Improving the role of global conservation treaties in addressing contemporary threats to lions

Improving the role of global conservation treaties in addressing contemporary threats to lions Biodivers Conserv (2018) 27:2747–2765 https://doi.org/10.1007/s10531-018-1567-1 ORIGINAL PAPER Improving the role of global conservation treaties in addressing contemporary threats to lions 1 2 1 1 Timothy Hodgetts  · Melissa Lewis  · Hans Bauer  · Dawn Burnham  · 1 1 1 2 Amy Dickman  · Ewan Macdonald  · David Macdonald  · Arie Trouwborst Received: 3 January 2018 / Revised: 17 March 2018 / Accepted: 23 May 2018 / Published online: 2 June 2018 © The Author(s) 2018 Abstract Despite their iconic status, lion (Panthera leo) populations continue to decline across the majority of their range. In the light of the recent decision (in October 2017) to add lions to the Appendices of the Convention on Migratory Species (CMS), this paper identifies the new and existing legal protections afforded to lions through five global trea - ties, and maps these protections against the most critical contemporary threats facing the species. It thus offers a new analysis of the CMS listing, and draws on existing legal reviews, to highlight the ways in which global treaties offer differing forms of protection for lions. It then combines multiple concordant assessments of lion populations, to highlight nine categories of threat: human-lion conflict, bushmeat poaching, human encroachment, trophy hunting, trade in lion bones, unpredictable environmental events, socio-economic factors, policy failures, and governance/institutional weakness. The paper assesses how the various treaties each address these different categories of threat. The analysis identifies two pathways for improving legal protection: expanding the application of global treaties in respect of lions and their habitats (the paper considers the CMS listing in these terms), and improving the implementation of treaty commitments through local and national-scale actions. Furthermore, it identifies local implementation challenges that include the local knowledge of rules, compliance with rules and enforcement capacity, alongside the variety in local contexts and situations, and suggests where global treaties might provide support in meeting these challenges. We suggest that this analysis has wider implications for how treaty protection can and is utilised to protect various species of large-bodied, wide-rang- ing animals. Communicated by David Hawksworth. This article belongs to the Topical Collection: Biodiversity legal instruments and regulations. * Timothy Hodgetts timothy.hodgetts@zoo.ox.ac.uk Wildlife Conservation Research Unit (Panthera et al.), University of Oxford, Tubney, UK Department of European and International Public Law, Tilburg University, Tilburg, The Netherlands 1 3 2748 Biodivers Conserv (2018) 27:2747–2765 Keywords International law · Treaties · Panthera leo · Threats · Implementation · Reform Introduction After a ground-breaking Conference of the Parties (COP) in Manila in October 2017, the lion (Panthera leo) (among 34 species, including leopards (Panthera pardus)) was added to the Appendices of the Convention on Migratory Species of Wild Animals (CMS), even though 4 range states opposed the listing, and several of these indicated their intention to enter reservations. This addition signals the need for states to develop a more elaborate and coordinated species-specific framework for lion conservation—and a first step towards achieving this was made through Parties’ decision to establish an African Carnivores Ini- tiative in collaboration with the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). In this paper, we consider how the CMS listing of lions (on Appendix II) combines with the existing international legal architecture for lion con- servation, to address the various threats that the species faces—and, importantly, where this architecture falls short, given the specific nature of those threats. We suggest that our analysis has wider relevance for mammalian wildlife (especially large carnivores), through identifying the various roles played by global treaties—and their omissions—in addressing the varied threats that endanger large animals. International treaties provide important frameworks for wildlife conservation worldwide (Bowman et al. 2010; Trouwborst et al. 2017a), and markedly so for charismatic carnivores (Trouwborst 2015). For large carnivores their wide-ranging ecology, reliance on large prey species, and intersection with global trade networks often requires cross-border coopera- tion for effective conservation action (Ripple et al. 2014). Moreover, large carnivore spe- cies tend to attract significant attention from publics and politicians (Lorimer 2015; Mac- donald et  al. 2016) and have the potential to raise awareness for a wide range of other threatened species (Macdonald et al. 2017b). Yet collectively these species are in trouble despite their ecological and cultural importance (Ripple et al. 2014), and lions (Bauer et al. 2015) are no exception. Measuring population sizes accurately is notoriously difficult, but recent estimates for lions suggest that numbers have rapidly declined, with between 20,000 and 30,000 lions remaining across Africa (Bauer et  al. 2016). The conservation of lions also has an added dimension insofar as they are a geographically widely distributed spe- cies (albeit occupying a fraction of their historical range), and measures directed towards their conservation may result in various benefits to other species (Macdonald et al. 2012). Therefore, legal instruments designed to conserve lions may thus also cast a protective shadow over wider biodiversity. In this transdisciplinary paper we (a team of legal experts, conservation biologists and social scientists) draw on the findings of two reviews concerning lions and international law (Trouwborst et al. 2017c; Watts 2016), combined with our analysis of recent develop- ments under the CMS, to map global wildlife treaties against the various ecological and socio-political threats this species faces. We demonstrate that while the coverage of such treaties across lion range states is reassuring, the use of these treaties to address the current threats faced by lions is patchy at best—even before we consider the daunting practicalities of implementation, monitoring and enforcement. Of course, international treaties are only one lever within wider conservation strategies, and will not always be the most appropriate instruments for addressing specific threats. Furthermore, in this paper we limit our scope 1 3 Biodivers Conserv (2018) 27:2747–2765 2749 to the global treaties, and do not assess the roles played by regional agreements and proto- cols in various African contexts. Nevertheless, we suggest improvements are possible and worthwhile pursuing. We note two pathways to improve the contribution of international law to lion conservation: (i) adapting and expanding the application of existing treaties, recent examples of which are the listing of, and associated decisions regarding, lions by the CMS COP (Conference of the Parties) in 2017, and (ii) improving the local-level imple- mentation of treaties. The relevance of international treaties for lions All contemporary lion range states are contracting parties to three or more of the ‘Big 5’ global conservation treaties that—amongst other things—obligate, support, regulate and coordinate measures beneficial to lions and their prey and habitat, either directly or indi- rectly  (Fig.  1). These are: the Convention on Biological Diversity, the ‘Ramsar’ Conven- tion on Wetlands of International Importance, the World Heritage Convention, CITES, and the CMS. Below, we summarize the relevance of each global treaty for lions. There are also sev- eral relevant treaties with a more limited geographic scope, but they are not the subject of this analysis. These include the 1968 African Convention on the Conservation of Nature and Natural Resources (and the 2003 revision thereof); sub-regional instruments like the SADC Protocol on Wildlife Conservation and Law Enforcement; treaty-based regional entities like the Commission of Central African Forests (COMIFAC), the East African Community (EAC) and the Economic Community of West African States (ECOWAS); and treaties establishing transfrontier conservation areas across Africa. Some of the most rel- evant of these agreements are discussed in (Trouwborst et al. 2017c), which considered 33 Fig. 1 Lion range states’ participation in 5 global wildlife treaties. (Color figure online) 1 3 2750 Biodivers Conserv (2018) 27:2747–2765 lion range states, including countries where lions have either been present in recent history, or where there is speculation that they may continue to persist. Here we limit our analysis to known contemporary populations, as listed in the IUCN Red List (25 African states plus India). Convention on Biological Diversity (CBD), 1992 The CBD is a broad-ranging treaty. It is concerned with the conservation and sustainable use of biodiversity, and amongst other things includes general obligations to create pro- tected areas, support threatened species, and create biodiversity strategies and action plans. It has played an important role in gaining additional political support for furthering habitat protection, globally. However, the text of the CBD is, from a legal perspective, so broadly worded as to make the thresholds for compliance somewhat ambiguous (Trouwborst 2015). The CBD also provides a forum for capacity building, discussion, and norm-creation around global biodiversity issues. The resulting high level biodiversity strategies, and guid- ance documents on more specific issues, have clear relevance for lion conservation. For example, the CBD’s Aichi Biodiversity Targets set clear goals around conserving threat- ened species, and the Convention has played a leading role in developing recommendations on addressing the unsustainable taking of bushmeat. All contemporary lion range states are parties. Ramsar Wetlands Convention, 1971 The longstanding global wetlands convention provides a basis for lion conservation through requiring that parties formulate and implement their planning so as to promote the conservation of a specified list of wetland habitats of international importance (‘Ram- sar sites’) designated by individual contracting parties, and as far as possible promote the ‘wise use’ of all wetlands. Certain Ramsar sites are important habitats for lions, and for 24 sites (across 13 countries) their importance for lions (amongst other species) is part of the documentation justifying designation. Ramsar designation thus confers a layer of interna- tionally recognised protection for certain key wetland areas in addition to any other protec- tive designation the site may have (as a reserve, national park etc.), and the potential ben- efits of support provided under the Convention. All contemporary lion range states, except Angola and Ethiopia, are parties. World Heritage Convention (WHC), 1972 Similarly to Ramsar, some important lion habitat is protected through the WHC. Examples of large, iconic sites include the Serengeti National Park in Tanzania, and the Okavango Delta in Botswana. In total, 15 sites in the 25 contemporary lion range states cover over 1,30,000 km of lion range (Trouwborst et al. 2017c). In contrast to the Ramsar Convention, the list of sites designated under the WHC is determined centrally by the World Heritage Committee (consti- tuting a selection of parties on rotation), following nominations by the states in which these sites occur. Furthermore, the condition of World Heritage Sites is monitored: sites can be deemed ‘in danger’ (relevant to 4 of the 15 at present), and ultimately WHC status can be removed. Given the international prestige (and tourism) driven by WHC status, the threat of removal creates an enforcement mechanism that the Ramsar Convention largely lacks. Fur- thermore, the WHC, which is embedded within UNESCO, can provide technical support and 1 3 Biodivers Conserv (2018) 27:2747–2765 2751 guidance to improve the management of ‘at risk’ sites. All contemporary lion range states are parties. Convention on International Trade in Endangered Species (CITES), 1973 CITES is relevant to lion conservation with respect to trade in lion body parts and trophy hunt- ing. The treaty aims to prevent the over-exploitation of species, and works through regulating international trade in live animals, body parts and derivative products. Species that are threat- ened or at risk of becoming threatened and are (potentially) affected by international trade are listed in the Convention’s Appendices, with Appendix I species (species threatened with extinction which are, or may be, affected by trade) being subject to greater restrictions than those on Appendix II (species which might become threatened with extinction if trade is not regulated). Captive-bred animals from Appendix I species are treated as Appendix II—which has been an important consideration in recent discussions around lions. At present, African lions are listed on Appendix II, with the Indian population on Appendix I. There have been two recent proposals from some lion range states to ‘uplist’ all lions to Appendix I, by Kenya in 2004 and by nine states from West and Central Africa ahead of the 2016 CITES COP. How- ever, this is an area of contention amongst lion range states, particularly due to the possible impact of uplisting on trophy hunting, although it is possible for some trophy hunting to con- tinue under an Appendix I listing. Notably, CITES’ ban on the international trade of Appendix I species applies only to specimens which, once imported, would be used for “primarily com- mercial purposes”, and the Convention additionally allows exemptions from its ordinary pro- visions for specimens which constitute “personal or household effects”. Under certain com- plex, and strictly limited, conditions it is therefore possible for some international movement of hunting trophies to continue under an Appendix I listing (as an example, see CITES Res. Conf. 10.14 (Rev. CoP16) on hunting trophies for leopards). While the COP negotiations did not ultimately result in a new Appendix I status for all lions, the meeting did agree on a new ‘annotation’ to the Appendix II listing for African lions which effectively prohibited international trade in most types of lion body parts from wild populations, although allowing regulated, quota-controlled trade for body parts deriving from captive-bred lions. Annotations are used to define the scope of a species’ inclusion on one of the CITES Appendices and can (as was the case for the lion) result in an Appendix II species being subject to more stringent trade restrictions than are ordinarily attached to this Appendix. The COP also adopted resolutions about trophy hunting (suggesting sustainable and well- managed activities can contribute to species conservation) and demand reduction strategies to address illegal wildlife trade, as well as several decisions on the African lion concerning the broader lion conservation agenda (addressing joint conservation planning, capacity building, research and education, among other things). All contemporary lion range states are currently parties to CITES, with the exception of South Sudan, which in any event participated as a non-party in the most recent CITES COP. The Convention has developed various mechanisms to facilitate and, if need be, compel compliance—including through the imposition of trade sanctions. Convention on Migratory Species of Wild Animals (Bonn Convention, CMS), The CMS, which is administered by the United Nations Environment Programme (UNEP), applies predominantly to ‘migratory species’, which are defined as those species where 1 3 2752 Biodivers Conserv (2018) 27:2747–2765 a ‘significant proportion’ of their members ‘cyclically and predictably cross one or more national jurisdictional boundaries’. The CMS COP has taken a remarkably flexible approach to interpreting this term, accepting that ‘cyclically’ ‘relates to a cycle of any nature, such as astronomical (circadian, annual etc.), life or climatic, and of any frequency’, and that ‘predictably’ ‘implies that a phenomenon can be anticipated to recur in a given set of circumstances, though not necessarily regularly in time’ (Res. 11.33). Depending on their conservation status, species which satisfy this definition can be listed on either (or both) of two appendices. The Convention identifies concrete conservation measures that parties must take in respect of the endangered migratory species listed in Appendix I— with ‘endangered’ being interpreted as meaning ‘facing a very high risk of extinction in the wild in the near future’, and as primarily encompassing species with an EW, CE or EN sta- tus on the IUCN Red List (Res. 11.33). Controversially, the measures required in respect of Appendix I-listed species include prohibiting the deliberate killing of these species, subject to limited exceptions. Such exceptions must be precise as to content and limited in space and time, should ‘not operate to the disadvantage of the species’, and may be made only (a) for scientific purposes, (b) for purposes of ‘enhancing the propagation or survival’ of the species, (c) to ‘accommodate the needs of traditional subsistence users’ of the species, or (d) if ‘extraordinary circumstances so require’, (CMS, Article III(5)). The Convention also provides a framework for developing tailor-made mechanisms to support the conservation of specific species/groups of species—including the migratory species listed on Appendix II (the emphasis of this appendix being on migratory species with an unfavourable con- servation status which require international cooperation for their conservation and man- agement), as well as any species whose members periodically cross international borders. Such mechanisms may take a variety of forms, ranging from legally binding ancillary trea- ties to non-binding Memoranda of Understanding, ‘Concerted Actions’, International Spe- cies Action Plans and ‘Special Species Initiatives’. Although their use is not restricted to listed species, listing arguably increases the likelihood that a species will receive attention under the Convention by raising its profile and providing a clear mandate to the CMS Sec- retariat to dedicate time and resources to supporting its conservation. In 2014, the 11th CMS COP recognized that lions are ‘migratory’ for the purposes of the Convention (Res. 11.32); and at the following meeting of the COP, in Manila in October 2017, a decision was made to add lions to Appendix II of the treaty. Basing their arguments on home range utilization, dispersal, movements following herbivore migrations, and movements as a result of annual climatic conditions, the proponents of the listing (Chad, Niger and Togo) asserted that the lion’s transboundary move- ments are sufficiently cyclical and predictable for the purposes of listing. They further identified countries sharing lion populations suspected to cyclically and predictably traverse national boundaries, such that a significant portion of lions could be consid- ered ‘migratory’ for CMS purposes (UNEP/CMS/COP12/Doc.25.1.3 2017). Despite earlier consensus (Res. 11.32), this argument became controversial, and four parties (South Africa, Tanzania, Uganda and Zimbabwe) opposed the listing, arguing, inter alia, that transborder movements do not necessarily equate to migration and that the lion’s movements fail to satisfy all elements of the Convention’s definition of ‘migra- tory species’. Ultimately, the matter had to be decided by vote, this being the first vote on a species’ listing in the history of the Convention. The listing was adopted by a large majority of the parties present and voting, with only the aforementioned four states voting against. Notably, the text of Resolution 11.33 was reconsidered at the 2017 COP, but its interpretation of ‘migratory species’ remained unchanged. To the extent that arguments exist for modifying the Convention’s flexible approach to listing, 1 3 Biodivers Conserv (2018) 27:2747–2765 2753 it would (for the sake of consistency) appear to be more appropriate to raise these in the context of a general discussion on whether to revise this Resolution than in dis- cussions over whether or not to list individual species that happen to be of political interest. To date, however, such a discussion has not emerged. The majority of listing proposals have been adopted without contention (indeed, there are instances in which species considerably less migratory than lions have been listed without debate), with the agreed interpretation of ‘migratory species’ tending only to be questioned when high-profile listings are at stake. In the absence of a broader discussion of Resolu- tion 11.33, each listing of a species that is transboundary but does not migrate in the classical sense adds weight to future arguments that the Convention’s appendices are not reserved exclusively for species that engage in predictable annual migrations. The lion’s listing is especially significant in this regard insofar as the majority of CMS par - ties were willing to explicitly endorse a flexible approach, even when confronted with fierce arguments against it. Although the CMS allows for listing to be applied selectively at the level of geo- graphically separate populations, it is significant that the proponents of the lion’s Appendix II listing were not prepared to exclude the lion populations of South Africa, Tanzania, Uganda and Zimbabwe, which are not biologically distinct from contiguous populations. Indeed, such an exclusion of parts of populations using ecologically arbi- trary boundaries—international frontiers between countries—would have been con- trary to the spirit of the Convention and would have set a bad precedent for future list- ing decisions. It is further notable that the CMS definition of ‘migratory species’ only applies to wild animals, and thus has no application to captive populations. Several lion populations are intensively managed and some were reintroduced after local extirpation (e.g. Akagera in Rwanda); South Africa distinguishes ‘wild’, ‘wild managed’ and ‘cap- tive’ populations (Bauer et  al. 2016; Funston and Levendal 2014; Miller et  al. 2013). Although CMS listing would exclude captive populations, all other populations would putatively be included—a precedent for this being established when Przewalski’s horse (Equus ferus przewalskii) was listed without any reference to it having been extinct in the wild for several decades and then reintroduced, using captive individuals, and man- aged (UNEP/CMS/COP12/Doc.25.1.8). In addition to listing the lion on Appendix II, the 2017 CMS COP adopted several decisions on this species (which corresponded to the decisions adopted at the most recent CITES COP) and agreed on the establishment of a joint CMS-CITES African Carnivores Initiative to support the implementation of resolutions and decisions on lions, leopards, cheetahs (Acinonyx jubatus) and wild dogs (Lycaon pictus) under both treaties (CMS 2017). Theoretically, the Initiative could ultimately pave the way for the development of a more formal arrangement, such as a carnivore-focused treaty. How- ever, this is unlikely in the foreseeable future, given the Convention’s recent shift away from the costly development of new legal and administrative frameworks in an attempt to channel more resources directly into implementation support. Notably, range states which are not parties to the CMS can still choose to participate in ancillary instruments, action plans and initiatives. Two existing multi-species CMS Concerted Actions are likely to become relevant to lions (Central Eurasian Aridland Mammals, Sahelo-Saha- ran Megafauna) and a third has been mooted as a possibility (Sub-Saharan Megafauna). The lion population in India could also potentially be included in the Convention’s Cen- tral Asian Mammals Initiative. The majority of lion range states are parties to the CMS, exceptions are: Botswana, Central African Republic, Malawi, Namibia, South Sudan, Sudan and Zambia. 1 3 2754 Biodivers Conserv (2018) 27:2747–2765 Assessing cumulative coverage of global treaties Global treaties thus support the conservation of contemporary populations of lions in vari- ous ways. Furthermore, the majority of lion range states are parties to the treaties—all for the CBD and the WHC, all except South Sudan for CITES and all except Angola and Ethi- opia for the Ramsar Convention. Even the CMS, which has the lowest level of coverage, still has 17 of 25 lion range states as parties (accounting for 80% of the estimated contem- porary lion species population). Mapping the contributions of global conservation treaties against contemporary threats The various forms of legal protection conferred through global treaties apply to the major- ity of lion range states and extant lion populations. However, they presently do not com- prehensively and directly address the most critical threats facing lions in Africa (99% of the worldwide population). We rely on three recent sources to collate threats to lions: (i) the Communiqué from the May 2016 CMS-CITES hosted meeting of African lion range states in Entebbe, (ii) a recent report on Africa’s lions published by Panthera, WildAid and the WildCRU, Oxford (Panthera et  al. 2016), and (iii) the IUCN’s Red List assessments (Bauer et  al. 2016; Breitenmoser et  al. 2008). Our synthesis of these three sources is in close accord with other recent assessments (Lindsey et al. 2017). The full list of threats is summarized in Table 1, with the relevance of each treaty noted for each threat. Whilst these threats vary in their severity for different regions and sub-populations, the summary herein is for lions in the aggregate. The most pressing issues facing African lions are human-lion conflict leading to retaliatory or pre-emptive killing, and bushmeat poaching leading to prey depletion: these threats are ranked as critical in the Panthera-led report, followed by human encroachment which is ranked as a high threat (Panthera et al. 2016). At present, these issues are addressed by global treaties only to a modest extent. The CBD provides a general requirement and platform to address these threats. In addition, the Ramsar and World Heritage Conventions require and facilitate addressing these threats for cer- tain designated sites. Both the CBD and CITES COPs have also adopted resolutions on the issue of bushmeat hunting, and the 2017 CMS COP adopted several decisions to address the unsustainable use of bushmeat (‘wild meat’, in CMS parlance). While the various convention texts do not address human-wildlife conflict specifically, a con- siderable body of guidance has been developed on the issue by the various COPs, in documents that are not themselves legally binding but can nevertheless influence the interpretation and application of the binding treaty provisions (also known as ‘soft law’). More importantly, they also address some of the causes (e.g., regulating live- stock access to protected areas) and some symptoms (e.g., the indiscriminate killing of lions). However, given the urgency of the threats, and the failure to address them at present, it is worth considering the additional roles global treaties might play. As dis- cussed above, the recent listing of lions in Appendix II of the CMS has created a legal framework through which a variety of actions might be taken that could focus specifi- cally on these issues, and could coordinate action across the remaining range states. We note the significant potential of the CMS-CITES African Carnivores Initiative in 1 3 Biodivers Conserv (2018) 27:2747–2765 2755 1 3 Table 1 Summary of how global treaties address threats to lions Threats Severity of threat Treaty Relevance Human-lion conflict (retaliatory and pre-emptive kill- Critical CBD Provides general requirement and platform to address threat ing) [i,ii,iii] RAMSAR Requires and facilitates addressing threat for certain wetlands WHC Requires and facilitates addressing threat for certain sites CMS Provides species-specific platform for coordination and targeted action CITES Provides species-specific platform for coordination and targeted action Bushmeat poaching (prey depletion) [i,ii,iii] Critical CITES Requires and facilitates regulation of international bushmeat trade CBD Provides general requirement and platform to address threat RAMSAR Requires and facilitates addressing threat for certain wetlands WHC Requires and facilitates addressing threat for certain sites CMS Provides species-specific platform for coordination and targeted action Human encroachment/habitat degradation [i,ii,iii] High CBD Provides general requirement and platform to address threat RAMSAR Requires and facilitates addressing threat for certain wetlands WHC Requires and facilitates addressing threat for certain sites CMS Provides species-specific platform for coordination and targeted action Poorly regulated trophy hunting [ii,iii] Medium CITES Regulates international movements of trophies CBD Provides general requirement and platform to ensure sustainability RAMSAR Requires ensuring sustainability of hunting for certain wetlands WHC Requires ensuring sustainability of hunting for certain sites CMS Provides species-specific platform for coordination and targeted action Trade in lion bones [i,ii,iii] Unknown CITES Regulates international trade (currently prohibited, except captive-bred) CBD Provides general requirement to promote sustainability of hunting RAMSAR Requires avoiding harmful impact for certain wetlands WHC Requires avoiding harmful impact for certain sites CMS Provides species-specific platform for coordination and targeted action 2756 Biodivers Conserv (2018) 27:2747–2765 1 3 Table 1 (continued) Threats Severity of threat Treaty Relevance Unpredictable events (e.g., floods) [iv] Not quantified CBD Provides general requirement to promote resilience RAMSAR Requires and facilitates ensuring resilience for certain wetlands WHC Requires and facilitates ensuring resilience for certain sites CMS Provides species-specific platform for coordination and targeted action Socio-economic factors [i] Not quantified CITES Requires and facilitates ensuring sustainability of trade CBD Requires and facilitates sustainable use RAMSAR Requires and facilitates wise use of wetlands WHC Requires and facilitates sustainable use of natural heritage CMS Provides species-specific platform for coordination and targeted action Policy failure and political factors [i] Not quantified CITES Provides platform for coordination regarding international trade CBD Provides general platform for coordination RAMSAR Provides platform for coordination regarding wetlands WHC Provides platform for coordination regarding natural heritage CMS Provides species-specific platform for coordination and targeted action Governance and institutional weakness [i] Not quantified CITES Promotes capacity-building regarding international trade CBD Promotes capacity-building regarding biodiversity generally RAMSAR Promotes capacity-building regarding wetlands WHC Promotes capacity-building regarding natural heritage CMS Provides species-specific platform for capacity-building Sources for threat analysis given below. ‘Severity of threat’ from Panthera et al. (2016) (i) The Entebbe Communiqué from the May 2016 CMS-CITES hosted meeting of African Range States. (ii) Panthera et al. (2016), (iii) Bauer et al. IUCN (2016), (iv) Bre- itenmoser et al. IUCN (2008) Biodivers Conserv (2018) 27:2747–2765 2757 this regard, with a substantial part of the Initiative’s envisaged budget earmarked for promoting human-carnivore coexistence (UNEP/CMS/COP12/Doc.24.3.1.1). That such frameworks might be accessible to non-party range states (see earlier discussion) adds significantly to their potential. The other threats to lions are addressed more directly by global treaties. Habitats gain a degree of legal protection from human encroachment and resulting degradation through the international designation of certain areas (with accompanying conserva- tion benefits) under the auspices of the WHC and Ramsar, and the broadly-phrased CBD commitment to establish protected areas and to protect endangered species and habitats. However, the continuing severity of the threats to lion habitat (Riggio et  al. 2013) raises important questions as to the scope of such ‘generalist’ (i.e., not species- specific) treaties, and the procedures and mechanisms by which enforcement of treaty provisions might occur (Trouwborst et  al. 2017c). Both the international movement of hunting trophies and trade in lion bones are addressed directly by CITES, although important debates and discussions continue as to whether the current arrangements (summarized earlier) are effective (see discussion). Stochastic events such as floods and fires can pose a threat to lions in small, geographically restricted populations, and remain a significant threat for the population of lions in India (Breitenmoser et al. 2008); again, the indirect support for protected areas provided by treaties is relevant here, as is the CMS objective of maintaining unfragmented, more robust and resil- ient transboundary populations. The Entebbe Communiqué also recognized a series of socio-political threats relating to governance, policy, and economic issues that combine to limit the efficacy of lion conservation. The various global treaties are par - ticularly important when it comes to policy formulation and capacity building in this respect. The bureaucracies of the various treaties, grounded inter alia in UNEP and UNESCO, hold significant potential as regards institutional support and coordination for lion conservation. As many species besides lions are covered by the various global wildlife treaties, some of which face similar threats to lions, several aspects of the preceding analysis concerning these treaties will also apply to their actual or potential roles with regard to such species, particularly other large carnivores (Trouwborst 2015). Discussion Becoming a party to international treaties is an important way that lion range states can signal their commitment to manage their wildlife populations sustainably, and the publicity around these treaties raises much-needed global awareness of the plight of lions and other species. However, despite the widespread applicability of global trea- ties across lion range, lions have continued to decline calamitously: across Africa, their numbers have approximately halved in the past 20 years, and they have been extirpated from over 90% of their historic range (Bauer et al. 2016). Clearly, therefore, there is a pressing need to improve the performance of international treaties in terms of effective lion conservation. Here, we suggest two main ways that lion conservation could be improved under the global treaties discussed in this paper: (i) Adapt and expand the application of existing treaties 1 3 2758 Biodivers Conserv (2018) 27:2747–2765 (ii) Improve local-level implementation of treaties Adapt and expand the application of existing treaties First, existing treaties might be better utilised for lion conservation (Trouwborst 2015). The recent listing of lions in Appendix II of the CMS is an example. This listing raises the lion’s international legal profile whilst simultaneously providing bureaucratic capacity and a framework to support additional coordinated action by lion range states to address the most critical threats to the species. However, international agreement by itself will not be enough to combat prey depletion, and policing the killing of large carnivores is resource intensive and difficult (Critchlow et  al. 2016; Johnson et  al. 2016). Thus, a package of measures is needed that improves both the legal framework and local implementation and enforcement (see below). Another reform might involve CITES. There is an important debate occurring as to whether the current treatment of lions in CITES is optimal (Bauer et al. 2018; Trouwborst et  al. 2017c). Future actions planned by CITES, resulting from the 2016 COP17, include the creation of a Task Force on African Lions and the formulation and implementation of conservation strategies for the species, in collaboration with the CMS. Yet significant questions continue to revolve around whether allowing legal markets for megafauna body parts from captive populations is compatible with reducing demand for illegally-sourced body parts (Di Minin et al. 2015), whether controlling a chain of custody for legal products is practically feasible (Bennett 2015) and whether look-alike issues create insurmountable enforcement problems across species. The extent of trade in body parts of wild lions has been a cause of concern, and although initial expert surveys do not reveal it as a serious problem at present, it may become so in the future (Williams et  al. 2015a, b, 2017a, b). There is also continuing debate around the status of trophy hunting within lion conserva- tion, and whether it should be considered as a threat to wild populations or as a sustainable form of management and source of conservation finance (Di Minin et al. 2016; Macdonald et al. 2016, 2017a). Further ways to increase the utility of global wildlife treaties include the listing of additional sites of importance to lion conservation under the Ramsar and World Heritage Conventions (Trouwborst et  al. 2017c). It would also be beneficial to more fully utilise the support mechanisms associated with these Conventions to improve the management of currently designated sites, so that they can better conserve lion populations. Funding has been identified as a major issue in lion conservation (Lindsey et al. 2017; Packer et al. 2013); global treaties can mobilise funding but can also provide guidance and bureaucratic capacity in spending and administering it. This is not an easy task as, in practice, ‘improv- ing management’ involves complex social and ecological challenges. As an example, the Ngorongoro Conservation Area (NCA) is a World Heritage Site, and has received over US$270 000 in international assistance since its designation in 1979 (UNESCO 2015). The NCA has experienced intense human-lion conflict (associated with a rapidly grow - ing human population) and the lion population has declined substantially since the 1980s. There are mounting tensions regarding the management of the NCA, a multiple land-use conservation area where humans (mainly Maasai pastoralists), lions and other wildlife are intended to coexist. UNESCO and the IUCN conducted a reactive monitoring mis- sion there in 2008, noting that while a previous study stated that the area had a carrying capacity of 25 000 people with cattle, 67,000 people lived in the NCA by 2007 (UNESCO 2015). However, the Maasai were not involved in the carrying capacity study and contested 1 3 Biodivers Conserv (2018) 27:2747–2765 2759 the findings. Moreover, many of the Maasai in the area have given up their nomadic life- styles and are now dependent upon agriculture, but all forms of agriculture were banned in the NCA in 2007 (Ikanda and Packer 2008). The ban led to much antagonism amongst local residents, although it has been neither enforced nor managed. UNESCO’s World Her- itage Centre and the IUCN consider that enforcing the ban would be positive for conserva- tion of the site, but it would clearly affect the livelihoods of local people, especially as even the 25,000 estimate of carrying capacity involved some reliance upon agriculture. Conflicts between local Maasai communities and the NCA authorities are growing, particularly as residents feel disempowered. The World Heritage Centre and IUCN have made several rec- ommendations for action, including commissioning a new carrying capacity study explic- itly considering the needs of the local Maasai community, encouraging the voluntary relo- cation of immigrants, and increasing the active participation of local communities in the decision-making processes. Thus, international treaties and their bureaucratic apparatuses can play a role in improving local management, but doing so involves navigating these complex social and ecological considerations. Improve local‑level implementation of international treaties The value of international treaties for conservation is multifaceted (Trouwborst et  al. 2017a), but their impact remains limited where they are poorly implemented, for example due to corruption or other poor governance practices. The provisions of international trea- ties are often transposed into national legal systems through domestic laws and regulations. Treaties thus impose obligations on states, but it is up to those states to utilise or create national arrangements to meet their obligations. Many of the treaty obligations are broad rather than very specific, and the party involved is expected to do what works best, which includes striking the right balance between top-down legislation and bottom-up approaches (Redpath et al. 2017). Since the fates of lions are largely determined by the actions of resi- dent or nomadic people living alongside them, sensitively designed conservation strategies at both a national and sub-national level are vital to ensuring that the obligations of inter- national treaties are met, while ensuring that the rules are applicable and appropriate for the local people concerned. Conversely, implementation of treaties can be ineffective in a variety of ways, notably: if compliance with, awareness of or enforcement of national laws and regulations is lacking; if bottom-up conservation strategies fail to meet parties’ obliga- tions; and/or if parties’ national implementation laws and other conservation actions are themselves inadequate for complying with international obligations. For domestic measures to be effective in meeting treaty obligations, it is important that people understand the different legal categories for wildlife, and that there are effective management plans and communication strategies regarding the rules associated with those categories. In many lion range countries, some or all of those components are lacking. All too often local communities are entirely unacquainted with national laws or regulations protecting wildlife, as they are often disengaged from the legal and conservation discourse. For example, in Tanzania’s Ruaha landscape, which still supports the world’s second larg- est lion population but has extremely high rates of lion killing (Abade et  al. 2014), local people are usually completely unaware that lions are in decline, and are also largely una- ware of domestic laws designed to protect them (Dickman pers. obs.). In Mozambique, a country with 15% of remaining lion range, a study in Maputo Elephant Reserve found that 65% of people (82% of whom were dependent upon consumptive wildlife use) had never heard of the country’s new Forest and Wildlife Policy (Soto et  al. 2001). Moving outside of lion range states, a study in Madagascar revealed that less than half the local 1 3 2760 Biodivers Conserv (2018) 27:2747–2765 respondents were able to correctly classify species into their legal categories (Keane et al. 2011). This study further suggested that engaging people directly in natural resource man- agement can sensitise them to conservation laws, which is likely to have relevance in many lion areas, where those people living alongside lions are often marginalised and report very little engagement in any conservation activities (Dickman 2009). Furthermore, increasing local awareness of international requirements can result in enhanced support for conserva- tion measures. For instance, in a survey of the benefits associated with the designation of Ramsar sites in Africa, for some sites international designation had led to increased interest by local communities, the establishment of community patrols to reduce trespassing and poaching, and/or in a change of behaviour of site users (Gardner et al. 2008). Even when knowledge of locally applicable rules and regulations is apparent, these are frequently ignored. For example, Tanzania, which has 40% of the world’s remaining lions and over a quarter of remaining lion range, has severe human-lion conflict and very high rates of anthropogenic lion killing, with just one study documenting 35 lions killed around 3 small villages in less than 18  months (Dickman 2015). Lion killings in Tanzania often fulfil both a ritual role, to prove bravery, and a defensive one to reduce attacks on livestock or people (Dickman 2015; Ikanda and Packer 2008; Kissui 2008). While Tanzania banned ritual lion hunting in the 1970s, the country’s 2009 Wildlife Conservation Act (amended in 2013) permits people to kill lions and other wildlife in defence of human life or livestock; if people are aware of legal restrictions they are also aware of this loophole. Lions impose major costs on local people (Dickman 2009; Packer et al. 2005), so additional measures to reduce conflict are necessary. Much lion killing is centred around livestock losses, which are particularly devastating for traditional pastoralist societies, where cattle have high cul- tural as well as economic value. Unless international treaty obligations can be translated into more effective livestock protection, such threats will continue. However, lion killing often has multiple drivers, such as the cultural status that people get from killing lions, or the fact it can offer one of the few ways of generating wealth (usually through gifts of cattle from herders in thanks for removing a predator) or facilitating marriages, and this can generate sufficient social and economic benefits for lion killing to persist even in the near-absence of livestock attacks (Fitzherbert et al. 2014). Understanding these dynamics is fundamentally important to developing effective conservation strategies, and requires the involvement of local people to ascertain site-specific threats and determine which legal measures would be most effective at combating them. Engaging communities in decision- making and ownership of control mechanisms has led to proven success in some lion areas: in Namibia, enabling local people to own and control their wildlife has contributed to one of the few increasing national lion populations, while in areas of Kenya, Tanzania, Ethio- pia and Mozambique, locally-driven programmes where communities develop and enforce rules have proven relatively successful at reducing threats to lions (Fitzherbert et al. 2014; Gebresenbet et al. 2017; Hazzah et al. 2014; Redpath et al. 2017). It is important to note, therefore, that the involvement of local people, participatory approaches, poverty allevia- tion, awareness-raising and education have become increasingly central tenets of all the major conservation treaties, as reflected in COP decisions, strategies, allocation of funding, manuals and other technical guidance. Useful examples of the latter include the Ramsar Handbook on Participatory Skills (Ramsar Convention Secretariat 2010), the World Herit- age Resource Manual on Managing Natural World Heritage (UNESCO et  al. 2012), and the CBD Technical Series volume on livelihood alternatives for unsustainable bushmeat use (Secretariat of the Convention on Biological Diversity 2011). The efficacy of national measures taken to implement international commitments is also determined by the ability of range states to monitor and enforce the ensuing regulations, 1 3 Biodivers Conserv (2018) 27:2747–2765 2761 and on the quality of the laws and regulations themselves. Laws may be flouted due to a low probability of detecting illegal behaviour, particularly in countries which have lim- ited capacity within their wildlife agencies (Shanee 2012). Many wildlife crimes fail to be detected by the authorities; data from Zambia’s Luangwa Valley suggested that detec- tion rates of black rhinoceros (Diceros bicornis) and elephant (Loxodonta africana) poach- ing were too low to prevent declines (Leader-Williams and Milner-Gulland 1993), while a study across four countries by Akella and Cannon (2004) estimated that the risk of punish- ment for environmental crime was very low (below 1% in the two countries with reason- able estimates). This is supported by our experience in lion range countries: in Ruaha, over 90% of the documented lion killing events were detected by researchers, with authorities having very little capacity to monitor anthropogenic killing outside (and sometimes even within) protected areas (Dickman pers. obs.). Wildlife rangers often have little training, and commonly resort to lethal control as a first option for resolving human-lion conflict. Such methods tend to reinforce local attitudes assuming killing lions is the best way to man- age conflict, and thus frequently lead to additional subsequent lion killing (Dickman pers. obs.). In addition to compliance and enforcement, the parties’ national implementation laws must be fit for purpose in the first place. This is not always the case. For example, the central bureaucracy of CITES monitors the extent to which contracting parties’ national legislation (and related measures) are able to implement the treaty’s provisions, and this differs markedly between lion range states (CITES 2016). National-level implementation capacity is affected by a range of socio-political, economic and cultural factors that shape the efficacy of national and sub-national bureaucratic activities—what might be termed a nation’s ‘conservation likelihood’(Dickman et al. 2015). As a final example of implementation challenges, the proliferation of ‘paper parks’ which are not effectively funded, managed or enforced is well documented (Bruner et al. 2001). Furthermore, the efficacy of protected areas can be additionally compromised by changes in governance arrangements, including to the human activities allowed therein, the size of the area, or even the removal of protected status—trends termed ‘PADDD’ or protected area downgrading, downsizing and degazettement in the literature (Mascia and Pailler 2011), and of potential relevance in some lion range states (see www.paddd track er.org for details). Many lion range states have insufficient funds to effectively manage core protected areas (Lindsey et  al. 2017), so providing sufficient law enforcement resources and expanding effective wildlife conservation on human-dominated land is unlikely with- out significant additional investment. International treaties have the capacity to leverage additional funding for protected areas, as well as wider wildlife conservation, so could play a very valuable role in this regard. Yet even with the stricter monitoring and enforcement provisions of the WHC noted earlier, many natural World Heritage Sites are threatened by the ecological isolation caused by development outside their borders (Allan et  al. 2017). Such edge effects, including those relating to the pressures of human populations, are espe- cially relevant for lions given the threats (such as bushmeat hunting and human-lion con- flict) they currently face (Woodroffe and Ginsberg 1998). Furthermore, action beyond their boundaries is often necessary even if protected areas are well managed, and even though lions are increasingly limited to protected areas some range lies outside of reserves; Durant et al. (2017) actually demonstrated that survival of some species depends on non-protected land, including the cheetah and African wild dog that have most of their range outside reserves. Addressing local concerns and community practices is a complex undertaking that requires a multi-faceted conservation strategy (Redpath et al. 2017); but as discussed herein, global treaties may help when it comes to building capacity and developing guid- ance in these respects. 1 3 2762 Biodivers Conserv (2018) 27:2747–2765 Concluding observations When it comes to international law, like all forms of wildlife law, the details of interpre- tation matter (Epstein et  al. 2016; Trouwborst et  al. 2017b). So do the contextual spe- cificities of the range states to which treaty provisions apply: their politics, governance, bureaucratic capacity, histories, cultures, and socio-economic characteristics (Dickman et  al. 2015). The review of global treaties offered here is a high-level summary, and as such the intricacies of how each treaty has been and might be further utilised (or not) to address specific threats to lions in different regions and cultural contexts are not addressed in great detail (see Trouwborst et  al. 2017c). Furthermore, legal meas- ures, whether created through international treaties, national laws, local or community restrictions, are only ever a part of a broader set of measures within conservation. How- ever, even limiting the review to this high level, we have suggested several priorities for reform and practical pathways towards improving lion conservation. These are: expand- ing the application of global treaties in respect of lions and their habitats (with the recent CMS listing representing a potentially significant step in these terms), improving the local-level implementation of treaty commitments through participatory regulatory developments, and supporting implementation and enforcement capacity at national and local scales. In conclusion, even if their effective implementation is beset with practical challenges, global wildlife treaties have distinct contributions to make to lion conserva- tion, the importance of which is likely to increase rather than diminish in the foresee- able future. Acknowledgements TH is the Kadas Senior Research Fellow in Geopolitics at Worcester College, Oxford. AT acknowledges the support of the Netherlands Organization for Scientific Research, as part of the project Ius Carnivoris (Project No.: 452-13-014). EAM is the Rivington Winant Post-doctoral Fellow and AD the Kaplan Senior Research Fellow in Felid Conservation at Pembroke College. All the authors grate- fully acknowledge the support of grants to DWM from the Robertson Foundation and the Recanati-Kaplan Foundation and Panthera. We would like to thank Dan Parker and Guillaume Chapron (reviewers) for their helpful comments; any errors remain ours alone. Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 Inter- national License (http://creat iveco mmons .org/licen ses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. References Abade L, Macdonald DW, Dickman AJ (2014) Assessing the relative importance of landscape and hus- bandry factors in determining large carnivore depredation risk in Tanzania’s Ruaha landscape. Biol Cons 180:241–248. https ://doi.org/10.1016/j.bioco n.2014.10.005 Akella AS, Cannon JB (2004) Strengthening the weakest links: strategies for improving the enforcement of environmental laws globally. Center for Conservation and Government [Conservation International] Allan JR, Venter O, Maxwell S, Bertzky B, Jones K, Shi Y, Watson JEM (2017) Recent increases in human pressure and forest loss threaten many Natural World Heritage Sites. Biol Cons 206:47–55. https ://doi. org/10.1016/j.bioco n.2016.12.011 Bauer H et al (2015) Lion (Panthera leo) populations are declining rapidly across Africa, except in inten- sively managed areas. Proc Natl Acad Sci USA 112:14894–14899. https ://doi.org/10.1073/pnas.15006 Bauer H, Nowell K, Sillero-Zubiri C, Macdonald DW (2018) Lions in the modern arena of CITES. Conserv Lett. https ://doi.org/10.1111/conl.12444 1 3 Biodivers Conserv (2018) 27:2747–2765 2763 Bauer H, Packer C, Funston PF, Henschel P, Nowell K (2016) Panthera leo. The IUCN Red List of Threat- ened Species 2016. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T1595 1A799 29984 .en. Accessed 02 August 2016 Bennett EL (2015) Legal ivory trade in a corrupt world and its impact on African elephant populations. Conserv Biol 29:54–60. https ://doi.org/10.1111/cobi.12377 Bowman M, Davies PGG, Redgwell C, Lyster S (2010) Lyster’s international wildlife law, 2nd edn. Cambridge University Press, Cambridge Breitenmoser U, Mallon DP, Ahmad Khan J, Driscoll C (2008) Panthera leo ssp. persica. IUCN Red List Threatened Species. https ://doi.org/10.2305/IUCN.UK.2008.RLTS.T1595 2A532 7221.en Bruner AG, Gullison RE, Rice RE, da Fonseca GAB (2001) Effectiveness of Parks in Protecting Tropi- cal. Biodiv Sci 291:125–128. https ://doi.org/10.1126/scien ce.291.5501.125 CITES (2016) Status of CITES implementation legislation CMS (2017) Press release: momentum grows to save world’s migratory wildlife. http://www.cms.int/en/ news/press -relea se-momen tum-grows -save-world ’s-migra tory-wildl ife. Accessed 30 October 2017 Critchlow R et  al (2016) Improving law-enforcement effectiveness and efficiency in protected areas using ranger-collected monitoring data. Conserv Lett. https ://doi.org/10.1111/conl.12288 Di Minin E et al (2015) Identification of policies for a sustainable legal trade in rhinoceros horn based on population projection and socioeconomic models. Conserv Biol 29:545–555. https ://doi. org/10.1111/cobi.12412 Di Minin E, Leader-Williams N, Bradshaw CJA (2016) Banning trophy hunting will exacerbate biodi- versity loss. Trends Ecol Evol 31:99–102. https ://doi.org/10.1016/j.tree.2015.12.006 Dickman AJ (2009) Key determinants of conflict between people and wildlife, particularly large carni- vores, around Ruaha National Park, Tanzania. PhD, University College London Dickman AJ (2015) Large carnivores and conflict in Tanzania’s Ruaha landscape. In: Redpath SM, Gut- ierrez RJ, Wood KA, Young JC (eds) Conflicts in conservation: navigating towards solutions. Cam- bridge University Press, Cambridge, pp 30–32 Dickman AJ, Hinks AE, Macdonald EA, Burnham D, Macdonald DW (2015) Priorities for global felid conservation. Conserv Biol 29:854–864. https ://doi.org/10.1111/cobi.12494 Durant SM et al (2017) The global decline of cheetah Acinonyx jubatus and what it means for conserva- tion. Proc Natl Acad Sci USA 114:528–533. https ://doi.org/10.1073/pnas.16111 22114 Epstein Y, López-Bao JV, Chapron G (2016) A legal-ecological understanding of favorable conservation status for species in Europe. Conserv Lett 9:81–88. https ://doi.org/10.1111/conl.12200 Fitzherbert E, Caro T, Johnson PJ, Macdonald DW, Mulder MB (2014) From avengers to hunters: lever- aging collective action for the conservation of endangered lions. Biol Cons 174:84–92 Funston P, Levendal M (2014) Biodiversity Management Plan for the Lion (Panthera leo) in South Africa. Republic of South Africa Gardner RC, Connolly KD, Bamba A (2008) African wetlands of international importance: assess- ment of benefits associated with designations under the Ramsar Convention. Geo Int’l Envtl L Rev 21:257 Gebresenbet F, Baraki B, Yirga G, Sillero-Zubiri C, Bauer H (2017) A culture of tolerance: coexisting with large carnivores in the Kafa Highlands, Ethiopia. Oryx. https ://doi.org/10.1017/s0030 60531 60013 56 Hazzah L, Dolrenry S, Naughton L, Edwards CT, Mwebi O, Kearney F, Frank L (2014) Efficacy of two lion conservation programs in Maasailand, Kenya. Conserv Biol 28:851–860 Ikanda D, Packer C (2008) Ritual vs. retaliatory killing of African lions in the Ngorongoro Conservation Area, Tanzania. Endanger Species Res 6:67–74 Johnson A et al (2016) To protect or neglect? Design, monitoring, and evaluation of a law enforcement strategy to recover small populations of wild tigers and their prey. Biol Conserv 202:99–109. https ://doi.org/10.1016/j.bioco n.2016.08.018 Keane A, Ramarolahy AA, Jones JP, Milner-Gulland E (2011) Evidence for the effects of environmental engagement and education on knowledge of wildlife laws in Madagascar. Conserv Lett 4:55–63 Kissui B (2008) Livestock predation by lions, leopards, spotted hyenas and their vulnerability to retalia- tory killing in the Maasai steppe, Tanzania. Animal Conserv 11:422–432 Leader-Williams N, Milner-Gulland EJ (1993) Policies for the enforcement of wildlife laws: the balance between detection and penalties in Luangwa Valley, Zambia. Conserv Biol 7:611–617 Lindsey P et  al (2017) The performance of African protected areas for lions and their prey. Biol Cons 209:137–149 Lorimer J (2015) Wildlife in the Anthropocene: conservation after nature. University of Minnesota Press, Minneapolis 1 3 2764 Biodivers Conserv (2018) 27:2747–2765 Macdonald D, Loveridge A, Dickman A, Johnson P, Jacobsen K, du Preez B (2017a) Lions, trophy hunt- ing and beyond, known unknowns and why they matter. Mammal Rev. https ://doi.org/10.1111/ mam.12096 Macdonald DW, Burnham D, Hinks AE, Wrangham R (2012) A problem shared is a problem reduced: seeking efficiency in the conservation of felids and primates. Folia Primatol 83:171–215 Macdonald DW, Jacobsen KS, Burnham D, Johnson PJ, Loveridge AJ (2016) Cecil: a moment or a movement? Analysis of media coverage of the death of a lion, Panthera leo. Animals 6:26 Macdonald EA et  al (2017b) Identifying ambassador species for conservation marketing. Glob Ecol Conserv. https ://doi.org/10.1016/j.gecco .2017.11.006 Mascia MB, Pailler S (2011) Protected area downgrading, downsizing, and degazettement (PADDD) and its conservation implications. Conserv Lett 4:9–20. https ://doi.org/10.1111/j.1755- 263X.2010.00147 .x Miller S et  al (2013) Management of reintroduced lions in small, fenced reserves in South Africa: an assessment and guidelines, South African. J Wildl Res 43:138–154 Packer C, Ikanda D, Kissui B, Kushnir H (2005) Lion attacks on humans in Tanzania. Nature 436:927–928 Packer C et al (2013) Conserving large carnivores: dollars and fence. Ecol Lett 16:635–641. https ://doi. org/10.1111/ele.12091 Panthera, WildAid, WildCRU (2016) Beyond Cecil: Africa’s Lions in Crisis Ramsar Convention Secretariat (2010) Participatory skills: establishing and strengthening local commu- nities’ and indigenous people’s participation in the management of wetlands. Ramsar Convention Secretariat, Gland Redpath SM et al (2017) Don’t forget to look down–collaborative approaches to predator conservation. Biol Rev 92:2157–2163 Riggio J et  al (2013) The size of savannah Africa: a lion’s (Panthera leo) view. Biodivers Conserv 22:17–35. https ://doi.org/10.1007/s1053 1-012-0381-4 Ripple WJ et  al (2014) Status and ecological effects of the world’s largest carnivores. Science. https :// doi.org/10.1126/scien ce.12414 84 Secretariat of the Convention on Biological Diversity (2011) Livelihood alternatives for the unsustain- able use of bushmeat. Secretariat of the CBD, Montreal Shanee N (2012) Trends in local wildlife hunting, trade and control in the Tropical Andes Biodiversity Hotspot, northeastern Peru. Endanger Species Res 19:177–186 Soto B, Munthali SM, Breen C (2001) Perceptions of the forestry and wildlife policy by the local com- munities living in the Maputo Elephant Reserve, Mozambique. Biodivers Conserv 10:1723–1738 Trouwborst A (2015) Global large carnivore conservation and international law. Biodivers Conserv 24:1567–1588. https ://doi.org/10.1007/s1053 1-015-0894-8 Trouwborst A et al (2017a) International wildlife law: understanding and enhancing its role in conserva- tion. Bioscience 67(9):784–790. https ://doi.org/10.1093/biosc i/bix08 6 Trouwborst A, Boitani L, Linnell JDC (2017b) Interpreting ‘favourable conservation status’ for large carnivores in Europe: how many are needed and how many are wanted? Biodivers Conserv 26:37– 61. https ://doi.org/10.1007/s1053 1-016-1238-z Trouwborst A et al (2017c) International law and lions (Panthera leo): understanding and improving the contribution of wildlife treaties to the conservation and sustainable use of an iconic carnivore. Nat Conserv 21:83–128. https ://doi.org/10.3897/natur econs ervat ion.21.13690 UNESCO (2015) State of Conservation: Ngorongoro Conservation Area. http://whc.unesc o.org/en/ soc/479. Accessed 26 July 2017 UNESCO, ICCROM, ICOMOS, IUCN (2012) World Heritage Resource Manual: Managing Natural World Heritage. UNESCO, Paris Watts S (2016) Protection of the African lion: a critical analysis of the current international legal regime. PER 19:1–41 Williams VL, Loveridge AJ, Newton DJ, Macdonald DW (2015a) Traditional medicines: tiger-bone trade could threaten lions. Nature 523:290 Williams VL, Loveridge AJ, Newton DJ, Macdonald DW (2017a) Questionnaire survey of the pan-Afri- can trade in lion body parts. PLoS ONE 12:e0187060. https ://doi.org/10.1371/journ al.pone.01870 Williams VL, Loveridge AJ, Newton DJ, Macdonald DW (2017b) A roaring trade? The legal trade in Panthera leo bones from Africa to East-Southeast Asia. PLoS ONE 12:e0185996. https ://doi. org/10.1371/journ al.pone.01859 96 1 3 Biodivers Conserv (2018) 27:2747–2765 2765 Williams VL, Newton DJ, Loveridge AJ, Macdonald DW (2015b) Bones of Contention: An Assessment of the South African Trade in African Lion Panthera leo Bones and Other Body Parts. TRAFFIC, Cambridge, UK & WildCRU, Oxford Woodroffe R, Ginsberg JR (1998) Edge effects and the extinction of populations inside protected areas. Science 280:2126–2128. https ://doi.org/10.1126/scien ce.280.5372.2126 Links to legal documents CMS Res. 11.32 http://www.cms.int/sites /defau lt/files /docum ent/Res_11_32_Afric an_Lion_Panth era_ leo_E_1.pdf CMS Res. 11.33 http://www.cms.int/sites /defau lt/files /docum ent/Res_11_33_Guide lines _Asses sing_ Listi ng_Propo sals_E_0.pdf UNEP/CMS/COP12/Doc.25.1.3 2017 http://www.cms.int/sites /defau lt/files /docum ent/cms_cop12 _ doc.25.1.3_listi ng-propo sal-lion-appII -chad-niger -togo_e.pdf UNEP/CMS/COP12/Doc.25.1.8 http://www.cms.int/sites /defau lt/files /docum ent/cms_cop12 _doc.25.1.8_ listi ng-propo sal-p-horse -appI-mongo lia_e.pdf UNEP/CMS/COP12/Doc.24.3.1.1 http://www.cms.int/sites /defau lt/files /docum ent/cms_cop12 _ doc.24.3.1.1_afric an-carni vores -initi ative _e.pdf CITES Res. Conf. 10.14 (Rev. CoP16) (if this reference is retained in the insertion suggested above): https :// www.cites .org/sites /defau lt/files /docum ent/E-Res-10-14-R16.pdf 1 3 http://www.deepdyve.com/assets/images/DeepDyve-Logo-lg.png Biodiversity and Conservation Springer Journals

Improving the role of global conservation treaties in addressing contemporary threats to lions

Free
19 pages

Loading next page...
 
/lp/springer_journal/improving-the-role-of-global-conservation-treaties-in-addressing-XT04qAY0M6
Publisher
Springer Journals
Copyright
Copyright © 2018 by The Author(s)
Subject
Life Sciences; Biodiversity; Ecology; Conservation Biology/Ecology; Climate Change/Climate Change Impacts
ISSN
0960-3115
eISSN
1572-9710
D.O.I.
10.1007/s10531-018-1567-1
Publisher site
See Article on Publisher Site

Abstract

Biodivers Conserv (2018) 27:2747–2765 https://doi.org/10.1007/s10531-018-1567-1 ORIGINAL PAPER Improving the role of global conservation treaties in addressing contemporary threats to lions 1 2 1 1 Timothy Hodgetts  · Melissa Lewis  · Hans Bauer  · Dawn Burnham  · 1 1 1 2 Amy Dickman  · Ewan Macdonald  · David Macdonald  · Arie Trouwborst Received: 3 January 2018 / Revised: 17 March 2018 / Accepted: 23 May 2018 / Published online: 2 June 2018 © The Author(s) 2018 Abstract Despite their iconic status, lion (Panthera leo) populations continue to decline across the majority of their range. In the light of the recent decision (in October 2017) to add lions to the Appendices of the Convention on Migratory Species (CMS), this paper identifies the new and existing legal protections afforded to lions through five global trea - ties, and maps these protections against the most critical contemporary threats facing the species. It thus offers a new analysis of the CMS listing, and draws on existing legal reviews, to highlight the ways in which global treaties offer differing forms of protection for lions. It then combines multiple concordant assessments of lion populations, to highlight nine categories of threat: human-lion conflict, bushmeat poaching, human encroachment, trophy hunting, trade in lion bones, unpredictable environmental events, socio-economic factors, policy failures, and governance/institutional weakness. The paper assesses how the various treaties each address these different categories of threat. The analysis identifies two pathways for improving legal protection: expanding the application of global treaties in respect of lions and their habitats (the paper considers the CMS listing in these terms), and improving the implementation of treaty commitments through local and national-scale actions. Furthermore, it identifies local implementation challenges that include the local knowledge of rules, compliance with rules and enforcement capacity, alongside the variety in local contexts and situations, and suggests where global treaties might provide support in meeting these challenges. We suggest that this analysis has wider implications for how treaty protection can and is utilised to protect various species of large-bodied, wide-rang- ing animals. Communicated by David Hawksworth. This article belongs to the Topical Collection: Biodiversity legal instruments and regulations. * Timothy Hodgetts timothy.hodgetts@zoo.ox.ac.uk Wildlife Conservation Research Unit (Panthera et al.), University of Oxford, Tubney, UK Department of European and International Public Law, Tilburg University, Tilburg, The Netherlands 1 3 2748 Biodivers Conserv (2018) 27:2747–2765 Keywords International law · Treaties · Panthera leo · Threats · Implementation · Reform Introduction After a ground-breaking Conference of the Parties (COP) in Manila in October 2017, the lion (Panthera leo) (among 34 species, including leopards (Panthera pardus)) was added to the Appendices of the Convention on Migratory Species of Wild Animals (CMS), even though 4 range states opposed the listing, and several of these indicated their intention to enter reservations. This addition signals the need for states to develop a more elaborate and coordinated species-specific framework for lion conservation—and a first step towards achieving this was made through Parties’ decision to establish an African Carnivores Ini- tiative in collaboration with the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). In this paper, we consider how the CMS listing of lions (on Appendix II) combines with the existing international legal architecture for lion con- servation, to address the various threats that the species faces—and, importantly, where this architecture falls short, given the specific nature of those threats. We suggest that our analysis has wider relevance for mammalian wildlife (especially large carnivores), through identifying the various roles played by global treaties—and their omissions—in addressing the varied threats that endanger large animals. International treaties provide important frameworks for wildlife conservation worldwide (Bowman et al. 2010; Trouwborst et al. 2017a), and markedly so for charismatic carnivores (Trouwborst 2015). For large carnivores their wide-ranging ecology, reliance on large prey species, and intersection with global trade networks often requires cross-border coopera- tion for effective conservation action (Ripple et al. 2014). Moreover, large carnivore spe- cies tend to attract significant attention from publics and politicians (Lorimer 2015; Mac- donald et  al. 2016) and have the potential to raise awareness for a wide range of other threatened species (Macdonald et al. 2017b). Yet collectively these species are in trouble despite their ecological and cultural importance (Ripple et al. 2014), and lions (Bauer et al. 2015) are no exception. Measuring population sizes accurately is notoriously difficult, but recent estimates for lions suggest that numbers have rapidly declined, with between 20,000 and 30,000 lions remaining across Africa (Bauer et  al. 2016). The conservation of lions also has an added dimension insofar as they are a geographically widely distributed spe- cies (albeit occupying a fraction of their historical range), and measures directed towards their conservation may result in various benefits to other species (Macdonald et al. 2012). Therefore, legal instruments designed to conserve lions may thus also cast a protective shadow over wider biodiversity. In this transdisciplinary paper we (a team of legal experts, conservation biologists and social scientists) draw on the findings of two reviews concerning lions and international law (Trouwborst et al. 2017c; Watts 2016), combined with our analysis of recent develop- ments under the CMS, to map global wildlife treaties against the various ecological and socio-political threats this species faces. We demonstrate that while the coverage of such treaties across lion range states is reassuring, the use of these treaties to address the current threats faced by lions is patchy at best—even before we consider the daunting practicalities of implementation, monitoring and enforcement. Of course, international treaties are only one lever within wider conservation strategies, and will not always be the most appropriate instruments for addressing specific threats. Furthermore, in this paper we limit our scope 1 3 Biodivers Conserv (2018) 27:2747–2765 2749 to the global treaties, and do not assess the roles played by regional agreements and proto- cols in various African contexts. Nevertheless, we suggest improvements are possible and worthwhile pursuing. We note two pathways to improve the contribution of international law to lion conservation: (i) adapting and expanding the application of existing treaties, recent examples of which are the listing of, and associated decisions regarding, lions by the CMS COP (Conference of the Parties) in 2017, and (ii) improving the local-level imple- mentation of treaties. The relevance of international treaties for lions All contemporary lion range states are contracting parties to three or more of the ‘Big 5’ global conservation treaties that—amongst other things—obligate, support, regulate and coordinate measures beneficial to lions and their prey and habitat, either directly or indi- rectly  (Fig.  1). These are: the Convention on Biological Diversity, the ‘Ramsar’ Conven- tion on Wetlands of International Importance, the World Heritage Convention, CITES, and the CMS. Below, we summarize the relevance of each global treaty for lions. There are also sev- eral relevant treaties with a more limited geographic scope, but they are not the subject of this analysis. These include the 1968 African Convention on the Conservation of Nature and Natural Resources (and the 2003 revision thereof); sub-regional instruments like the SADC Protocol on Wildlife Conservation and Law Enforcement; treaty-based regional entities like the Commission of Central African Forests (COMIFAC), the East African Community (EAC) and the Economic Community of West African States (ECOWAS); and treaties establishing transfrontier conservation areas across Africa. Some of the most rel- evant of these agreements are discussed in (Trouwborst et al. 2017c), which considered 33 Fig. 1 Lion range states’ participation in 5 global wildlife treaties. (Color figure online) 1 3 2750 Biodivers Conserv (2018) 27:2747–2765 lion range states, including countries where lions have either been present in recent history, or where there is speculation that they may continue to persist. Here we limit our analysis to known contemporary populations, as listed in the IUCN Red List (25 African states plus India). Convention on Biological Diversity (CBD), 1992 The CBD is a broad-ranging treaty. It is concerned with the conservation and sustainable use of biodiversity, and amongst other things includes general obligations to create pro- tected areas, support threatened species, and create biodiversity strategies and action plans. It has played an important role in gaining additional political support for furthering habitat protection, globally. However, the text of the CBD is, from a legal perspective, so broadly worded as to make the thresholds for compliance somewhat ambiguous (Trouwborst 2015). The CBD also provides a forum for capacity building, discussion, and norm-creation around global biodiversity issues. The resulting high level biodiversity strategies, and guid- ance documents on more specific issues, have clear relevance for lion conservation. For example, the CBD’s Aichi Biodiversity Targets set clear goals around conserving threat- ened species, and the Convention has played a leading role in developing recommendations on addressing the unsustainable taking of bushmeat. All contemporary lion range states are parties. Ramsar Wetlands Convention, 1971 The longstanding global wetlands convention provides a basis for lion conservation through requiring that parties formulate and implement their planning so as to promote the conservation of a specified list of wetland habitats of international importance (‘Ram- sar sites’) designated by individual contracting parties, and as far as possible promote the ‘wise use’ of all wetlands. Certain Ramsar sites are important habitats for lions, and for 24 sites (across 13 countries) their importance for lions (amongst other species) is part of the documentation justifying designation. Ramsar designation thus confers a layer of interna- tionally recognised protection for certain key wetland areas in addition to any other protec- tive designation the site may have (as a reserve, national park etc.), and the potential ben- efits of support provided under the Convention. All contemporary lion range states, except Angola and Ethiopia, are parties. World Heritage Convention (WHC), 1972 Similarly to Ramsar, some important lion habitat is protected through the WHC. Examples of large, iconic sites include the Serengeti National Park in Tanzania, and the Okavango Delta in Botswana. In total, 15 sites in the 25 contemporary lion range states cover over 1,30,000 km of lion range (Trouwborst et al. 2017c). In contrast to the Ramsar Convention, the list of sites designated under the WHC is determined centrally by the World Heritage Committee (consti- tuting a selection of parties on rotation), following nominations by the states in which these sites occur. Furthermore, the condition of World Heritage Sites is monitored: sites can be deemed ‘in danger’ (relevant to 4 of the 15 at present), and ultimately WHC status can be removed. Given the international prestige (and tourism) driven by WHC status, the threat of removal creates an enforcement mechanism that the Ramsar Convention largely lacks. Fur- thermore, the WHC, which is embedded within UNESCO, can provide technical support and 1 3 Biodivers Conserv (2018) 27:2747–2765 2751 guidance to improve the management of ‘at risk’ sites. All contemporary lion range states are parties. Convention on International Trade in Endangered Species (CITES), 1973 CITES is relevant to lion conservation with respect to trade in lion body parts and trophy hunt- ing. The treaty aims to prevent the over-exploitation of species, and works through regulating international trade in live animals, body parts and derivative products. Species that are threat- ened or at risk of becoming threatened and are (potentially) affected by international trade are listed in the Convention’s Appendices, with Appendix I species (species threatened with extinction which are, or may be, affected by trade) being subject to greater restrictions than those on Appendix II (species which might become threatened with extinction if trade is not regulated). Captive-bred animals from Appendix I species are treated as Appendix II—which has been an important consideration in recent discussions around lions. At present, African lions are listed on Appendix II, with the Indian population on Appendix I. There have been two recent proposals from some lion range states to ‘uplist’ all lions to Appendix I, by Kenya in 2004 and by nine states from West and Central Africa ahead of the 2016 CITES COP. How- ever, this is an area of contention amongst lion range states, particularly due to the possible impact of uplisting on trophy hunting, although it is possible for some trophy hunting to con- tinue under an Appendix I listing. Notably, CITES’ ban on the international trade of Appendix I species applies only to specimens which, once imported, would be used for “primarily com- mercial purposes”, and the Convention additionally allows exemptions from its ordinary pro- visions for specimens which constitute “personal or household effects”. Under certain com- plex, and strictly limited, conditions it is therefore possible for some international movement of hunting trophies to continue under an Appendix I listing (as an example, see CITES Res. Conf. 10.14 (Rev. CoP16) on hunting trophies for leopards). While the COP negotiations did not ultimately result in a new Appendix I status for all lions, the meeting did agree on a new ‘annotation’ to the Appendix II listing for African lions which effectively prohibited international trade in most types of lion body parts from wild populations, although allowing regulated, quota-controlled trade for body parts deriving from captive-bred lions. Annotations are used to define the scope of a species’ inclusion on one of the CITES Appendices and can (as was the case for the lion) result in an Appendix II species being subject to more stringent trade restrictions than are ordinarily attached to this Appendix. The COP also adopted resolutions about trophy hunting (suggesting sustainable and well- managed activities can contribute to species conservation) and demand reduction strategies to address illegal wildlife trade, as well as several decisions on the African lion concerning the broader lion conservation agenda (addressing joint conservation planning, capacity building, research and education, among other things). All contemporary lion range states are currently parties to CITES, with the exception of South Sudan, which in any event participated as a non-party in the most recent CITES COP. The Convention has developed various mechanisms to facilitate and, if need be, compel compliance—including through the imposition of trade sanctions. Convention on Migratory Species of Wild Animals (Bonn Convention, CMS), The CMS, which is administered by the United Nations Environment Programme (UNEP), applies predominantly to ‘migratory species’, which are defined as those species where 1 3 2752 Biodivers Conserv (2018) 27:2747–2765 a ‘significant proportion’ of their members ‘cyclically and predictably cross one or more national jurisdictional boundaries’. The CMS COP has taken a remarkably flexible approach to interpreting this term, accepting that ‘cyclically’ ‘relates to a cycle of any nature, such as astronomical (circadian, annual etc.), life or climatic, and of any frequency’, and that ‘predictably’ ‘implies that a phenomenon can be anticipated to recur in a given set of circumstances, though not necessarily regularly in time’ (Res. 11.33). Depending on their conservation status, species which satisfy this definition can be listed on either (or both) of two appendices. The Convention identifies concrete conservation measures that parties must take in respect of the endangered migratory species listed in Appendix I— with ‘endangered’ being interpreted as meaning ‘facing a very high risk of extinction in the wild in the near future’, and as primarily encompassing species with an EW, CE or EN sta- tus on the IUCN Red List (Res. 11.33). Controversially, the measures required in respect of Appendix I-listed species include prohibiting the deliberate killing of these species, subject to limited exceptions. Such exceptions must be precise as to content and limited in space and time, should ‘not operate to the disadvantage of the species’, and may be made only (a) for scientific purposes, (b) for purposes of ‘enhancing the propagation or survival’ of the species, (c) to ‘accommodate the needs of traditional subsistence users’ of the species, or (d) if ‘extraordinary circumstances so require’, (CMS, Article III(5)). The Convention also provides a framework for developing tailor-made mechanisms to support the conservation of specific species/groups of species—including the migratory species listed on Appendix II (the emphasis of this appendix being on migratory species with an unfavourable con- servation status which require international cooperation for their conservation and man- agement), as well as any species whose members periodically cross international borders. Such mechanisms may take a variety of forms, ranging from legally binding ancillary trea- ties to non-binding Memoranda of Understanding, ‘Concerted Actions’, International Spe- cies Action Plans and ‘Special Species Initiatives’. Although their use is not restricted to listed species, listing arguably increases the likelihood that a species will receive attention under the Convention by raising its profile and providing a clear mandate to the CMS Sec- retariat to dedicate time and resources to supporting its conservation. In 2014, the 11th CMS COP recognized that lions are ‘migratory’ for the purposes of the Convention (Res. 11.32); and at the following meeting of the COP, in Manila in October 2017, a decision was made to add lions to Appendix II of the treaty. Basing their arguments on home range utilization, dispersal, movements following herbivore migrations, and movements as a result of annual climatic conditions, the proponents of the listing (Chad, Niger and Togo) asserted that the lion’s transboundary move- ments are sufficiently cyclical and predictable for the purposes of listing. They further identified countries sharing lion populations suspected to cyclically and predictably traverse national boundaries, such that a significant portion of lions could be consid- ered ‘migratory’ for CMS purposes (UNEP/CMS/COP12/Doc.25.1.3 2017). Despite earlier consensus (Res. 11.32), this argument became controversial, and four parties (South Africa, Tanzania, Uganda and Zimbabwe) opposed the listing, arguing, inter alia, that transborder movements do not necessarily equate to migration and that the lion’s movements fail to satisfy all elements of the Convention’s definition of ‘migra- tory species’. Ultimately, the matter had to be decided by vote, this being the first vote on a species’ listing in the history of the Convention. The listing was adopted by a large majority of the parties present and voting, with only the aforementioned four states voting against. Notably, the text of Resolution 11.33 was reconsidered at the 2017 COP, but its interpretation of ‘migratory species’ remained unchanged. To the extent that arguments exist for modifying the Convention’s flexible approach to listing, 1 3 Biodivers Conserv (2018) 27:2747–2765 2753 it would (for the sake of consistency) appear to be more appropriate to raise these in the context of a general discussion on whether to revise this Resolution than in dis- cussions over whether or not to list individual species that happen to be of political interest. To date, however, such a discussion has not emerged. The majority of listing proposals have been adopted without contention (indeed, there are instances in which species considerably less migratory than lions have been listed without debate), with the agreed interpretation of ‘migratory species’ tending only to be questioned when high-profile listings are at stake. In the absence of a broader discussion of Resolu- tion 11.33, each listing of a species that is transboundary but does not migrate in the classical sense adds weight to future arguments that the Convention’s appendices are not reserved exclusively for species that engage in predictable annual migrations. The lion’s listing is especially significant in this regard insofar as the majority of CMS par - ties were willing to explicitly endorse a flexible approach, even when confronted with fierce arguments against it. Although the CMS allows for listing to be applied selectively at the level of geo- graphically separate populations, it is significant that the proponents of the lion’s Appendix II listing were not prepared to exclude the lion populations of South Africa, Tanzania, Uganda and Zimbabwe, which are not biologically distinct from contiguous populations. Indeed, such an exclusion of parts of populations using ecologically arbi- trary boundaries—international frontiers between countries—would have been con- trary to the spirit of the Convention and would have set a bad precedent for future list- ing decisions. It is further notable that the CMS definition of ‘migratory species’ only applies to wild animals, and thus has no application to captive populations. Several lion populations are intensively managed and some were reintroduced after local extirpation (e.g. Akagera in Rwanda); South Africa distinguishes ‘wild’, ‘wild managed’ and ‘cap- tive’ populations (Bauer et  al. 2016; Funston and Levendal 2014; Miller et  al. 2013). Although CMS listing would exclude captive populations, all other populations would putatively be included—a precedent for this being established when Przewalski’s horse (Equus ferus przewalskii) was listed without any reference to it having been extinct in the wild for several decades and then reintroduced, using captive individuals, and man- aged (UNEP/CMS/COP12/Doc.25.1.8). In addition to listing the lion on Appendix II, the 2017 CMS COP adopted several decisions on this species (which corresponded to the decisions adopted at the most recent CITES COP) and agreed on the establishment of a joint CMS-CITES African Carnivores Initiative to support the implementation of resolutions and decisions on lions, leopards, cheetahs (Acinonyx jubatus) and wild dogs (Lycaon pictus) under both treaties (CMS 2017). Theoretically, the Initiative could ultimately pave the way for the development of a more formal arrangement, such as a carnivore-focused treaty. How- ever, this is unlikely in the foreseeable future, given the Convention’s recent shift away from the costly development of new legal and administrative frameworks in an attempt to channel more resources directly into implementation support. Notably, range states which are not parties to the CMS can still choose to participate in ancillary instruments, action plans and initiatives. Two existing multi-species CMS Concerted Actions are likely to become relevant to lions (Central Eurasian Aridland Mammals, Sahelo-Saha- ran Megafauna) and a third has been mooted as a possibility (Sub-Saharan Megafauna). The lion population in India could also potentially be included in the Convention’s Cen- tral Asian Mammals Initiative. The majority of lion range states are parties to the CMS, exceptions are: Botswana, Central African Republic, Malawi, Namibia, South Sudan, Sudan and Zambia. 1 3 2754 Biodivers Conserv (2018) 27:2747–2765 Assessing cumulative coverage of global treaties Global treaties thus support the conservation of contemporary populations of lions in vari- ous ways. Furthermore, the majority of lion range states are parties to the treaties—all for the CBD and the WHC, all except South Sudan for CITES and all except Angola and Ethi- opia for the Ramsar Convention. Even the CMS, which has the lowest level of coverage, still has 17 of 25 lion range states as parties (accounting for 80% of the estimated contem- porary lion species population). Mapping the contributions of global conservation treaties against contemporary threats The various forms of legal protection conferred through global treaties apply to the major- ity of lion range states and extant lion populations. However, they presently do not com- prehensively and directly address the most critical threats facing lions in Africa (99% of the worldwide population). We rely on three recent sources to collate threats to lions: (i) the Communiqué from the May 2016 CMS-CITES hosted meeting of African lion range states in Entebbe, (ii) a recent report on Africa’s lions published by Panthera, WildAid and the WildCRU, Oxford (Panthera et  al. 2016), and (iii) the IUCN’s Red List assessments (Bauer et  al. 2016; Breitenmoser et  al. 2008). Our synthesis of these three sources is in close accord with other recent assessments (Lindsey et al. 2017). The full list of threats is summarized in Table 1, with the relevance of each treaty noted for each threat. Whilst these threats vary in their severity for different regions and sub-populations, the summary herein is for lions in the aggregate. The most pressing issues facing African lions are human-lion conflict leading to retaliatory or pre-emptive killing, and bushmeat poaching leading to prey depletion: these threats are ranked as critical in the Panthera-led report, followed by human encroachment which is ranked as a high threat (Panthera et al. 2016). At present, these issues are addressed by global treaties only to a modest extent. The CBD provides a general requirement and platform to address these threats. In addition, the Ramsar and World Heritage Conventions require and facilitate addressing these threats for cer- tain designated sites. Both the CBD and CITES COPs have also adopted resolutions on the issue of bushmeat hunting, and the 2017 CMS COP adopted several decisions to address the unsustainable use of bushmeat (‘wild meat’, in CMS parlance). While the various convention texts do not address human-wildlife conflict specifically, a con- siderable body of guidance has been developed on the issue by the various COPs, in documents that are not themselves legally binding but can nevertheless influence the interpretation and application of the binding treaty provisions (also known as ‘soft law’). More importantly, they also address some of the causes (e.g., regulating live- stock access to protected areas) and some symptoms (e.g., the indiscriminate killing of lions). However, given the urgency of the threats, and the failure to address them at present, it is worth considering the additional roles global treaties might play. As dis- cussed above, the recent listing of lions in Appendix II of the CMS has created a legal framework through which a variety of actions might be taken that could focus specifi- cally on these issues, and could coordinate action across the remaining range states. We note the significant potential of the CMS-CITES African Carnivores Initiative in 1 3 Biodivers Conserv (2018) 27:2747–2765 2755 1 3 Table 1 Summary of how global treaties address threats to lions Threats Severity of threat Treaty Relevance Human-lion conflict (retaliatory and pre-emptive kill- Critical CBD Provides general requirement and platform to address threat ing) [i,ii,iii] RAMSAR Requires and facilitates addressing threat for certain wetlands WHC Requires and facilitates addressing threat for certain sites CMS Provides species-specific platform for coordination and targeted action CITES Provides species-specific platform for coordination and targeted action Bushmeat poaching (prey depletion) [i,ii,iii] Critical CITES Requires and facilitates regulation of international bushmeat trade CBD Provides general requirement and platform to address threat RAMSAR Requires and facilitates addressing threat for certain wetlands WHC Requires and facilitates addressing threat for certain sites CMS Provides species-specific platform for coordination and targeted action Human encroachment/habitat degradation [i,ii,iii] High CBD Provides general requirement and platform to address threat RAMSAR Requires and facilitates addressing threat for certain wetlands WHC Requires and facilitates addressing threat for certain sites CMS Provides species-specific platform for coordination and targeted action Poorly regulated trophy hunting [ii,iii] Medium CITES Regulates international movements of trophies CBD Provides general requirement and platform to ensure sustainability RAMSAR Requires ensuring sustainability of hunting for certain wetlands WHC Requires ensuring sustainability of hunting for certain sites CMS Provides species-specific platform for coordination and targeted action Trade in lion bones [i,ii,iii] Unknown CITES Regulates international trade (currently prohibited, except captive-bred) CBD Provides general requirement to promote sustainability of hunting RAMSAR Requires avoiding harmful impact for certain wetlands WHC Requires avoiding harmful impact for certain sites CMS Provides species-specific platform for coordination and targeted action 2756 Biodivers Conserv (2018) 27:2747–2765 1 3 Table 1 (continued) Threats Severity of threat Treaty Relevance Unpredictable events (e.g., floods) [iv] Not quantified CBD Provides general requirement to promote resilience RAMSAR Requires and facilitates ensuring resilience for certain wetlands WHC Requires and facilitates ensuring resilience for certain sites CMS Provides species-specific platform for coordination and targeted action Socio-economic factors [i] Not quantified CITES Requires and facilitates ensuring sustainability of trade CBD Requires and facilitates sustainable use RAMSAR Requires and facilitates wise use of wetlands WHC Requires and facilitates sustainable use of natural heritage CMS Provides species-specific platform for coordination and targeted action Policy failure and political factors [i] Not quantified CITES Provides platform for coordination regarding international trade CBD Provides general platform for coordination RAMSAR Provides platform for coordination regarding wetlands WHC Provides platform for coordination regarding natural heritage CMS Provides species-specific platform for coordination and targeted action Governance and institutional weakness [i] Not quantified CITES Promotes capacity-building regarding international trade CBD Promotes capacity-building regarding biodiversity generally RAMSAR Promotes capacity-building regarding wetlands WHC Promotes capacity-building regarding natural heritage CMS Provides species-specific platform for capacity-building Sources for threat analysis given below. ‘Severity of threat’ from Panthera et al. (2016) (i) The Entebbe Communiqué from the May 2016 CMS-CITES hosted meeting of African Range States. (ii) Panthera et al. (2016), (iii) Bauer et al. IUCN (2016), (iv) Bre- itenmoser et al. IUCN (2008) Biodivers Conserv (2018) 27:2747–2765 2757 this regard, with a substantial part of the Initiative’s envisaged budget earmarked for promoting human-carnivore coexistence (UNEP/CMS/COP12/Doc.24.3.1.1). That such frameworks might be accessible to non-party range states (see earlier discussion) adds significantly to their potential. The other threats to lions are addressed more directly by global treaties. Habitats gain a degree of legal protection from human encroachment and resulting degradation through the international designation of certain areas (with accompanying conserva- tion benefits) under the auspices of the WHC and Ramsar, and the broadly-phrased CBD commitment to establish protected areas and to protect endangered species and habitats. However, the continuing severity of the threats to lion habitat (Riggio et  al. 2013) raises important questions as to the scope of such ‘generalist’ (i.e., not species- specific) treaties, and the procedures and mechanisms by which enforcement of treaty provisions might occur (Trouwborst et  al. 2017c). Both the international movement of hunting trophies and trade in lion bones are addressed directly by CITES, although important debates and discussions continue as to whether the current arrangements (summarized earlier) are effective (see discussion). Stochastic events such as floods and fires can pose a threat to lions in small, geographically restricted populations, and remain a significant threat for the population of lions in India (Breitenmoser et al. 2008); again, the indirect support for protected areas provided by treaties is relevant here, as is the CMS objective of maintaining unfragmented, more robust and resil- ient transboundary populations. The Entebbe Communiqué also recognized a series of socio-political threats relating to governance, policy, and economic issues that combine to limit the efficacy of lion conservation. The various global treaties are par - ticularly important when it comes to policy formulation and capacity building in this respect. The bureaucracies of the various treaties, grounded inter alia in UNEP and UNESCO, hold significant potential as regards institutional support and coordination for lion conservation. As many species besides lions are covered by the various global wildlife treaties, some of which face similar threats to lions, several aspects of the preceding analysis concerning these treaties will also apply to their actual or potential roles with regard to such species, particularly other large carnivores (Trouwborst 2015). Discussion Becoming a party to international treaties is an important way that lion range states can signal their commitment to manage their wildlife populations sustainably, and the publicity around these treaties raises much-needed global awareness of the plight of lions and other species. However, despite the widespread applicability of global trea- ties across lion range, lions have continued to decline calamitously: across Africa, their numbers have approximately halved in the past 20 years, and they have been extirpated from over 90% of their historic range (Bauer et al. 2016). Clearly, therefore, there is a pressing need to improve the performance of international treaties in terms of effective lion conservation. Here, we suggest two main ways that lion conservation could be improved under the global treaties discussed in this paper: (i) Adapt and expand the application of existing treaties 1 3 2758 Biodivers Conserv (2018) 27:2747–2765 (ii) Improve local-level implementation of treaties Adapt and expand the application of existing treaties First, existing treaties might be better utilised for lion conservation (Trouwborst 2015). The recent listing of lions in Appendix II of the CMS is an example. This listing raises the lion’s international legal profile whilst simultaneously providing bureaucratic capacity and a framework to support additional coordinated action by lion range states to address the most critical threats to the species. However, international agreement by itself will not be enough to combat prey depletion, and policing the killing of large carnivores is resource intensive and difficult (Critchlow et  al. 2016; Johnson et  al. 2016). Thus, a package of measures is needed that improves both the legal framework and local implementation and enforcement (see below). Another reform might involve CITES. There is an important debate occurring as to whether the current treatment of lions in CITES is optimal (Bauer et al. 2018; Trouwborst et  al. 2017c). Future actions planned by CITES, resulting from the 2016 COP17, include the creation of a Task Force on African Lions and the formulation and implementation of conservation strategies for the species, in collaboration with the CMS. Yet significant questions continue to revolve around whether allowing legal markets for megafauna body parts from captive populations is compatible with reducing demand for illegally-sourced body parts (Di Minin et al. 2015), whether controlling a chain of custody for legal products is practically feasible (Bennett 2015) and whether look-alike issues create insurmountable enforcement problems across species. The extent of trade in body parts of wild lions has been a cause of concern, and although initial expert surveys do not reveal it as a serious problem at present, it may become so in the future (Williams et  al. 2015a, b, 2017a, b). There is also continuing debate around the status of trophy hunting within lion conserva- tion, and whether it should be considered as a threat to wild populations or as a sustainable form of management and source of conservation finance (Di Minin et al. 2016; Macdonald et al. 2016, 2017a). Further ways to increase the utility of global wildlife treaties include the listing of additional sites of importance to lion conservation under the Ramsar and World Heritage Conventions (Trouwborst et  al. 2017c). It would also be beneficial to more fully utilise the support mechanisms associated with these Conventions to improve the management of currently designated sites, so that they can better conserve lion populations. Funding has been identified as a major issue in lion conservation (Lindsey et al. 2017; Packer et al. 2013); global treaties can mobilise funding but can also provide guidance and bureaucratic capacity in spending and administering it. This is not an easy task as, in practice, ‘improv- ing management’ involves complex social and ecological challenges. As an example, the Ngorongoro Conservation Area (NCA) is a World Heritage Site, and has received over US$270 000 in international assistance since its designation in 1979 (UNESCO 2015). The NCA has experienced intense human-lion conflict (associated with a rapidly grow - ing human population) and the lion population has declined substantially since the 1980s. There are mounting tensions regarding the management of the NCA, a multiple land-use conservation area where humans (mainly Maasai pastoralists), lions and other wildlife are intended to coexist. UNESCO and the IUCN conducted a reactive monitoring mis- sion there in 2008, noting that while a previous study stated that the area had a carrying capacity of 25 000 people with cattle, 67,000 people lived in the NCA by 2007 (UNESCO 2015). However, the Maasai were not involved in the carrying capacity study and contested 1 3 Biodivers Conserv (2018) 27:2747–2765 2759 the findings. Moreover, many of the Maasai in the area have given up their nomadic life- styles and are now dependent upon agriculture, but all forms of agriculture were banned in the NCA in 2007 (Ikanda and Packer 2008). The ban led to much antagonism amongst local residents, although it has been neither enforced nor managed. UNESCO’s World Her- itage Centre and the IUCN consider that enforcing the ban would be positive for conserva- tion of the site, but it would clearly affect the livelihoods of local people, especially as even the 25,000 estimate of carrying capacity involved some reliance upon agriculture. Conflicts between local Maasai communities and the NCA authorities are growing, particularly as residents feel disempowered. The World Heritage Centre and IUCN have made several rec- ommendations for action, including commissioning a new carrying capacity study explic- itly considering the needs of the local Maasai community, encouraging the voluntary relo- cation of immigrants, and increasing the active participation of local communities in the decision-making processes. Thus, international treaties and their bureaucratic apparatuses can play a role in improving local management, but doing so involves navigating these complex social and ecological considerations. Improve local‑level implementation of international treaties The value of international treaties for conservation is multifaceted (Trouwborst et  al. 2017a), but their impact remains limited where they are poorly implemented, for example due to corruption or other poor governance practices. The provisions of international trea- ties are often transposed into national legal systems through domestic laws and regulations. Treaties thus impose obligations on states, but it is up to those states to utilise or create national arrangements to meet their obligations. Many of the treaty obligations are broad rather than very specific, and the party involved is expected to do what works best, which includes striking the right balance between top-down legislation and bottom-up approaches (Redpath et al. 2017). Since the fates of lions are largely determined by the actions of resi- dent or nomadic people living alongside them, sensitively designed conservation strategies at both a national and sub-national level are vital to ensuring that the obligations of inter- national treaties are met, while ensuring that the rules are applicable and appropriate for the local people concerned. Conversely, implementation of treaties can be ineffective in a variety of ways, notably: if compliance with, awareness of or enforcement of national laws and regulations is lacking; if bottom-up conservation strategies fail to meet parties’ obliga- tions; and/or if parties’ national implementation laws and other conservation actions are themselves inadequate for complying with international obligations. For domestic measures to be effective in meeting treaty obligations, it is important that people understand the different legal categories for wildlife, and that there are effective management plans and communication strategies regarding the rules associated with those categories. In many lion range countries, some or all of those components are lacking. All too often local communities are entirely unacquainted with national laws or regulations protecting wildlife, as they are often disengaged from the legal and conservation discourse. For example, in Tanzania’s Ruaha landscape, which still supports the world’s second larg- est lion population but has extremely high rates of lion killing (Abade et  al. 2014), local people are usually completely unaware that lions are in decline, and are also largely una- ware of domestic laws designed to protect them (Dickman pers. obs.). In Mozambique, a country with 15% of remaining lion range, a study in Maputo Elephant Reserve found that 65% of people (82% of whom were dependent upon consumptive wildlife use) had never heard of the country’s new Forest and Wildlife Policy (Soto et  al. 2001). Moving outside of lion range states, a study in Madagascar revealed that less than half the local 1 3 2760 Biodivers Conserv (2018) 27:2747–2765 respondents were able to correctly classify species into their legal categories (Keane et al. 2011). This study further suggested that engaging people directly in natural resource man- agement can sensitise them to conservation laws, which is likely to have relevance in many lion areas, where those people living alongside lions are often marginalised and report very little engagement in any conservation activities (Dickman 2009). Furthermore, increasing local awareness of international requirements can result in enhanced support for conserva- tion measures. For instance, in a survey of the benefits associated with the designation of Ramsar sites in Africa, for some sites international designation had led to increased interest by local communities, the establishment of community patrols to reduce trespassing and poaching, and/or in a change of behaviour of site users (Gardner et al. 2008). Even when knowledge of locally applicable rules and regulations is apparent, these are frequently ignored. For example, Tanzania, which has 40% of the world’s remaining lions and over a quarter of remaining lion range, has severe human-lion conflict and very high rates of anthropogenic lion killing, with just one study documenting 35 lions killed around 3 small villages in less than 18  months (Dickman 2015). Lion killings in Tanzania often fulfil both a ritual role, to prove bravery, and a defensive one to reduce attacks on livestock or people (Dickman 2015; Ikanda and Packer 2008; Kissui 2008). While Tanzania banned ritual lion hunting in the 1970s, the country’s 2009 Wildlife Conservation Act (amended in 2013) permits people to kill lions and other wildlife in defence of human life or livestock; if people are aware of legal restrictions they are also aware of this loophole. Lions impose major costs on local people (Dickman 2009; Packer et al. 2005), so additional measures to reduce conflict are necessary. Much lion killing is centred around livestock losses, which are particularly devastating for traditional pastoralist societies, where cattle have high cul- tural as well as economic value. Unless international treaty obligations can be translated into more effective livestock protection, such threats will continue. However, lion killing often has multiple drivers, such as the cultural status that people get from killing lions, or the fact it can offer one of the few ways of generating wealth (usually through gifts of cattle from herders in thanks for removing a predator) or facilitating marriages, and this can generate sufficient social and economic benefits for lion killing to persist even in the near-absence of livestock attacks (Fitzherbert et al. 2014). Understanding these dynamics is fundamentally important to developing effective conservation strategies, and requires the involvement of local people to ascertain site-specific threats and determine which legal measures would be most effective at combating them. Engaging communities in decision- making and ownership of control mechanisms has led to proven success in some lion areas: in Namibia, enabling local people to own and control their wildlife has contributed to one of the few increasing national lion populations, while in areas of Kenya, Tanzania, Ethio- pia and Mozambique, locally-driven programmes where communities develop and enforce rules have proven relatively successful at reducing threats to lions (Fitzherbert et al. 2014; Gebresenbet et al. 2017; Hazzah et al. 2014; Redpath et al. 2017). It is important to note, therefore, that the involvement of local people, participatory approaches, poverty allevia- tion, awareness-raising and education have become increasingly central tenets of all the major conservation treaties, as reflected in COP decisions, strategies, allocation of funding, manuals and other technical guidance. Useful examples of the latter include the Ramsar Handbook on Participatory Skills (Ramsar Convention Secretariat 2010), the World Herit- age Resource Manual on Managing Natural World Heritage (UNESCO et  al. 2012), and the CBD Technical Series volume on livelihood alternatives for unsustainable bushmeat use (Secretariat of the Convention on Biological Diversity 2011). The efficacy of national measures taken to implement international commitments is also determined by the ability of range states to monitor and enforce the ensuing regulations, 1 3 Biodivers Conserv (2018) 27:2747–2765 2761 and on the quality of the laws and regulations themselves. Laws may be flouted due to a low probability of detecting illegal behaviour, particularly in countries which have lim- ited capacity within their wildlife agencies (Shanee 2012). Many wildlife crimes fail to be detected by the authorities; data from Zambia’s Luangwa Valley suggested that detec- tion rates of black rhinoceros (Diceros bicornis) and elephant (Loxodonta africana) poach- ing were too low to prevent declines (Leader-Williams and Milner-Gulland 1993), while a study across four countries by Akella and Cannon (2004) estimated that the risk of punish- ment for environmental crime was very low (below 1% in the two countries with reason- able estimates). This is supported by our experience in lion range countries: in Ruaha, over 90% of the documented lion killing events were detected by researchers, with authorities having very little capacity to monitor anthropogenic killing outside (and sometimes even within) protected areas (Dickman pers. obs.). Wildlife rangers often have little training, and commonly resort to lethal control as a first option for resolving human-lion conflict. Such methods tend to reinforce local attitudes assuming killing lions is the best way to man- age conflict, and thus frequently lead to additional subsequent lion killing (Dickman pers. obs.). In addition to compliance and enforcement, the parties’ national implementation laws must be fit for purpose in the first place. This is not always the case. For example, the central bureaucracy of CITES monitors the extent to which contracting parties’ national legislation (and related measures) are able to implement the treaty’s provisions, and this differs markedly between lion range states (CITES 2016). National-level implementation capacity is affected by a range of socio-political, economic and cultural factors that shape the efficacy of national and sub-national bureaucratic activities—what might be termed a nation’s ‘conservation likelihood’(Dickman et al. 2015). As a final example of implementation challenges, the proliferation of ‘paper parks’ which are not effectively funded, managed or enforced is well documented (Bruner et al. 2001). Furthermore, the efficacy of protected areas can be additionally compromised by changes in governance arrangements, including to the human activities allowed therein, the size of the area, or even the removal of protected status—trends termed ‘PADDD’ or protected area downgrading, downsizing and degazettement in the literature (Mascia and Pailler 2011), and of potential relevance in some lion range states (see www.paddd track er.org for details). Many lion range states have insufficient funds to effectively manage core protected areas (Lindsey et  al. 2017), so providing sufficient law enforcement resources and expanding effective wildlife conservation on human-dominated land is unlikely with- out significant additional investment. International treaties have the capacity to leverage additional funding for protected areas, as well as wider wildlife conservation, so could play a very valuable role in this regard. Yet even with the stricter monitoring and enforcement provisions of the WHC noted earlier, many natural World Heritage Sites are threatened by the ecological isolation caused by development outside their borders (Allan et  al. 2017). Such edge effects, including those relating to the pressures of human populations, are espe- cially relevant for lions given the threats (such as bushmeat hunting and human-lion con- flict) they currently face (Woodroffe and Ginsberg 1998). Furthermore, action beyond their boundaries is often necessary even if protected areas are well managed, and even though lions are increasingly limited to protected areas some range lies outside of reserves; Durant et al. (2017) actually demonstrated that survival of some species depends on non-protected land, including the cheetah and African wild dog that have most of their range outside reserves. Addressing local concerns and community practices is a complex undertaking that requires a multi-faceted conservation strategy (Redpath et al. 2017); but as discussed herein, global treaties may help when it comes to building capacity and developing guid- ance in these respects. 1 3 2762 Biodivers Conserv (2018) 27:2747–2765 Concluding observations When it comes to international law, like all forms of wildlife law, the details of interpre- tation matter (Epstein et  al. 2016; Trouwborst et  al. 2017b). So do the contextual spe- cificities of the range states to which treaty provisions apply: their politics, governance, bureaucratic capacity, histories, cultures, and socio-economic characteristics (Dickman et  al. 2015). The review of global treaties offered here is a high-level summary, and as such the intricacies of how each treaty has been and might be further utilised (or not) to address specific threats to lions in different regions and cultural contexts are not addressed in great detail (see Trouwborst et  al. 2017c). Furthermore, legal meas- ures, whether created through international treaties, national laws, local or community restrictions, are only ever a part of a broader set of measures within conservation. How- ever, even limiting the review to this high level, we have suggested several priorities for reform and practical pathways towards improving lion conservation. These are: expand- ing the application of global treaties in respect of lions and their habitats (with the recent CMS listing representing a potentially significant step in these terms), improving the local-level implementation of treaty commitments through participatory regulatory developments, and supporting implementation and enforcement capacity at national and local scales. In conclusion, even if their effective implementation is beset with practical challenges, global wildlife treaties have distinct contributions to make to lion conserva- tion, the importance of which is likely to increase rather than diminish in the foresee- able future. Acknowledgements TH is the Kadas Senior Research Fellow in Geopolitics at Worcester College, Oxford. AT acknowledges the support of the Netherlands Organization for Scientific Research, as part of the project Ius Carnivoris (Project No.: 452-13-014). EAM is the Rivington Winant Post-doctoral Fellow and AD the Kaplan Senior Research Fellow in Felid Conservation at Pembroke College. All the authors grate- fully acknowledge the support of grants to DWM from the Robertson Foundation and the Recanati-Kaplan Foundation and Panthera. We would like to thank Dan Parker and Guillaume Chapron (reviewers) for their helpful comments; any errors remain ours alone. Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 Inter- national License (http://creat iveco mmons .org/licen ses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. References Abade L, Macdonald DW, Dickman AJ (2014) Assessing the relative importance of landscape and hus- bandry factors in determining large carnivore depredation risk in Tanzania’s Ruaha landscape. Biol Cons 180:241–248. https ://doi.org/10.1016/j.bioco n.2014.10.005 Akella AS, Cannon JB (2004) Strengthening the weakest links: strategies for improving the enforcement of environmental laws globally. Center for Conservation and Government [Conservation International] Allan JR, Venter O, Maxwell S, Bertzky B, Jones K, Shi Y, Watson JEM (2017) Recent increases in human pressure and forest loss threaten many Natural World Heritage Sites. Biol Cons 206:47–55. https ://doi. org/10.1016/j.bioco n.2016.12.011 Bauer H et al (2015) Lion (Panthera leo) populations are declining rapidly across Africa, except in inten- sively managed areas. Proc Natl Acad Sci USA 112:14894–14899. https ://doi.org/10.1073/pnas.15006 Bauer H, Nowell K, Sillero-Zubiri C, Macdonald DW (2018) Lions in the modern arena of CITES. Conserv Lett. https ://doi.org/10.1111/conl.12444 1 3 Biodivers Conserv (2018) 27:2747–2765 2763 Bauer H, Packer C, Funston PF, Henschel P, Nowell K (2016) Panthera leo. The IUCN Red List of Threat- ened Species 2016. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T1595 1A799 29984 .en. Accessed 02 August 2016 Bennett EL (2015) Legal ivory trade in a corrupt world and its impact on African elephant populations. Conserv Biol 29:54–60. https ://doi.org/10.1111/cobi.12377 Bowman M, Davies PGG, Redgwell C, Lyster S (2010) Lyster’s international wildlife law, 2nd edn. Cambridge University Press, Cambridge Breitenmoser U, Mallon DP, Ahmad Khan J, Driscoll C (2008) Panthera leo ssp. persica. IUCN Red List Threatened Species. https ://doi.org/10.2305/IUCN.UK.2008.RLTS.T1595 2A532 7221.en Bruner AG, Gullison RE, Rice RE, da Fonseca GAB (2001) Effectiveness of Parks in Protecting Tropi- cal. Biodiv Sci 291:125–128. https ://doi.org/10.1126/scien ce.291.5501.125 CITES (2016) Status of CITES implementation legislation CMS (2017) Press release: momentum grows to save world’s migratory wildlife. http://www.cms.int/en/ news/press -relea se-momen tum-grows -save-world ’s-migra tory-wildl ife. Accessed 30 October 2017 Critchlow R et  al (2016) Improving law-enforcement effectiveness and efficiency in protected areas using ranger-collected monitoring data. Conserv Lett. https ://doi.org/10.1111/conl.12288 Di Minin E et al (2015) Identification of policies for a sustainable legal trade in rhinoceros horn based on population projection and socioeconomic models. Conserv Biol 29:545–555. https ://doi. org/10.1111/cobi.12412 Di Minin E, Leader-Williams N, Bradshaw CJA (2016) Banning trophy hunting will exacerbate biodi- versity loss. Trends Ecol Evol 31:99–102. https ://doi.org/10.1016/j.tree.2015.12.006 Dickman AJ (2009) Key determinants of conflict between people and wildlife, particularly large carni- vores, around Ruaha National Park, Tanzania. PhD, University College London Dickman AJ (2015) Large carnivores and conflict in Tanzania’s Ruaha landscape. In: Redpath SM, Gut- ierrez RJ, Wood KA, Young JC (eds) Conflicts in conservation: navigating towards solutions. Cam- bridge University Press, Cambridge, pp 30–32 Dickman AJ, Hinks AE, Macdonald EA, Burnham D, Macdonald DW (2015) Priorities for global felid conservation. Conserv Biol 29:854–864. https ://doi.org/10.1111/cobi.12494 Durant SM et al (2017) The global decline of cheetah Acinonyx jubatus and what it means for conserva- tion. Proc Natl Acad Sci USA 114:528–533. https ://doi.org/10.1073/pnas.16111 22114 Epstein Y, López-Bao JV, Chapron G (2016) A legal-ecological understanding of favorable conservation status for species in Europe. Conserv Lett 9:81–88. https ://doi.org/10.1111/conl.12200 Fitzherbert E, Caro T, Johnson PJ, Macdonald DW, Mulder MB (2014) From avengers to hunters: lever- aging collective action for the conservation of endangered lions. Biol Cons 174:84–92 Funston P, Levendal M (2014) Biodiversity Management Plan for the Lion (Panthera leo) in South Africa. Republic of South Africa Gardner RC, Connolly KD, Bamba A (2008) African wetlands of international importance: assess- ment of benefits associated with designations under the Ramsar Convention. Geo Int’l Envtl L Rev 21:257 Gebresenbet F, Baraki B, Yirga G, Sillero-Zubiri C, Bauer H (2017) A culture of tolerance: coexisting with large carnivores in the Kafa Highlands, Ethiopia. Oryx. https ://doi.org/10.1017/s0030 60531 60013 56 Hazzah L, Dolrenry S, Naughton L, Edwards CT, Mwebi O, Kearney F, Frank L (2014) Efficacy of two lion conservation programs in Maasailand, Kenya. Conserv Biol 28:851–860 Ikanda D, Packer C (2008) Ritual vs. retaliatory killing of African lions in the Ngorongoro Conservation Area, Tanzania. Endanger Species Res 6:67–74 Johnson A et al (2016) To protect or neglect? Design, monitoring, and evaluation of a law enforcement strategy to recover small populations of wild tigers and their prey. Biol Conserv 202:99–109. https ://doi.org/10.1016/j.bioco n.2016.08.018 Keane A, Ramarolahy AA, Jones JP, Milner-Gulland E (2011) Evidence for the effects of environmental engagement and education on knowledge of wildlife laws in Madagascar. Conserv Lett 4:55–63 Kissui B (2008) Livestock predation by lions, leopards, spotted hyenas and their vulnerability to retalia- tory killing in the Maasai steppe, Tanzania. Animal Conserv 11:422–432 Leader-Williams N, Milner-Gulland EJ (1993) Policies for the enforcement of wildlife laws: the balance between detection and penalties in Luangwa Valley, Zambia. Conserv Biol 7:611–617 Lindsey P et  al (2017) The performance of African protected areas for lions and their prey. Biol Cons 209:137–149 Lorimer J (2015) Wildlife in the Anthropocene: conservation after nature. University of Minnesota Press, Minneapolis 1 3 2764 Biodivers Conserv (2018) 27:2747–2765 Macdonald D, Loveridge A, Dickman A, Johnson P, Jacobsen K, du Preez B (2017a) Lions, trophy hunt- ing and beyond, known unknowns and why they matter. Mammal Rev. https ://doi.org/10.1111/ mam.12096 Macdonald DW, Burnham D, Hinks AE, Wrangham R (2012) A problem shared is a problem reduced: seeking efficiency in the conservation of felids and primates. Folia Primatol 83:171–215 Macdonald DW, Jacobsen KS, Burnham D, Johnson PJ, Loveridge AJ (2016) Cecil: a moment or a movement? Analysis of media coverage of the death of a lion, Panthera leo. Animals 6:26 Macdonald EA et  al (2017b) Identifying ambassador species for conservation marketing. Glob Ecol Conserv. https ://doi.org/10.1016/j.gecco .2017.11.006 Mascia MB, Pailler S (2011) Protected area downgrading, downsizing, and degazettement (PADDD) and its conservation implications. Conserv Lett 4:9–20. https ://doi.org/10.1111/j.1755- 263X.2010.00147 .x Miller S et  al (2013) Management of reintroduced lions in small, fenced reserves in South Africa: an assessment and guidelines, South African. J Wildl Res 43:138–154 Packer C, Ikanda D, Kissui B, Kushnir H (2005) Lion attacks on humans in Tanzania. Nature 436:927–928 Packer C et al (2013) Conserving large carnivores: dollars and fence. Ecol Lett 16:635–641. https ://doi. org/10.1111/ele.12091 Panthera, WildAid, WildCRU (2016) Beyond Cecil: Africa’s Lions in Crisis Ramsar Convention Secretariat (2010) Participatory skills: establishing and strengthening local commu- nities’ and indigenous people’s participation in the management of wetlands. Ramsar Convention Secretariat, Gland Redpath SM et al (2017) Don’t forget to look down–collaborative approaches to predator conservation. Biol Rev 92:2157–2163 Riggio J et  al (2013) The size of savannah Africa: a lion’s (Panthera leo) view. Biodivers Conserv 22:17–35. https ://doi.org/10.1007/s1053 1-012-0381-4 Ripple WJ et  al (2014) Status and ecological effects of the world’s largest carnivores. Science. https :// doi.org/10.1126/scien ce.12414 84 Secretariat of the Convention on Biological Diversity (2011) Livelihood alternatives for the unsustain- able use of bushmeat. Secretariat of the CBD, Montreal Shanee N (2012) Trends in local wildlife hunting, trade and control in the Tropical Andes Biodiversity Hotspot, northeastern Peru. Endanger Species Res 19:177–186 Soto B, Munthali SM, Breen C (2001) Perceptions of the forestry and wildlife policy by the local com- munities living in the Maputo Elephant Reserve, Mozambique. Biodivers Conserv 10:1723–1738 Trouwborst A (2015) Global large carnivore conservation and international law. Biodivers Conserv 24:1567–1588. https ://doi.org/10.1007/s1053 1-015-0894-8 Trouwborst A et al (2017a) International wildlife law: understanding and enhancing its role in conserva- tion. Bioscience 67(9):784–790. https ://doi.org/10.1093/biosc i/bix08 6 Trouwborst A, Boitani L, Linnell JDC (2017b) Interpreting ‘favourable conservation status’ for large carnivores in Europe: how many are needed and how many are wanted? Biodivers Conserv 26:37– 61. https ://doi.org/10.1007/s1053 1-016-1238-z Trouwborst A et al (2017c) International law and lions (Panthera leo): understanding and improving the contribution of wildlife treaties to the conservation and sustainable use of an iconic carnivore. Nat Conserv 21:83–128. https ://doi.org/10.3897/natur econs ervat ion.21.13690 UNESCO (2015) State of Conservation: Ngorongoro Conservation Area. http://whc.unesc o.org/en/ soc/479. Accessed 26 July 2017 UNESCO, ICCROM, ICOMOS, IUCN (2012) World Heritage Resource Manual: Managing Natural World Heritage. UNESCO, Paris Watts S (2016) Protection of the African lion: a critical analysis of the current international legal regime. PER 19:1–41 Williams VL, Loveridge AJ, Newton DJ, Macdonald DW (2015a) Traditional medicines: tiger-bone trade could threaten lions. Nature 523:290 Williams VL, Loveridge AJ, Newton DJ, Macdonald DW (2017a) Questionnaire survey of the pan-Afri- can trade in lion body parts. PLoS ONE 12:e0187060. https ://doi.org/10.1371/journ al.pone.01870 Williams VL, Loveridge AJ, Newton DJ, Macdonald DW (2017b) A roaring trade? The legal trade in Panthera leo bones from Africa to East-Southeast Asia. PLoS ONE 12:e0185996. https ://doi. org/10.1371/journ al.pone.01859 96 1 3 Biodivers Conserv (2018) 27:2747–2765 2765 Williams VL, Newton DJ, Loveridge AJ, Macdonald DW (2015b) Bones of Contention: An Assessment of the South African Trade in African Lion Panthera leo Bones and Other Body Parts. TRAFFIC, Cambridge, UK & WildCRU, Oxford Woodroffe R, Ginsberg JR (1998) Edge effects and the extinction of populations inside protected areas. Science 280:2126–2128. https ://doi.org/10.1126/scien ce.280.5372.2126 Links to legal documents CMS Res. 11.32 http://www.cms.int/sites /defau lt/files /docum ent/Res_11_32_Afric an_Lion_Panth era_ leo_E_1.pdf CMS Res. 11.33 http://www.cms.int/sites /defau lt/files /docum ent/Res_11_33_Guide lines _Asses sing_ Listi ng_Propo sals_E_0.pdf UNEP/CMS/COP12/Doc.25.1.3 2017 http://www.cms.int/sites /defau lt/files /docum ent/cms_cop12 _ doc.25.1.3_listi ng-propo sal-lion-appII -chad-niger -togo_e.pdf UNEP/CMS/COP12/Doc.25.1.8 http://www.cms.int/sites /defau lt/files /docum ent/cms_cop12 _doc.25.1.8_ listi ng-propo sal-p-horse -appI-mongo lia_e.pdf UNEP/CMS/COP12/Doc.24.3.1.1 http://www.cms.int/sites /defau lt/files /docum ent/cms_cop12 _ doc.24.3.1.1_afric an-carni vores -initi ative _e.pdf CITES Res. Conf. 10.14 (Rev. CoP16) (if this reference is retained in the insertion suggested above): https :// www.cites .org/sites /defau lt/files /docum ent/E-Res-10-14-R16.pdf 1 3

Journal

Biodiversity and ConservationSpringer Journals

Published: Jun 2, 2018

References

You’re reading a free preview. Subscribe to read the entire article.


DeepDyve is your
personal research library

It’s your single place to instantly
discover and read the research
that matters to you.

Enjoy affordable access to
over 18 million articles from more than
15,000 peer-reviewed journals.

All for just $49/month

Explore the DeepDyve Library

Search

Query the DeepDyve database, plus search all of PubMed and Google Scholar seamlessly

Organize

Save any article or search result from DeepDyve, PubMed, and Google Scholar... all in one place.

Access

Get unlimited, online access to over 18 million full-text articles from more than 15,000 scientific journals.

Your journals are on DeepDyve

Read from thousands of the leading scholarly journals from SpringerNature, Elsevier, Wiley-Blackwell, Oxford University Press and more.

All the latest content is available, no embargo periods.

See the journals in your area

DeepDyve

Freelancer

DeepDyve

Pro

Price

FREE

$49/month
$360/year

Save searches from
Google Scholar,
PubMed

Create lists to
organize your research

Export lists, citations

Read DeepDyve articles

Abstract access only

Unlimited access to over
18 million full-text articles

Print

20 pages / month

PDF Discount

20% off