty in Costa Rica and Thailand. Proc Natl Acad Sci USA. 2010. Vol. 107(22):9996–10001. [Cross Ref]

            23. Coulthard S, Mcgregor JA, White C. Multiple dimensions of wellbeing in practiceSchreckenberg K, Mace G, Poudyal M. Ecosystem Services and Poverty Alleviation: Trade-Offs and Governance. London: Routledge. 2018. p. 243–56. Accessed 30 November 2020 [Cross Ref]

            24. Schreckenberg K, Franks P, Martin A, Lang B. Unpacking equity for protected area conservation. Parks. 2016. Vol. 22(2):11–28. [Cross Ref]

            25. Hutton J, Adams WM, Murombedzi JC. Back to the barriers? Changing narratives in biodiversity conservation. Forum Dev Stud. 2005. Vol. 32(2):341–70. [Cross Ref]

            26. Roe E. “Development narratives” or making the best of development blueprints. World Dev. 1991. Vol. 19(4):287–300. [Cross Ref]

            27. Blaikie P. Is small really beautiful? Community-based natural resource management in Malawi and Botswana. World Dev. 2006. Vol. 34:1942–57. [Cross Ref]

            28. Koot S, Hebinck P, Sullivan S. Science for success – a conflict of interest? Researcher position and reflexivity in socio-ecological research for CBNRM in Namibia. Soc Nat Resour. 2020. [Cross Ref]

            29. Catalano AS, Lyons-White J, Mills MM, Knight AT. Learning from published project failures in conservation. Biol Conserv. 2019. Vol. 238:108223. [Cross Ref]

            30. Howe C, Corbera E, Vira B, Brockington D, Adams WM. Distinct positions underpin ecosystem services for poverty alleviation. Oryx. 2018. Vol. 54(3):375–82. [Cross Ref]

            31. McShane TO, Newby SA. Expecting the unattainable: the assumptions behind ICDPsMcShane TO, Wells MP. Getting Biodiversity Projects to Work: Towards More Effective Conservation and Development. New York: Columbia University Press. 2004. p. 49–74

            32. Ravenelle J, Nyhus PJ. Global patterns and trends in human-wildlife conflict compensation. Conserv Biol. 2017. Vol. 31(6):1247–56. [Cross Ref]

            33. Agrawal A, Ribot J. Accountability in decentralization: a framework with South Asian and West African cases. J Dev Areas. 1999. Vol. 33:473–502. [Cross Ref]

            34. Robinson BE, Masuda YJ, Kelly A, Holland MB, Bedford C, Childress M, et al.. Incorporating land tenure security into conservation. Conserv Lett. 2017. Vol. 11(2):e12383. [Cross Ref]

            35. Dudley N, Jonas H, Nelson F, Parrish J, Pyhälä A, Stolton S, et al.. The essential role of other effective area-based conservation measures in achieving big bold conservation targets. Glob Ecol Conserv. 2018. Vol. 15:e00424. [Cross Ref]

            36. IUCN. Recognising and Reporting Other Effective Area-Based Conservation Measures. Gland, Switzerland: IUCN. 2019

            37. Brockington D, Scholfield K. The work of conservation organisations in sub-Saharan Africa. J Mod Afr Stud. 2010. Vol. 48(1):1–33

            38. Haddaway NR, Woodcock P, Macura B, Collins A. Making literature reviews more reliable through application of lessons from systematic reviews. Conserv Biol. 2015. Vol. 29(6):1596–605. [Cross Ref]

            39. Cornish F. Evidence synthesis in international development: a critique of systematic reviews and a pragmatist alternative. Anthropol Med. 2015. Vol. 22(3):263–77. [Cross Ref]

            40. Mallett R, Hagen-Zanker J, Slater R, Duvendack M. The benefits and challenges of using systematic reviews in international development research. J Dev Eff. 2012. Vol. 4(3):445–55. [Cross Ref]

            41. Adams WM, Sandbrook C. Conservation, evidence and policy. Oryx. 2013. Vol. 47(3):329–35. [Cross Ref]

            42. Greenhalgh T, Thorne S, Malterud K. Time to challenge the spurious hierarchy of systematic over narrative reviews? Eur J Clin Invest. 2018. Vol. 48(6):e12931. [Cross Ref]

            43. McKinnon MC, Cheng SH, Dupre S, Edmond J, Garside R, Glew L, et al.. What are the effects of nature conservation on human well-being? A systematic map of empirical evidence from developing countries. Environ Evid. 2016. Vol. 5(1):8[Cross Ref]

            44. Millennium Ecosystem Assessment. Ecosystems and Human Well-Being: Synthesis. Washington, DC: Island Press. 2005

            45. ESPA. Ecosystems Services for Poverty Alleviation (ESPA). Accessed 12 September 2018 http://www.espa.ac.uk/

            46. Woodhouse E, Homewood KM, Beaucham E, Clements T, McCabe JT, Wilkie D, et al.. Guiding principles for evaluating the impacts of conservation interventions on human well-being. Philos Trans R Soc Lond B. 2015. Vol. 370:1681[Cross Ref]

            47. Snilstveit B, Oliver S, Vojtkova M. Narrative approaches to systematic review and synthesis of evidence for international development policy and practice. J Dev Eff. 2012. Vol. 4(3):409–29. [Cross Ref]

            48. Turner WR, Brandon K, Brooks TM, Gascon C, Gibbs HK, Lawrence KS, et al.. Global biodiversity conservation and the alleviation of poverty. BioScience. 2012. Vol. 62(1):85–92. [Cross Ref]

            49. Roe D, Seddon N, Elliott J. Biodiversity Loss is a Development Issue A Rapid Review of Evidence. London: IIED. 2019

            50. Keane A, Lund JF, Bluwstein J, Burgess ND, Nielsen MR, Homewood K. Impact of Tanzania’s Wildlife Management Areas on household wealth. Nat Sustain. 2020. Vol. 3:226–33. [Cross Ref]

            51. Mohammed AJ, Inoue M. Forest-dependent communities’ livelihood in decentralized forest governance policy epoch: case study from West Shoa zone, Ethiopia. J Nat Res Policy Res. 2013. Vol. 5(1):49–66. [Cross Ref]

            52. Vedeld P, Jumane A, Wapalila G, Songorwa A. Protected areas, poverty and conflicts. A livelihood case study of Mikumi National Park, Tanzania. For Policy Econ. 2012. Vol. 21:20–31. [Cross Ref]

            53. Moshy VH, Bryceson I, Mwaipopo R. Social-ecological changes, livelihoods and resilience among fishing communities in Mafia Island Marine Park, Tanzania. Forum Dev Stud. 2015. Vol. 42(3):529–53. [Cross Ref]

            54. Amin A, Koné I. People and protected areas: an assessment of cost and benefits of conservation to local people in Southeastern Ivory Coast. Soc Nat Res. 2015. Vol. 28(9):925–40. [Cross Ref]

            55. Tumusiime DM, Vedeld P. Can biodiversity conservation benefit local people? Costs and benefits at a strict protected area in Uganda. J Sustain For. 2015. Vol. 34(8):761–86. [Cross Ref]

            56. Beauchamp E, Clements T, Milner-Gulland EJ. Assessing medium-term impacts of conservation interventions on local livelihoods in Northern Cambodia. World Dev. 2018. Vol. 101:202–18. [Cross Ref]

            57. Pailler S, Naidoo R, Burgess ND, Freeman OE, Fisher B. Impacts of community-based natural resource management on wealth, food security and child health in Tanzania. PLoS One. 2015. Vol. 10(7):e0133252. [Cross Ref]

            58. Dawson N, Martin A. Assessing the contribution of ecosystem services to human wellbeing: a disaggregated study in western Rwanda. Ecol Econ. 2015. Vol. 117:62–72. [Cross Ref]

            59. Tumusiime DM, Vedeld P, Gombya-Ssembajjwe W. Breaking the law? Illegal livelihoods from a protected area in Uganda. For Policy Econ. 2011. Vol. 13(4):273–83. [Cross Ref]

            60. Richardson RB, Fernandez A, Tschirley D, Tembo G. Wildlife conservation in Zambia: impacts on rural household welfare. World Dev. 2012. Vol. 40(5):1068–81. [Cross Ref]

            61. Suich H, Howe C, Mace G. Ecosystem services and poverty alleviation: a review of the empirical links. Ecosyst Serv. 2015. Vol. 12:137–47. [Cross Ref]

            62. Kamanga P, Vedeld P, Sjaastad E. Forest incomes and rural livelihoods in Chiradzulu District, Malawi. Ecol Econ. 2009. Vol. 68(3):613–24. [Cross Ref]

            63. Naughton-Treves L, Alix-Garcia J, Chapman CA. Lessons about parks and poverty from a decade of forest loss and economic growth around Kibale National Park, Uganda. Proc Natl Acad Sci USA. 2011. Vol. 108(34):13919–24. [Cross Ref]

            64. Darling ES. Assessing the effect of marine reserves on household food security in Kenyan coral reef fishing communities. PLoS One. 2014. Vol. 9(11):e113614. [Cross Ref]

            65. Canavire-Bacarreza G, Hanauer MM. Estimating the impacts of Bolivia’s protected areas on poverty. World Dev. 2013. Vol. 41:265–85. [Cross Ref]

            66. Naidoo R, Gerkey D, Hole D, Pfaff A, Ellis AM, Golden CD, et al.. Evaluating the impacts of protected areas on human well-being across the developing world. Sci Adv. 2019. Vol. 5(4):eaav3006. [Cross Ref]

            67. Sims KRE, Alix-Garcia JM. Parks versus PES: evaluating direct and incentive-based land conservation in Mexico. J Environ Econ Manage. 2017. Vol. 86:8–28. [Cross Ref]

            68. Tobey J, Torell E. Coastal poverty and MPA management in mainland Tanzania and Zanzibar. Ocean Coast Manage. 2006. Vol. 49(11):834–54. [Cross Ref]

            69. Gurney GG, Cinner J, Ban NC, Pressey RL, Pollnac R, Campbell SJ, et al.. Poverty and protected areas: an evaluation of a marine integrated conservation and development project in Indonesia. Global Environ Change. 2014. Vol. 26:98–107. [Cross Ref]

            70. Akyeampong OA. Pro-poor tourism: residents’ expectations, experiences and perceptions in the Kakum National Park area of Ghana. J Sustain Tour. 2011. Vol. 19(2):197–213. [Cross Ref]

            71. McNally CG, Uchida E, Gold AJ. The effect of a protected area on the tradeoffs between short-run and long-run benefits from mangrove ecosystems. Proc Natl Acad Sci USA. 2011. Vol. 108(34):13945–50. [Cross Ref]

            72. IUCN, UNEP, WWF. World Conservation Strategy: Living Resource Conservation for Sustainable Development. Gland, Switzerland: IUCN. 1980

            73. Spiteri A, Nepal SK. Incentive-based conservation programs in developing countries: a review of some key issues and suggestions for improvements. Environ Manage. 2006. Vol. 37(1):1–14. [Cross Ref]

            74. Nepal S, Spiteri A. Linking livelihoods and conservation: an examination of local residents’ perceived linkages between conservation and livelihood benefits around Nepal’s Chitwan National Park. Environ Manage. 2011. Vol. 47(5):727–38. [Cross Ref]

            75. Solomon J, Jacobson SK, Liu I. Fishing for a solution: can collaborative resource management reduce poverty and support conservation? Environ Conserv. 2012. Vol. 39(1):51–61. [Cross Ref]

            76. Torell E, McNally C, Crawford B, Majubwa G. Coastal livelihood diversification as a pathway out of poverty and vulnerability: experiences from Tanzania. Coast Manage. 2017. Vol. 45(3):199–218. [Cross Ref]

            77. Aheto DW, Kankam S, Okyere I, Mensah E, Osman A, Jonah FE, et al.. Community-based mangrove forest management: implications for local livelihoods and coastal resource conservation along the Volta estuary catchment area of Ghana. Ocean Coast Manage. 2016. Vol. 127:43–54. [Cross Ref]

            78. Sheppard DJ, Moehrenschlager A, Mcpherson JM, Mason JJ. Ten years of adaptive community-governed conservation: evaluating biodiversity protection and poverty alleviation in a West African hippopotamus reserve. Environ Conserv. 2010. Vol. 37(3):270–82. [Cross Ref]

            79. Ferraro PJ, Kiss A. Direct payments to conserve biodiversity. Science. 2002. Vol. 298(5599):1718–9

            80. Morgan-Brown T, Jacobson SK, Wald K, Child B. Quantitative assessment of a Tanzanian integrated conservation and development project involving butterfly farming. Conserv Biol. 2010. Vol. 24:563–72. [Cross Ref]

            81. Thapa Karki S. Do protected areas and conservation incentives contribute to sustainable livelihoods? A case study of Bardia National Park, Nepal. J Environ Manage. 2013. Vol. 128:988–99. [Cross Ref]

            82. Acheampong E, Insaidoo TFG, Ros-Tonen MAF. Management of Ghana’s modified taungya system: challenges and strategies for improvement. Agrofor Syst. 2016. Vol. 90(4):659–74. [Cross Ref]

            83. Clements T, Milner-Gulland EJ. Impact of payments for environmental services and protected areas on local livelihoods and forest conservation in northern Cambodia. Conserv Biol. 2015. Vol. 29(1):78–87. [Cross Ref]

            84. Hegde R, Bull GQ. Performance of an agro-forestry based payments-for-environmental-services project in Mozambique: a household level analysis. Ecol Econ. 2011. Vol. 71(1):122–30. [Cross Ref]

            85. Gubbi S, Linkie M, Leader-Williams N. Evaluating the legacy of an integrated conservation and development project around a tiger reserve in India. Environ Conserv. 2008. Vol. 35(4):331–9. [Cross Ref]

            86. Bedelian C, Ogutu J. Trade-offs for climate-resilient pastoral livelihoods in wildlife conservancies in the Mara ecosystem. Pastoralism. 2017. Vol. 7(1):10[Cross Ref]

            87. Kumar R, Horwitz P, Milton GR, Sellamuttu SS, Buckton ST, Davidson NC, et al.. Assessing wetland ecosystem services and poverty interlinkages: a general framework and case study. Hydrol Sci J. 2011. Vol. 56(8):1602–21. [Cross Ref]

            88. Katikiro RE. Improving alternative livelihood interventions in marine protected areas: a case study in Tanzania. Mar Policy. 2016. Vol. 70:22–9. [Cross Ref]

            89. Chaigneau T, Brown K. Challenging the win-win discourse on conservation and development: analyzing support for marine protected areas. Ecol Soc. 2016. Vol. 21(1):36[Cross Ref]

            90. Sassen M, Sheil D, Giller KE, ter Braak CJF. Complex contexts and dynamic drivers: understanding four decades of forest loss and recovery in an East African protected area. Biol Conserv. 2013. Vol. 159:257–68. [Cross Ref]

            91. Naidu SC. Legal exclusions, private wealth and livelihoods: an analysis of work time allocation in protected areas. Ecol Eco. 2013. Vol. 89:82–91. [Cross Ref]

            92. Marshall NA, Marshall PA, Abdulla A, Rouphael T. The links between resource dependency and attitude of commercial fishers to coral reef conservation in the red sea. Ambio. 2010. Vol. 39(4):305–13. [Cross Ref]

            93. Roe D, Booker F, Day M, Zhou W, Allebone-Webb S, Hill NAO, et al.. Are alternative livelihood projects effective at reducing local threats to specified elements of biodiversity and/or improving or maintaining the conservation status of those elements? Environ Evid. 2015. Vol. 4(22)[Cross Ref]

            94. Stern MJ. Coercion, voluntary compliance and protest: the role of trust and legitimacy in combating local opposition to protected areas. Environ Conserv. 2008. Vol. 35(3):200–10. [Cross Ref]

            95. Roe D, Oviedo G, Pabon L, Painter M, Redford K, Siegele L, et al.. Conservation and Human Rights: the Need for International Standards. London: IIED, London. 2010

            96. Springer J. Addressing the social impacts of conservation: lessons from experience and future directions. Conserv Soc. 2009. Vol. 7(1):26[Cross Ref]

            97. Dickman AJ, Macdonald EA, Macdonald DW. A review of financial instruments to pay for predator conservation and encourage human-carnivore coexistence. Proc Natl Acad Sci USA. 2011. Vol. 108(34):13937–44. [Cross Ref]

            98. IFC. Performance Standards on Environmental and Social Sustainability. Washington, DC: International Finance Corporation. 2012

            99. Bhattacharjee A, Parthasarathy N. Coexisting with large carnivores: a case study from Western Duars, India. Hum Dimens Wildl. 2013. Vol. 18(1):20–31. [Cross Ref]

            100. Ogra M, Badola R. Compensating human-wildlife conflict in protected area communities: Ground-Level perspectives from Uttarakhand, India. Hum Ecol. 2008. Vol. 36(5):717–29. [Cross Ref]

            101. Bidaud C, Schreckenberg K, Rabeharison M, Ranjatson P, Gibbons J, Jones JG. The sweet and the bitter: intertwined positive and negative social impacts of a biodiversity offset. Conserv Soc. 2017. Vol. 15(1):1–13. [Cross Ref]

            102. Vedeld P, Cavanagh C, Petursson J, Nakakaawa C, Moll R, Sjaastad E. The political economy of conservation at mount elgon, Uganda: between local deprivation, regional sustainability, and global public goods. Conserv Soc. 2016. Vol. 14(3):183[Cross Ref]

            103. Martin A, Gross-Camp N, Akol A. Towards an explicit justice framing of the social impacts of conservation. Conserv Soc. 2015. Vol. 13(2):166[Cross Ref]

            104. Desbureaux S, Brimont L. Between economic loss and social identity: the multi-dimensional cost of avoiding deforestation in Eastern Madagascar. Ecol Econ. 2015. Vol. 118:10–20. [Cross Ref]

            105. Lam L, Paul S. Disputed land rights and conservation-led displacement: a double whammy on the poor. Conserv Soc. 2014. Vol. 12(1):65[Cross Ref]

            106. Lam L. Cultural perspectives of land and livelihoods: a case study of Shuklaphanta Wildlife Reserve in far-Western Nepal. Conserv Soc. 2011. Vol. 9(4):311[Cross Ref]

            107. Torri M. Conservation, relocation and the social consequences of conservation policies in protected areas: case study of the Sariska Tiger Reserve, India. Conserv Soc. 2011. Vol. 9(1):54[Cross Ref]

            108. Harihar A, Veríssimo D, MacMillan DC. Beyond compensation: integrating local communities’ livelihood choices in large carnivore conservation. Glob Environ Change. 2015. Vol. 33:122–30. [Cross Ref]

            109. Bayani A, Tiwade D, Dongre A, Dongre AP, Phatak R, Watve M. Assessment of crop damage by protected wild mammalian herbivores on the Western boundary of Tadoba-Andhari Tiger Reserve (TATR), Central India. PLOS One. 2016. Vol. 11(4):e0153854. [Cross Ref]

            110. Seifu M, Beyene F. Local livelihoods and institutions in managing wildlife ecosystems: the case of Babile Elephant Sanctuary in Ethiopia. J Nat Conserv. 2014. Vol. 22(6):559–69. [Cross Ref]

            111. Tumusiime DM, Sjaastad E. Conservation and development: Justice, inequality, and attitudes around Bwindi Impenetrable National Park. J Dev Stud. 2014. Vol. 50(2):204–25. [Cross Ref]

            112. Poudyal M, Ramamonjisoa BS, Hockley N, Rakotonarivo OS, Gibbons JM, Mandimbiniaina R, et al.. Can REDD+ social safeguards reach the “right” people? Lessons from Madagascar. Glob Environ Change. 2016. Vol. 37:31–42. [Cross Ref]

            113. Hall JM, Burgess ND, Rantala S, Vihemaki H, Jambiya G, Gereau RE, et al.. Ecological and social outcomes of a new protected area in Tanzania. Conserv Biol. 2014. Vol. 28(6):1512–21. [Cross Ref]

            114. Ostrom E. Governing the Commons: The Evolution of Institutions for Collective Action. Cambridge: Cambridge University Press. 1990

            115. Berkes F. Sacred Ecology: Traditional Ecological Knowledge and Resource Management. London: Taylor & Francis. 1999

            116. Cooke B, Kothari U. Participation: The New Tyranny? New York: Zed Books. 2002

            117. Coulibaly-Lingani P, Savadogo P, Tigabu M, Oden PC. Factors influencing people’s participation in the forest management program in Burkina Faso, West Africa. For Policy Econ. 2011. Vol. 13(4):292–302. [Cross Ref]

            118. Macura B, Secco L, Pisani E, Pullin AS, Reyes-García V. All that glitters is not gold: the effect of top-down participation on conservation knowledge, attitudes and institutional trust in a Central Indian tiger reserve. Reg Environ Change. 2016. Vol. 16(1):125–40. [Cross Ref]

            119. Musyoki JK, Mugwe J, Mutundu K, Muchiri M. Factors influencing level of participation of community forest associations in management forests in Kenya. J Sustain For. 2016. Vol. 35(3):205–16. [Cross Ref]

            120. Barnes-Mauthe M, Oleson KLL, Brander LM, Zafindrasilivonona B, Oliver TA, van Beukering P. Social capital as an ecosystem service: evidence from a locally managed marine area. Ecosyst Serv. 2015. Vol. 16:283–93. [Cross Ref]

            121. Gross-Camp N. Tanzania’s community forests: their impact on human well-being and persistence in spite of the lack of benefit. Ecol Soc. 2017. Vol. 22(1)[Cross Ref]

            122. Himberg N, Omoro L, Pellikka P, Luukkanen O. The benefits and constraints of participation in forest management. The case of Taita Hills, Kenya. Fennia - Int J Geogr. 2009. Vol. 187(1):61–76. https://fennia.journal.fi/article/view/3704

            123. Gustavsson M, Lindström L, Jiddawi NS, de la Torre-Castro M. Procedural and distributive justice in a community-based managed Marine Protected Area in Zanzibar, Tanzania. Marine Policy. 2014. Vol. 46:91–100. [Cross Ref]

            124. Khadka D, Nepal SK. Local responses to participatory conservation in Annapurna Conservation Area, Nepal. Environ Manage. 2010. Vol. 45(2):351–62. [Cross Ref]

            125. Tran L, Walter P. Ecotourism, gender and development in northern Vietnam. Ann Tour Res. 2014. Vol. 44(1):116–30. [Cross Ref]

            126. Mazunda J, Shively G. Measuring the forest and income impacts of forest user group participation under Malawi’s Forest Co-management Program. Ecol Econ. 2015. Vol. 119:262–73. [Cross Ref]

            127. Cinner JE, McClanahan TR. A sea change on the African coast? Preliminary social and ecological outcomes of a governance transformation in Kenyan fisheries. Glob Environ Change. 2015. Vol. 30:133–9. [Cross Ref]

            128. Freed S, Dujon V, Granek EF, Mouhhidine J. Enhancing small-scale fisheries management through community engagement and multi-community partnerships: Comoros case study. Marine Policy. 2016. Vol. 63:81–91. [Cross Ref]

            129. Noe C, Kangalawe RM. Wildlife protection, community participation in conservation, and (dis) empowerment in Southern Tanzania. Conserv Soc. 2015. Vol. 13(3):244[Cross Ref]

            130. Katikiro RE, Macusi ED, Ashoka Deepananda KHM. Challenges facing local communities in Tanzania in realising locally-managed marine areas. Marine Policy. 2015. Vol. 51:220–9. [Cross Ref]

            131. Brechin SR, Wilshusen PR, Fortwangler L, West PC. Beyond the square wheel: toward a more comprehensive understanding of biodiversity conservation as social and political process. Soc Nat Resour. 2002. Vol. 15:41–64

            132. Wright VC. Turbulent terrains: the contradictions and politics of decentralised conservation. Conserv Soc. 2017. Vol. 15(2):157[Cross Ref]

            133. Gurney GG, Cinner JE, Sartin J, Pressey RL, Ban NC, Marshall NA, et al.. Participation in devolved commons management: multiscale socioeconomic factors related to individuals’ participation in community-based management of marine protected areas in Indonesia. Environ Sci Policy. 2016. Vol. 61:212–20. [Cross Ref]

            134. Steenbergen DJ. Strategic customary village leadership in the context of marine conservation and development in Southeast Maluku, Indonesia. Hum Ecol. 2016. Vol. 44(3):311–27. [Cross Ref]

            135. Larson AM, Springer J. Recognition and Respect for Tenure Rights (NRGF Conceptual Paper). Gland, Switzerland: IUCN, CEESP and CIFOR. 2016

            136. Schlager E, Ostrom E. Property-rights regimes and natural resources: a conceptual analysis. Land Econ. 1992. Vol. 68(3):249–62. [Cross Ref]

            137. FAO. Voluntary guidelines of the responsible governance of tenure of land, fisheries and forests in the context of natural food security. Rome, Italy: Food and Agriculture Organization of the United Nations. 2012

            138. Garnett ST, Burgess ND, Fa JE, Fernández-Llamazares Á, Molnár Z, Robinson CJ, et al.. A spatial overview of the global importance of Indigenous lands for conservation. Nat Sustain. 2018. Vol. 1:369–74. [Cross Ref]

            139. Sunderlin WD, Larson AM, Duchelle AE, Resosudarmo IAP, Huynh TB, Awono A, et al.. How are REDD+ proponents addressing tenure problems? Evidence from Brazil, Cameroon, Tanzania, Indonesia, and Vietnam. World Dev. 2014. Vol. 55:37–52. [Cross Ref]

            140. Land Portal. Land and the Sustainable Development Goals (SDGs). 2019 Accessed 30 November 2020 https://landportal.org/book/sdgs

            141. Brännlund R, Sidibe A, Gong P. Participation to forest conservation in National Kabore Tambi Park in Southern Burkina Faso. For Policy Econ. 2009. Vol. 11(7):468–74. [Cross Ref]

            142. Hyakumura K. “Slippage” in the implementation of forest policy by local officials: a case study of a protected area management in Lao PDR. Small-Scale Forestry. 2010. Vol. 9(3):349–67. [Cross Ref]

            143. Roy AKD, Alam K, Gow J. Community perceptions of state forest ownership and management: a case study of the Sundarbans Mangrove Forest in Bangladesh. J Environ Manage. 2013. Vol. 117:141–9. [Cross Ref]

            144. Yami M, Mekuria W, Hauser M. The effectiveness of village bylaws in sustainable management of community-managed exclosures in Northern Ethiopia. Sustain Sci. 2013. Vol. 8(1):73–86. [Cross Ref]

            145. Rahman HMT, Sarker SK, Hickey GM, Mohasinul Haque M, Das N. Informal institutional responses to government interventions: lessons from Madhupur National Park, Bangladesh. Environ Manage. 2014. Vol. 54(5):1175–89. [Cross Ref]

            146. Awung N, Marchant R. Investigating the role of the local community as co-managers of the Mount Cameroon National Park Conservation Project. Environments. 2016. Vol. 3(4):36. [Cross Ref]

            147. Phuc TX. Why did the forest conservation policy fail in the Vietnamese uplands? Forest conflicts in Ba Vi National Park in Northern Region. Int J Environ Stud. 2009. Vol. 66(1):59–68. [Cross Ref]

            148. Awono A, Somorin OA, Eba’a Atyi R, Levang P. Tenure and participation in local REDD+ projects: insights from southern Cameroon. Environ Sci Policy. 2014. Vol. 35:76–86. [Cross Ref]

            149. Scheba A, Rakotonarivo OS. Territorialising REDD+: conflicts over market-based forest conservation in Lindi, Tanzania. Land Use Policy. 2016. Vol. 57:625–37. [Cross Ref]

            150. Atela JO, Quinn CH, Minang PA, Duguma LA. Implementing REDD+ in view of integrated conservation and development projects: leveraging empirical lessons. Land Use Policy. 2015. Vol. 48:329–40. [Cross Ref]

            151. Clements T, Suon S, Wilkie DS, Milner-Gulland EJ. Impacts of protected areas on local livelihoods in Cambodia. World Dev. 2014. Vol. 64:S125–34. [Cross Ref]

            152. Sinu PA, Kent SM, Chandrashekara K. Forest resource use and perception of farmers on conservation of a usufruct forest (Soppinabetta) of Western Ghats, India. Land Use Policy. 2012. Vol. 29(3):702–9. [Cross Ref]

            153. Sikor T, He J, Lestrelin G. Property rights regimes and natural resources: a conceptual analysis revisited. World Dev. 2017. Vol. 93:337–49. [Cross Ref]

            154. Davis A. ‘Ha! What is the benefit of living next to the park?’ Factors limiting in-migration next to Tarangire National Park, Tanzania. Conserv Soc. 2011. Vol. 9(1):25[Cross Ref]

            155. Nagendra H, Gokhale Y. Management regimes, property rights, and forest biodiversity in Nepal and India. Environ Manage. 2008. Vol. 41(5):719–33. [Cross Ref]

            156. Chomba S, Treue T, Sinclair F. The political economy of forest entitlements: can community based forest management reduce vulnerability at the forest margin? For Policy Econ. 2015. Vol. 58:37–46. [Cross Ref]

            157. Gbedomon RC, Floquet A, Mongbo R, Salako VK, Fandohan AB, Assogbadjo AE, et al.. Socio-economic and ecological outcomes of community based forest management: a case study from Tobé-Kpobidon forest in Benin, Western Africa. For Policy Econ. 2016. Vol. 64:46–55. [Cross Ref]

            158. Büscher B, Fletcher R. Towards convivial conservation. Conserv Soc. 2019. Vol. 17(3):283[Cross Ref]

            159. Martin A. Just Conservation: Biodiversity, Wellbeing and Sustainability. London: Taylor & Francis. 2017

            160. Brockington D. Community conservation, inequality and injustice: myths of power in protected area management. Conserv Soc. 2004. Vol. 2(2):411–32

            161. Adams W, Hulme D. If community conservation is the answer in Africa, what is the question? Oryx. 2001. Vol. 35(3):193–200. [Cross Ref]

            162. Persha L, Agrawal A, Chhatre A. Social and ecological synergy: local rulemaking, forest livelihoods, and biodiversity conservation. Science. 2011. Vol. 331(6024):1606–8. [Cross Ref]

            163. Andrade GSM, Rhodes JR. Protected areas and local communities: an inevitable partnership toward successful conservation strategies? Ecol Soc. 2012. Vol. 17(4):14[Cross Ref]

            164. Porter-Bolland L, Ellis EA, Guariguata MR, Ruiz-Mallén I, Negrete-Yankelevich S, Reyes-García V. Community managed forests and forest protected areas: an assessment of their conservation effectiveness across the tropics. For Ecol Manage. 2012. Vol. 268:6–17. [Cross Ref]

            165. Dawson NM, Coolsaet B, Sterling EJ, Loveridge R, Gross-Camp ND, Wongbusarakum S, et al.. The role of Indigenous peoples and local communities in effective and equitable conservation. Ecol Soc. 2021. Vol. 26(3):19. [Cross Ref]

            166. Morgera E. Under the radar: fair and equitable benefit-sharing and the human rights of indigenous peoples and local communities connected to natural resources. Int J Hum Rights. 2019. Vol. 23:1098–139

            167. Borrini-Feyerabend G, Jaeger T, Lassen B, Pathak Broome N, Phillips A, Sandwith T. Governance of Protected Areas: From Understanding to Action. Best Practice Protected Area Guidelines Series No. 20. Gland, Switzerland: IUCN. 2013

            168. Zafra-Calvo N, Garmendia E, Pascual U, Palomo I, Gross-Camp N, Brockington D, et al.. Progress toward equitably managed protected areas in Aichi target 11: a global survey. BioScience. 2019. Vol. 69(3):191–7

            169. Zafra-Calvo N, Balvanera P, Pascual U, Merçon J, Martín-López B, van Noordwijk M, et al.. Plural valuation of nature for equity and sustainability: insights from the Global South. Glob Environ Change. 2020. Vol. 63:102115. [Cross Ref]

            170. Booker F, Franks P. Governance Assessment for Protected and Conserved Areas (GAPA): Methodology manual for GAPA facilitators. London: IIED. 2019 Accessed 30 November 2020 https://pubs.iied.org/pdfs/17655IIED.pdf

            171. Díaz S, Demissew S, Carabias J, Joly C, Lonsdale M, Ash N, et al.. The IPBES conceptual framework – connecting nature and people. Curr Opin Environ Sust. 2015. Vol. 14:1–16. [Cross Ref]

            172. Agawal B. Environmental action, gender equity and women’s participation. Dev Change. 1997. Vol. 28:1–44. [Cross Ref]

            173. Keane A, Gurd H, Kaelo D, Said MY, de Leeuw J, Rowcliffe JM, et al.. Gender differentiated preferences for a community-based conservation initiative. PLoS ONE. 2016. Vol. 11(3):e0152432. [Cross Ref]

            174. Biedenweg K, Gross-Camp ND. A brave new world: integrating well-being and conservation. Ecol Soc. 2018. Vol. 23(2):32. [Cross Ref]

            175. Bennett NJ. Using perceptions as evidence to improve conservation and environmental management. Conserv Biol. 2016. Vol. 30(3):582–92. [Cross Ref]

            176. Blundo-Canto G, Bax V, Quintero M, Cruz-Garcia GS, Groeneveld RA, Perez-Marulanda L. The different dimensions of livelihood impacts of payments for environmental services (PES) schemes: a systematic review. Ecol Econ. 2018. Vol. 149:160–83. [Cross Ref]

            177. Antkowiak T. A dark side of virtue: the Inter-American court and reparations for Indigenous Peoples. Duke J Comp Int Law. 2014. Vol. 25:1–80

            178. Woodhouse E, Bedelian C, Dawson N, Barnes P. Social impacts of protected areas: exploring evidence of trade-offs and synergiesSchreckenberg K, Mace G, Poudyal M. Ecosystem Services and Poverty Alleviation: Trade-Offs and Governance. London: Routledge. 2018. p. 243–56. [Cross Ref]

            179. Galafassi D, Daw TM, Munyi L, Brown K, Barnaud C, Fazey I. Learning about social-ecological trade-offs. Ecol Soc. 2017. Vol. 22(1):2[Cross Ref]

            180. McShane TO, Hirsch PD, Trung TC, Songorwa AN, Kinzig A, Monteferri B, et al.. Hard choices: making trade-offs between biodiversity conservation and human well-being. Biol Conserv. 2011. Vol. 144(3):966–72. [Cross Ref]

            181. McCarter J, Sterling EJ, Jupiter SD, Cullman GD, Albert S, Basi M, et al.. Biocultural approaches to developing well-being indicators in Solomon Islands. Ecol Soc. 2018. Vol. 23(1):32. [Cross Ref]

            182. Lenzen M, Moran D, Kanemoto K, Foran B, Lobefaro L, Geschke A. International trade drives biodiversity threats in developing nations. Nature. 2012. Vol. 486(7401):109–12. [Cross Ref]

            183. Perfecto I, Vandermeer J. Breakfast of Biodiversity: The Political Ecology of Rainforest Destruction. Oakland, CA: Food First Books. 2005

            184. Duffy R, St John FAV, Büscher B, Brockington D. Toward a new understanding of the links between poverty and illegal wildlife hunting. Conserv Biol. 2016. Vol. 30(1):14–22. [Cross Ref]

            185. Dinerstein E, Vynne C, Sala E, Joshi AR, Fernando S, Lovejoy TE, et al.. A global deal for nature: guiding principles, milestones, and targets. Sci Adv. 2019. Vol. 5:eaaw2869. [Cross Ref]

            186. Waldron A, Adams V, Allan J, Arnell A, Asner G, Atkinson S, et al.. Protecting 30% of the Planet for Nature: Costs, Benefits and Economic Implications: Working paper Analysing the Economic Implications of the Proposed 30% Target for Areal Protection in the Draft Post-2020 Global Biodiversity Framework. 2020 Accessed 30 November 2020 https://www.conservation.cam.ac.uk/files/waldron_report_30_by_30_publish.pdf

            Supporting information

            Conservation organisations

            Evidence for narratives on conservation organisation websites (January 2018)

            *Organisation operates internationally outside of Africa.

              Strongly evident  
              Weakly evident

            A Rocha*
            Africa Conservation Fund UK
            African Conservation Centre
            African Ele-Fund
            African Fund for Endangered Wildlife
            African Mangrove Network (AMN)
            African Parks Foundation
            African Wildlife Foundation
            Amara Conservation
            Ambassadors for Wildlife through Education (AWE)
            Amboseli Community Wildlife Tourism Project (ACWTP)
            Amboseli Trust for Elephants
            Ape Action Africa
            Arboretum D’Antsokay
            ARCOS – Albertine Rift Conservation Society
            Association ‘Les Amis des Oiseaux’ (AAO)
            Association pour la Conservation de la Nature au Rwanda
            Biodiversity Foundation for Africa (BFA)
            BirdLife Botswana (BLB)
            Birdlife International (Secretariat)*
            BirdLife Zimbabwe (BLZ)
            Bonobo Conservation Initiative (BCI)
            Born Free Foundation*
            Bushmeat Project
            Cameroon Environmental Watch
            Cheetah Conservation Botswana
            Cheetah Conservation Fund
            Chobe Wildlife Trust
            Conservation International*
            Conservation Society of Sierra Leone (CSSL)
            Conservation South Luangwa
            Conservation through Poverty Alleviation
            Conserve Africa
            David Sheldrick Wildlife Trust
            David Shepherd Wildlife Foundation*
            Dian Fossey Gorilla Fund International
            Durrell Wildlife Conservation Trust*
            Earthwatch Institute*
            East African Wild Life Society
            Elephant Pepper Development Trust
            Elephant Voices
            Endangered Wildlife Trust (EWT)
            Environmental Foundation for Africa, Sierra Leone
            Ethiopian Wolf Conservation Programme
            Fauna and Flora International*
            Fondation Pour les Aires Protegées at la Biodiversite de Madagascar
            Fondation Tany Meva
            Frankfurt Zoological Society*
            Friedkin Conservation Fund
            Friends of Conservation (UK)
            Friends of Conservation (USA)
            Friends of Elephant/Vrienden van de Olifant
            Friends of the Hippo and The Turgwe Hippo Trust
            Gallmann Memorial Foundation (GMF)
            George Adamson Wildlife Preservation Trust
            Ghana Wildlife Society (GWS)
            GORILLA Association
            Gorilla Organization
            Grassland Society of Southern Africa
            H.E.L.P. Congo
            Humane Society International*
            Hurghada Environmental Protection & Conservation Association
            International Elephant Foundation*
            International Rhino Foundation (IRF)*
            Jane Goodall Institute
            Kasanka Trust
            Kenya Wildlife Trust
            Kilimanjaro Environmental Conservation Management Trust Fund
            Kipepeo Butterfly Project
            Laikipia Wildlife Forum
            Last Great Ape Organization
            Lewa Wildlife Conservancy
            Lion Conservation Fund
            Living with Lions
            Lukuru Wildlife Research Project (LWRP)
            Maasai Foundation of East Africa
            Madagascar Fauna Group
            Madagascar Wildlife Conservation
            Man And the Environment (MATE)
            Mokolodi Wildlife Foundation
            Mount Kenya Wildlife Conservancy
            Mpala Wildlife Foundation
            Nature Djibouti
            Nature Kenya: The East Africa Natural History Society
            Nature Seychelles
            NatureUganda (NU)
            Nigerian Conservation Foundation (NCF)
            Nigerian Montane Forests Project
            Noé Conservation
            Northern Rangelands Trust
            Nouvelles Approches (now Biodiversité au Katanga)
            Organização para a Defesa eDesenvolvimento das Zonas Húmidas
            Owens Foundation for Wildlife Conservation
            Painted Dog Conservation Trust
            Pan African Sanctuary Alliance (PASA)
            Partners in Conservation
            Peace Parks Foundation
            Peregrine Fund*
            Predator Conservation Trust
            Project Primate
            Rainforest Action Network (RAN)*
            Rainforest Foundation*
            Rare Species Conservatory Foundation*
            Rhino Ark
            Robin Hurt Wildlife Foundation
            RSPB International*
            Safari Club International Foundation*
            Sahara Conservation Fund
            Save My Future Foundation (SAMFU)
            Save The Elephants (STE)*
            Save the Rhino International*
            Save the Rhino Trust
            Save the Species Worldwide Foundation*
            Sebakwe Black Rhino Trust
            SEED Madagascar
            Somali Environmental Protection and Anti-Desertification Organisation
            Southern African Wildlife College
            Space for Elephants
            System of Protected Areas of Madagascar (SPAM)
            Tandroy Conservation Trust
            Tanzania Forest Conservation Group
            Tanzania Natural Resources Forum
            The Colobus Trust
            The International Crane Foundation*
            The Kesho Trust
            The Rainforest Foundation Fund Inc (Norway)
            The Wasmoeth Wildlife Foundation
            Trees for the Future
            TUSK Trust
            Uganda Conservation Foundation
            West African Primate Conservation Action (WAPCA)
            West African Bird Studies Association (WABSA)
            West Lunga Trust
            Westerveld Conservation Trust
            Wetlands International*
            Wild Chimpanzee Foundation
            WILD Foundation*
            Wilderness Trust of Southern Africa
            Wildlife Action Group Malawi
            Wildlife and Environment Society of Malawi
            Wildlife Conservation Foundation of Tanzania
            Wildlife Conservation Society (WCS)*
            Wildlife Conservation Society of Tanzania (WCST)
            Wildlife Direct
            Wildlife Now
            Wildlife Warriors Worldwide*
            William Holden Wildlife Foundation
            World Parrot Trust*
            World Resources Institute*
            World Turtle Trust*
            WWF (International)*
            WWF UK
            WWF US
            Zambezi Society
            Zimbabwe Conservation Task Force
            Zoological Society for the Conservation of Species and Populations
            Zoological Society of Milwaukee
            Interview validation

            World Bank Economies

            (March 2017)

            CountryWorld Bank Economic categoryRegion (United Nations geoscheme)
            AfghanistanLow incomeAsia
            ArmeniaLower middle incomeAsia
            BangladeshLower middle incomeAsia
            BeninLow incomeAfrica
            BhutanLower middle incomeAsia
            BoliviaLower middle incomeAmericas
            Burkina FasoLow incomeAfrica
            BurundiLow incomeAfrica
            Cabo VerdeLower middle incomeAfrica
            CambodiaLower middle incomeAsia
            CameroonLower middle incomeAfrica
            Central African RepublicLow incomeAfrica
            ChadLow incomeAfrica
            ComorosLow incomeAfrica
            Congo, Dem. Rep.Low incomeAfrica
            Congo, Rep.Lower middle incomeAfrica
            Côte d'IvoireLower middle incomeAfrica
            DjiboutiLower middle incomeAfrica
            Egypt, Arab Rep.Lower middle incomeAfrica
            El SalvadorLower middle incomeAmericas
            EritreaLow incomeAfrica
            EthiopiaLow incomeAfrica
            Gambia, TheLow incomeAfrica
            GhanaLower middle incomeAfrica
            GuatemalaLower middle incomeAmericas
            GuineaLow incomeAfrica
            Guinea-BissauLow incomeAfrica
            HaitiLow incomeAmericas
            HondurasLower middle incomeAmericas
            IndiaLower middle incomeAsia
            IndonesiaLower middle incomeAsia
            KenyaLower middle incomeAfrica
            KiribatiLower middle incomeOceania
            Korea, Dem. People's Rep.Low incomeAsia
            KosovoLower middle incomeEurope
            Kyrgyz RepublicLower middle incomeAsia
            Lao PDRLower middle incomeAsia
            LesothoLower middle incomeAfrica
            LiberiaLow incomeAfrica
            MadagascarLow incomeAfrica
            MalawiLow incomeAfrica
            MaliLow incomeAfrica
            MauritaniaLower middle incomeAfrica
            Micronesia, Fed. Sts.Lower middle incomeOceania
            MoldovaLower middle incomeEurope
            MongoliaLower middle incomeAsia
            MoroccoLower middle incomeAfrica
            MozambiqueLow incomeAfrica
            MyanmarLower middle incomeAsia
            NepalLow incomeAsia
            NicaraguaLower middle incomeAmericas
            NigerLow incomeAfrica
            NigeriaLower middle incomeAfrica
            PakistanLower middle incomeAsia
            Papua New GuineaLower middle incomeOceania
            PhilippinesLower middle incomeAsia
            RwandaLow incomeAfrica
            SamoaLower middle incomeOceania
            São Tomé and PrincipeLower middle incomeAfrica
            SenegalLow incomeAfrica
            Sierra LeoneLow incomeAfrica
            Solomon IslandsLower middle incomeOceania
            SomaliaLow incomeAfrica
            South SudanLow incomeAfrica
            Sri LankaLower middle incomeAsia
            SudanLower middle incomeAfrica
            SwazilandLower middle incomeAfrica
            Syrian Arab RepublicLower middle incomeAsia
            TajikistanLower middle incomeAsia
            TanzaniaLow incomeAfrica
            Timor-LesteLower middle incomeAsia
            TogoLow incomeAfrica
            TongaLower middle incomeOceania
            TunisiaLower middle incomeAfrica
            UgandaLow incomeAfrica
            UkraineLower middle incomeEurope
            UzbekistanLower middle incomeAsia
            VanuatuLower middle incomeOceania
            VietnamLower middle incomeAsia
            West Bank and GazaLower middle incomeAsia
            Yemen, Rep.Lower middle incomeAsia
            ZambiaLower middle incomeAfrica
            ZimbabweLow incomeAfrica
            Exclusion Criteria

            Exclude on date: The study has a publication date before 2014.

            Exclude on country: The study is outside of the list of included countries for the IMPACTS project, which focuses on low- and lower middle-income countries only (according to the World Bank).

            Exclude on population: The subjects of the intervention are not discrete individuals, households, communities or national states.

            Exclude on intervention: The study does not include the establishment or management of an area-based protected or conserved area intervention or associated policy or programme.

            Exclude on outcome: The study does not observe, measure or describe human wellbeing indicators, outcomes, or impacts. The study only focuses on biophysical outcomes of conservation or solely examines how status or trends in human wellbeing affect conservation outcomes.

            Exclude on study type: The study is a theoretical or conceptual article, modelling study, commentary, editorial or narrative review.

            Search Terms

            Protected area intervention terms

            protected area* OR nature reserve* OR wilderness area* OR national park* OR natural monument* OR natural feature* OR management area* OR world heritage site* OR biosphere reserve* OR biodiversity conservation OR national reserve* OR conservanc* OR ecotourism OR corridor* OR community-based conservation OR payment for ecosystem services OR PES AND

            Intervention adjacent terms

            marine OR freshwater OR coastal OR forest* OR ecosystem* OR species OR habitat* OR biodiversity OR sustainab* OR ecolog* OR integrated OR landscape OR seascape OR coral reef* OR natural resource* AND

            Outcome terms

            wellbeing OR well-being OR well being OR ecosystem service* OR nutrition OR skill* OR empower* OR clean water OR livelihood* OR (food) security OR resilience* OR vulnerability OR (social) capital OR attitude* OR perception* OR (human) health* OR human capital OR (traditional knowledge or TEK) AND

            Outcome adjacent terms

            human* OR people OR person* OR community* OR household* OR fisher* OR collaborative


            Bibliographic info Author/s
            Type of BiomeTerrestrial, marine
            Affiliations of authorsAcademic, independent (no affiliation), PA management, public sector, private sector, research institute
            Protected area (PA) Name of PA
            IUCN Protected Area CategoryIa strict nature reserve; Ib wilderness area; II national park; III natural monument/feature; IV habitat/species management area; V protected landscape/seascape; VI protected area with sustainable use; buffer/transition zone; biosphere reserve; ICCA (not covered by IUCN); private (not covered by IUCN); other – specify, e.g., de facto, voluntary conservation; not reported
            Governance type/implementergovernment, shared (diverse stakeholders), private, indigenous or local communities, not specified
            Country of PA
            Year established (if stated)
            Study info Year of study (if stated)
            Data sourcePrimary, secondary
            Unit of analysisindividual, household, village, country
            Data typeQuantitative, qualitative, mixed
            Includes subjective measuresY/N
            Outcomes reported onSocial, social and environmental
            Evidence of processOutcomes reported only, process and outcomes reported, other
            Aspect of PA studiedestablishment (presence/absence), management activities, governance processes, indirect (e.g., tourism or PES)
            Outcomes Social outcome/s reportedincome, other material (food, assets, livelihoods, access to services), health, security, social relations/conflict, agency/empowerment/participation, cultural values/practices, subjective (overall, e.g., how's life? or satisfaction with specific aspects of wellbeing)
            Details of main outcomes covered
            Wellbeing explicitly mentionedY/N
            Equity/distributional aspects of outcomes [differential outcomes reported]Y/N
            Equity/distributional aspects of outcomes [equity explicitly mentioned]Y/N
            Environmental outcomes or behaviours included [environmental outcomes (e.g., biodiversity)]Y/N
            Environmental outcomes or behaviours included [Environmental behaviours (e.g., fishing, hunting)]Y/N
            Environmental outcomes linked to social outcomes or processesY/N
            ES specifiedNone, supporting, provisioning, regulation, cultural
            Positive or negative social impactsPositive, negative, mixed, not explicit
            Narratives 1. Conservation is pro-poor [link to narrative]Yes, no, partially
            1. Conservation is pro-poor [supportive of narrative]Yes, no, partially
            1. Pro-poor narrative notes
            2. Poverty reduction benefits conservation narrative [link to narrative]Yes, no, partially
            2. Poverty reduction benefits conservation narrative [supportive of narrative]Yes, no, partially
            2. Poverty reduction narrative notes
            3. Compensation neutralises conservation costs [link to narrative]Yes, no, partially
            3. Compensation neutralises conservation costs [supportive of narrative]Yes, no, partially
            3. Compensation narrative notes
            4. Participation is good for conservation [link to narrative]Yes, no, partially
            4. Participation is good for conservation [supportive of narrative]Yes, no, partially
            4. Participation narrative notes
            5. Resource tenure underpins long-term conservation [link to narrative]Yes, no, partially
            5. Resource tenure underpins long-term conservation [supportive of narrative]
            Non-academic interviewees

            Type of organisationBased inRegion/country specialism
            Conservation membership organisationKenyaKenya
            Country office of international conservation NGOLaosLao
            Country office of international conservation NGONepalNepal
            Country office of international conservation NGOPakistanPakistan
            Government conservation agencyUgandaUganda
            Government research instituteKenyaKenya
            Grassroots development NGOKenyaKenya
            In-country conservation NGOMadagascarMadagascar
            In-country conservation NGOBrazilBrazil
            Intergovernmental organisationItalyOceania
            International conservation NGOUSACentral Africa, Latin America and Asia
            International conservation NGOUSANepal, East and Southern Africa
            International conservation NGOUSAColombia, Peru, Madagascar
            International conservation policy organisationUKAfrica
            International development organisationNetherlandsLatin America
            NGO focused on indigenous rightsacross AfricaSouth Africa
            Research organisation on environment and developmentUKEast Africa, West Africa
            Interview Questions

            Please consider the following context and the widespread assumptions that follow. We would then like to ask about your experience, and your opinion on those assumptions, through a set of structured questions.

            STUDY CONTEXT

            • We are interested in understanding the processes involved in positive and negative social impacts of PAs on human wellbeing, how impacts may differ between groups, for example, according to gender and age, and how relationships between social and environmental outcomes may vary with context such as with governance type, economic and social factors.

            • We are interested in impacts on multi-dimensional human wellbeing and equity. Therefore, please consider the following aspects:

              • Material wellbeing including assets, income, food, livelihoods and subsistence activities

              • Health

              • Security – confidence in the future

              • Social relations, for example, within the community and between communities and PA authorities

              • Agency, empowerment and participation

              • Recognition of and impacts on cultural values and practices

              • Subjective wellbeing – how people feel about change

            • By ‘protected areas’, we mean all kinds of protected and conserved areas in marine and terrestrial habitats. This includes the six IUCN Protected Area management categories, plus other effective area-based conservation measures, such as other types of indigenous, community and privately conserved areas; and areas that provide connectivity between designated protected areas. We are interested in the establishment, management processes and activities associated with these areas.

            • Our focus is on PAs and communities in low- and lower middle-income countries (according to the World Bank), the countries that are the target of ESPA work.

            We are structuring the analysis by investigating five key narratives in the data, which we have identified as underlying PA establishment and management actions. We are interested in whether these assumptions hold in real-life situations.


            1. Ecosystem services narrative

            Because poor people are disproportionately dependent on ecosystem services, protected areas that target those services will be pro-poor

            This narrative sees PAs as a tool to reduce poverty. It is often the poorest people who are most dependent on ecosystems for their livelihoods and food security. By protecting these ES, PAs are thus important for delivering poverty reduction objectives by supporting a range of economic activities such as forestry, fisheries, agriculture and tourism as well as providing access to clean water and energy.

            2. Poverty and conservation narrative

            Because poor people are disproportionately dependent on ecosystem services, improving their material wellbeing will reduce pressure on protected areas

            This narrative sees poverty reduction as a means to achieve PA conservation. This can occur through strategies such as alternative livelihoods, revenue sharing, investment in infrastructure and tourism, which are implemented to reduce reliance on natural resources and behaviours that might be environmentally damaging. The economic benefits generated by these strategies also increase local support for conservation. Incentive schemes such as PES that provide benefits to poor people are directly linked to PA conservation objectives, thus enhancing conservation success.

            3. Compensation narrative

            Unavoidable social costs of protected areas for poor people can be neutralised by providing appropriate compensation

            Because poor people endure the costs of PAs, such as due to human–wildlife conflict (crop-raiding, livestock predation) or reduced access to PA resources for food, fuel or livelihoods, compensation schemes offset these costs and create more positive attitudes towards PAs.

            4. Participation narrative

            Participation in protected area governance is seen by communities as a positive social benefit and it is a route to effective conservation

            This narrative sees participation of local people in PA decision-making and recognition of their values and interests as important factors contributing to long-term conservation success. Participation is valued by communities and increases the legitimacy of the PA and its policies. Participation increases communities’ sense of stewardship over PAs, builds capacity and creates greater incentives to harvest resources sustainably to ensure future access to benefits.

            5. Secure tenure narrative

            Secure land and resource tenure underpins improved conservation outcomes (social and ecological) in and around protected areas

            This assumes that tenure insecurity is the cause of resource degradation. Secure land rights enable poor people to invest in resources and strategies that promote resilient livelihoods. It is also the foundation for the sustainable use of resources that supports long-term conservation outcomes.

            We would like to ask you the following questions, and for you to share your thoughts based on your own experiences through your work on ESPA projects or other similar projects or research.


            1. From your ESPA project/other professional experience, can you give examples of a) positive and b) negative social impacts of PAs on the wellbeing of local people? Can you explain why these might have occurred? Where they have been negative? What has been done to reduce them?

            2. From your own experience, what are the synergies you’ve found in PA conservation (i.e., different outcomes interact to improve the overall outcome) a) between social and ecological outcomes, and b) between different social outcomes? Can you give examples of each from your work?

            3. What do you see as some of the critical trade-offs in protected area conservation, a) between social and ecological outcomes, and b) between different social outcomes? Can you give examples of each from your work? Are there difficult decisions that you’ve had to make, or you have seen others make, in regard to these trade-offs, and how they have been resolved?

            Protected area narratives

            For each of the narratives above can you/answer the following:

            1. Is this assumption familiar to you? (circle as appropriate)

            2. Where have you come across the idea?

            3. Do you think the assumption has changed through time? How?

            4. From your experience do you agree that the assumption is valid? (circle as appropriate)

            5. If at all valid, can you provide examples? Where? In what kinds of PA? For whom?

            6. If you do not think it is completely valid in what ways or in which contexts do you think it is not valid? Where and for whom? Please refer to specific examples such as case studies or papers.

            7. Do you have an additional narrative or idea that you think guides PA management?

            Author and article information

            UCL Open Environ
            UCL Open Environment
            UCL Open Environ
            UCL Press (UK )
            16 November 2022
            : 4
            [1 ]Department of Anthropology, University College London, London, UK
            [2 ]International Institute for Environment and Development, London, UK
            [3 ]EDGE of Existence Programme, Zoological Society London, London, NW1 4RY, UK
            [4 ]Sowing Diversity = Harvesting Security, Oxfam Novib, The Hague, The Netherlands
            [5 ]School of International Development, University of East Anglia, Norwich, UK
            [6 ]Commission on Environmental, Economic and Social Policy, International Union for the Conservation of Nature, Gland, Switzerland
            [7 ]Boston College, Morrissey College of the Arts & Sciences, Environmental Studies Program, Chestnut Hill, MA, USA
            [8 ]College of Environmental Sciences and Engineering, Bangor University, Bangor, UK
            [9 ]Law School, University of Strathclyde, Glasgow, UK
            [10 ]Geography Department, King’s College London, London, UK
            Author notes
            *Corresponding author: E-mail: e.woodhouse@ 123456ucl.ac.uk
            © 2022 The Authors.

            This is an open access article distributed under the terms of the Creative Commons Attribution Licence (CC BY) 4.0, which permits unrestricted use, distribution and reproduction in any medium, provided the original author and source are credited.

            Research Article

            poverty,development,conservation,ecosystem services,governance,equity,social justice wellbeing,protected areas


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