35
views
0
recommends
+1 Recommend
0 collections
    3
    shares
      • Record: found
      • Abstract: found
      • Article: found
      Is Open Access

      Real‐time anti‐poaching tags could help prevent imminent species extinctions

      research-article

      Read this article at

      Bookmark
          There is no author summary for this article yet. Authors can add summaries to their articles on ScienceOpen to make them more accessible to a non-specialist audience.

          Abstract

          Introduction At an estimated $7–10 billion annually, the global trade in illegal wildlife parts is comparable in economic value to human trafficking, and the smuggling of weapons and drugs (Wasser et al. 2008; Wyler & Sheikh 2013). Basic economic principles of supply and demand ensure that, as target species become ever rarer, their market value continues to rise, gradually pushing them towards extinction (Courchamp et al. 2006; Nowell 2012a). One particular problem is that anti‐poaching rangers often arrive too late at crime scenes to arrest criminals, making poaching a low‐risk and high‐gains enterprise (Wyler & Sheikh 2013). Here, we identify an opportunity to address this fundamental problem – we propose that cutting‐edge tracking technology could be harnessed to implement effective ‘real‐time poaching‐alert systems’. Animals would be fitted with miniature electronic devices (‘biologgers’) that can detect a poaching event, establish its exact location and relay data remotely to ground teams. Such systems should considerably increase the chances of successful interception, and thereby, escalate the actual and perceived risks of poaching, establishing a powerful new deterrent. In combination with other mitigation strategies (reviewed below), this innovative approach could lead to a much‐needed breakthrough in the increasingly desperate fight against wildlife crime. Almost gone While a wide range of species is targeted for illegal trading, we focus here on the poaching of large mammals, as these are often particularly vulnerable due to their naturally low population densities and reproductive rates. Three case studies serve to illustrate the urgency of implementing effective anti‐poaching measures (cf. Nowell 2012b), but our novel approach would no doubt benefit many other species. Rhinos are currently experiencing unprecedented poaching pressure (Fig. 1), with rates of one animal killed every 13 hours in some areas, and are fast heading towards wholesale extinction in the wild (Biggs et al. 2013). In fact, following a precipitous, poaching‐induced population crash in the 1960s (Emslie & Brooks 1999), the African western black rhino was declared extinct by the International Union for Conservation of Nature (IUCN) in 2011 (Biggs et al. 2013). As the price of ivory is rising, elephants fare little better and could be virtually extinct across most of their African range by 2020, unless poaching off‐take is considerably reduced (Wasser et al. 2008; see also Maisels et al. 2013). Finally, tigers are another group under extreme pressure (Nowell & Xu 2007; Walston et al. 2010), with three subspecies having already been lost in the last 70 years, and a lack of confirmed sightings from southern China likely signalling another extinction event (Tilson, Traylor‐Holzer & Jiang 1997). Figure 1 Real‐time poaching‐alert tags could prevent the imminent extinction of rhinos. (a) A black rhino Diceros bicornis bull in Damaraland, Namibia, home to one of the last free‐living populations of this critically endangered species; photograph: Tom Collier. Inset: real‐time poaching‐alert tags could be fitted inside rhinos’ horns (cf. Fig. 2). Here, a captive black rhino bull has been fitted with a miniature video camera during pilot trials carried out at Port Lympne Wild Animal Park, Kent, UK; photograph: Paul O'Donoghue. (b) A black rhino cow and calf feeding on Euphorbia, in Damaraland, Namibia. With its large horns, a mature individual like this is a prime target for poachers. The calf of the slaughtered mother would simply be left to die; photograph: Tom Collier. Mission impossible? Many anti‐poaching measures have been explored over the years (Sutherland 2008), including the following: environmental education programmes, to reduce demand for wildlife parts in East Asia (Lee & Tilbury 1998; Nowell & Xu 2007); legalization of high‐value products, such as ivory or rhino horn, to control trade dynamics (Gillson & Lindsay 2003; Martin et al. 2012; Biggs et al. 2013); targeted monitoring of money‐laundering activities, to hamper illegal trading (as highlighted by a recent international summit; Coghlan 2014); drastic in situ management of threatened animal populations, such as large‐scale dehorning of rhinos, to reduce poaching opportunities (Lindsey & Taylor 2011); and ‘militarization’ of nature reserves (Milliken & Shaw 2012; see below), to facilitate arrests and deter criminal activities. As we have illustrated above, however, illegal trade in wildlife products remains rife, and novel solutions are urgently needed. Our proposal aims at increasing the effectiveness of a widely used approach for protecting the most critically endangered species, the deployment of mobile, armed anti‐poaching units (Milliken & Shaw 2012). While these teams are often highly trained and well equipped, they generally have no way of knowing the exact time and location of poaching events. Since many target species are wide ranging and live in inaccessible habitats, this means that carcasses are often only found days or weeks after death (Martin 2001). As a result, arrests of poachers are rare and resources are mainly being focussed on securing evidence (Wasser et al. 2008), which is often insufficient for successful prosecution. Our proposed real‐time poaching‐alert systems would enable rangers to head towards crime scenes with rapid response times, substantially increasing the chances of apprehending suspects. In conjunction with legislation that ensures the severe punishment of convicted poachers, these altered risk dynamics should substantially reduce the economic attractiveness of poaching, giving heavily persecuted animal populations time to recover. In fact, even a temporary slowing of harvest rates would be valuable, as it would allow longer‐term measures – such as educational programmes – to deliver benefits. Smart electronics The rationale of our proposed biologging system is straightforward (for a schematic illustration, see Fig. 2, and for a summary of key challenges, see Table 1). Animals are fitted with miniature electronic tags that detect poaching events and transmit relevant information remotely to anti‐poaching units on the ground. In terms of technological implementation, the integration of a few existing, well‐tested components would enable an effective three‐step process for raising an alarm: detection –location – transmission/alert. Exact system specifications will depend on a wide range of factors, including the size, behaviour and habitat preferences of the species in question, as well as the availability of local infrastructure and other resources, but the following description outlines key principles. Table 1 Key challenges for developing real‐time poaching‐alert systems. See main text for possible solutions to some of these problems (a) Technological challenges Poaching sensor Sensors must trigger reliably, which requires extensive pre‐deployment testing; sensors must trigger quickly – detecting lack of motion alone (e.g. with old‐fashioned ‘jitter’ mortality switches) is insufficient, because of unacceptable time delays (see main text); some sensors (e.g. heart‐rate sensors) would require invasive procedures, such as (electrode) implantation, with possible effects on subjects’ welfare and on tagging speed (see below) ad hoc data generation and transmission Tags must generate (GPS) coordinate information and transmit alerts to satellites and/or ground receivers, before they can be destroyed by poachers; bandwidth is likely to be an issue and will necessitate data compression; where mobile phone networks are not available, dedicated infrastructure may need to be set up Battery power Tags’ batteries should last as long as possible, to minimize the need for retrapping subjects (see below) Tag attachment Tags must be attached to animals in a way that they are well concealed and achieve reliable sensor readings, without causing undue burden; invasive procedures (see above) will increase handling time, potentially hampering efforts of mass deployment (see below) (b) Other challenges Permits for deployment Some drone‐based projects experienced problems with obtaining permits for deployment; support of local authorities, and other stakeholder groups, is required System costs System costs should be minimized, to facilitate mass deployment Trapping effort A large proportion of animals must be (perceived to be) tagged, for establishing a successful deterrent function; this may be possible in small, extensively managed populations, but would be difficult in vast patrol areas; efforts of mass deployment would benefit from low system costs (see above) and straightforward deployment techniques (see above) Infrastructure requirements Anti‐poaching units must be able to reach remote crime scenes quickly, once an alert has been raised by a system; this will usually require the use of helicopters Sentencing of apprehended poachers Real‐time poaching‐alert systems can only become a major deterrent if they increase the chances of arresting poachers, and if arrests lead to successful prosecution and appropriate sentencing; local authorities need to ensure the latter John Wiley & Sons, Ltd Figure 2 Schematic illustration of the proposed real‐time poaching‐alert system. An electronic tag is fitted inside a rhino's horn (cf. Fig. 1). Multiple sensors continuously monitor the behaviour and physiology of the tagged animal, detecting when it is shot or otherwise badly injured [①]. Once a poaching event has been recorded, a GPS unit boots up to establish the exact location of the animal [②]. Information about the event is then transmitted via satellite uplink [③] to an anti‐poaching team that heads towards the crime scene by helicopter, in an effort to intercept the poacher(s). Meanwhile, after raising the alert, the horn‐mounted tag triggers a miniature camera, which transmits video evidence [④] until the rangers arrive. Graphic: Steve Thompson (http://stevethompsondesign.com/). A range of sensors could be used to detect when an animal is shot or trapped, including accelerometers or heart‐rate sensors (Rutz & Hays 2009; see Table 1). To avoid false alarms, sensors would require careful calibration before system deployment and could even be combined within a single tag, to enable redundant event‐triggering (i.e. multiple sensors must trigger before the tag raises an alarm) or remote validation – for example, an accelerometer could trigger an integrated video camera (Fig. 2; Rutz et al. 2007; Watanabe & Takahashi 2013) or microphone (Lynch et al. 2013). Once the tag's sensors have confirmed a poaching event, an on‐board GPS receiver is booted up (Tomkiewicz et al. 2010), to establish the position of the trapped, injured or dead animal. State‐of‐the‐art systems can estimate coordinates of suitable accuracy (within tens of metres) within split‐seconds, with minimal power requirements (e.g. Fastloc). In the final step, the tag communicates the event – that is, animal ID, trigger time, sensor readings and GPS coordinate information – to a mission control centre and/or directly to rangers in the field. This could be achieved through various routes, including satellite uplinks (e.g. Iridium), UHF transmission, or pre‐existing or ad hoc mobile phone networks. We estimate that a well‐designed system could raise an alarm within ca. 10 s, which in the majority of scenarios will be faster than poachers could reach the animal and destroy its tag. Anti‐poaching units often have helicopters at their disposal, ensuring that crime scenes could be reached within minutes, or tens of minutes, after receiving an alert (Fig. 2), even in vast and inaccessible patrol areas. Where helicopters are not available, reserves would at least be warned of ongoing poaching activity, enabling them to focus ranger resources spatially, patrol park perimeters and conduct targeted vehicle checks, greatly increasing the chances of apprehending poachers. The proposed technology should not be confused with standard satellite tracking, as routinely used with endangered species (e.g. Galanti et al. 2006). Although conventional GPS loggers could in principle be employed to infer poaching events from animals’ movement trajectories, costly time delays – to establish whether a stationary animal is merely resting or has indeed been injured or killed – would rule out their utility for guiding ad hoc intervention. Furthermore, constant sampling and relaying of positional data would quickly deplete batteries (in cases where solar power is not an option), which is not an issue with the ‘one‐shot’ tags we envisage here. Likewise, the marking of animals with PIT/RFID chips (Casey 2014), or with cutting‐edge life‐history tags (e.g. Horning & Mellish 2012), only enables the post hoc identification of mortalities, but cannot support a real‐time response, which lies at the heart of our proposal (for the use of real‐time ‘listening’ stations, to detect illegal logging, see Gross 2014). We can think of many ways to tailor system specifications to suit particular species or deployment contexts, or to extend basic system functionality. For example, event‐triggering could be combined very effectively with another anti‐poaching technology that is currently being developed – unmanned aerial systems, or ‘drones’ (Marks 2013, 2014; Casey 2014; Gross 2014; Mulero‐Pázmány et al. 2014). Rather than putting (tagged) animals under intermittent or constant drone surveillance, however, as currently planned, poaching‐alert tags could guide drones selectively to confirmed crime scenes, for collection of still‐image or video evidence until anti‐poaching units arrive on the ground. Such targeted monitoring should considerably increase the effectiveness of drone‐based projects, while reducing their logistical complexity and running costs. Practical considerations It is useful to explore briefly the practicalities of implementing our approach (cf. Table 1). Assuming that the engineering challenges of constructing suitable tags can be met, a key requirement is adequate tagging effort. Our approach aims at escalating the potential risks involved in committing poaching crimes, driving an unfavourable cost‐benefit ratio for poachers. This can only be achieved if a substantial proportion of local animal populations is marked with poaching‐alert tags or is at least being perceived to be marked, forcing poachers to take an increased risk, every time they pull the trigger or check a snare. It would of course be desirable if tags were difficult to see at a distance, because they are either very small or well hidden (e.g. in the horn of rhinos, or in ankle bracelets that cannot be seen in high grass; see Fig. 1), but where this is impossible (e.g. because tags need to be mounted on a collar, as with tigers), the strategic use of cheap dummy tags could considerably reduce programme costs (dummy tags are often used in biologging projects, to assess tagging effects; e.g. Bridger & Booth 2003). Trapping effort would admittedly pose significant challenges for large populations, but is unlikely to be an issue in those areas where intervention is most urgently needed: this is because critically endangered populations are often heavily managed, with large numbers of subjects being routinely trapped for ID marking (Ngene et al. 2011) and health checks. As with any new technology employed in antagonistic contexts, one particular concern is the possible development of counter measures. In our case, this could involve, for example, technology to jam tags’ two‐way communication with satellites. We think that such an ‘arms race’ is unlikely, at least in the short term, given the required levels of technological expertise, and the substantial costs involved, which would quickly diminish criminals’ profit margins. Quick action For two main reasons, we are surprised that real‐time poaching‐alert systems have not been implemented yet. First, the fight against most other types of crime heavily relies on the use of event‐triggered technology. While large‐scale CCTV surveillance, and regular police patrols, may lead to reductions in crime rates (e.g. Levitt 1997), the success of policing is no doubt dramatically enhanced by systems that raise alarms in real‐time and enable arrests at crime scenes. This includes house and car alarms, panic buttons and rape alarms, and perhaps most importantly, the victims’ ability in many circumstances to phone the police directly. We see no reason why this powerful route of ‘self‐reporting’ could not be emulated in the desperate fight against poaching crime. To our knowledge, this opportunity has so far been overlooked, despite increasing interest in technology‐driven approaches (see above). Secondly, over the last 10 years or so, significant advances have been made in biologging science, producing tags of unprecedented miniaturization, sophistication and integration (Rutz & Hays 2009) – while major engineering challenges lie ahead (see Table 1), the construction of real‐time poaching‐alert systems is well within reach of current expertise. We hope others will join us in our efforts to implement the ideas outlined in this essay. To start with, we invite biologging engineers – many of whom already have keen interests in conservation biology (Cooke 2008; Bograd et al. 2010) – to collaborate with us on system development, as free sharing of expertise and other resources will be essential to making rapid progress. But, success will also depend on support from wildlife biologists and ranger teams on the ground, and on the willingness of governments and other authorities to issue permits for system deployment, to facilitate the cross‐border pursuit of criminal suspects and to put in place robust legislation for the sentencing of convicted poachers (cf. Maisels et al. 2013; see Table 1). Given that many target species are fast heading towards extinction, we need to explore all available anti‐poaching tools with utmost urgency, aiming for intervention at every stage of the trade chain. While we are fully aware that our reactive, technology‐based approach does not provide an all‐encompassing solution, it should – through its contribution to improving arrest rates and establishing an effective deterrent – buy crucial time until longer‐term, preventive measures have gained sufficient traction. Author contributions PO initiated this collaboration; PO and CR conceived ideas; PO and CR conducted research; and CR drafted the manuscript, which was edited by PO and CR. Competing interests The authors have started developing prototype poaching‐alert tags, but do not intend to exploit the technology commercially. Data accessibility Data have not been archived because this article does not contain data. Biosketch Paul O'Donoghue is an applied ecologist with a PhD from the University of Sheffield. Through his work on black rhinos in Namibia and South Africa, he has gained considerable ‘front‐line’ experience of fighting poaching crime. Christian Rutz is an evolutionary ecologist with a DPhil from the University of Oxford. He uses cutting‐edge ‘biologging’ technologies extensively in his field projects and has pioneered the use of miniature video cameras and proximity loggers for studying wild birds. By pooling their diverse practical expertise, Paul and Christian hope to make a contribution to the development of innovative real‐time anti‐poaching tools.

          Related collections

          Most cited references17

          • Record: found
          • Abstract: found
          • Article: not found

          New frontiers in biologging science.

          The term 'biologging' refers to the use of miniaturized animal-attached tags for logging and/or relaying of data about an animal's movements, behaviour, physiology and/or environment. Biologging technology substantially extends our abilities to observe, and take measurements from, free-ranging, undisturbed subjects, providing much scope for advancing both basic and applied biological research. Here, we review highlights from the third international conference on biologging science, which was held in California, USA, from 1 to 5 September 2008. Over the last few years, considerable progress has been made with a range of recording technologies as well as with the management, visualization, integration and analysis of increasingly large and complex biologging datasets. Researchers use these techniques to study animal biology with an unprecedented level of detail and across the full range of ecological scales-from the split-second decision making of individuals to the long-term dynamics of populations, and even entire communities. We conclude our report by suggesting some directions for future research.
            Bookmark
            • Record: found
            • Abstract: found
            • Article: found
            Is Open Access

            Bringing the Tiger Back from the Brink—The Six Percent Solution

            The Tiger Summit, to be hosted by Prime Minister Vladimir Putin in Russia in November 2010—the Chinese Year of the Tiger and the International Year of Biodiversity—promises to be the most significant meeting ever held to discuss the fate of a single non-human species. The Summit will culminate efforts by the Global Tiger Initiative (GTI), launched in 2008 by Robert Zoellick, World Bank President. Leaders of 13 tiger range states, supported by international donors and conservationists attending the summit, are being asked to commit to substantive measures to prevent the unthinkable: extinction of the world's last wild tiger populations. Wild tiger numbers are at an historic low. There is no evidence of breeding populations of tigers in Cambodia, China, Vietnam, and DPR Korea. Current approaches to tiger conservation are not slowing the decline in tiger numbers [1]–[3], which has continued unabated over the last two decades. While the scale of the challenge is enormous, we submit that the complexity of effective implementation is not: commitments should shift to focus on protecting tigers at spatially well-defined priority sites, supported by proven best practices of law enforcement, wildlife management, and scientific monitoring. Conflict with local people needs to be mitigated. We argue that such a shift in emphasis would reverse the decline of wild tigers and do so in a rapid and cost-efficient manner. The Decline of the Tiger Despite a long history of concern for wild tigers, both their range and total number have collapsed: fewer than 3,500 animals now live in the wild, occupying less than 7% of their historical range [4]. Of these, approximately 1,000 are likely to be breeding females [5]. In most countries, overhunting has been the driver of the decline in tigers and their prey [6],[7]. Additionally, loss and fragmentation of habitat was locally important [8]. Nevertheless, beginning in the early 1970s, conservation initiatives helped establish a large number of tiger reserves, particularly in India, Nepal, and, to a lesser extent, in Thailand, Indonesia, and Russia. Probably the most successful of these, at least initially, was Project Tiger in India, which was launched in 1972 with the political support of Prime Minister Indira Ghandi. The apparent success of these reserves prompted, in the 1990s, many conservationists [4],[9],[10] (including some of the co-authors of this report) to shift their focus to a landscape approach, which sought to conserve tigers well beyond protected areas, so as to maintain the genetic and demographic viability of populations of this low-density, wide-ranging species. Conservation investments subsequently increased, but the array of activities was complex, less directly related to tigers, and spread thinly across large landscapes [11]. With hindsight, it also became clear that protection and management of many reserves remained inadequate (the extirpation of tigers in the Indian tiger reserves of Sariska, reported in 2004, and Panna, reported in 2010, is illustrative) and this, coupled with an increased demand for tiger parts [12], meant that poaching of tigers and prey decimated populations across Asia, both inside and outside reserves. Protecting Source Sites While approximately 1.5 million square kilometers of suitable habitat still remain in Asia ([9], Figure 1), tigers today are distributed heterogeneously [7],[13] and, except in the Russian Far East, are now restricted to small pockets, mostly in protected areas. The recent analysis ([13], Table S1) identified 42 “source sites,” so termed because these areas contain concentrations of tigers that have the potential to repopulate larger landscapes. Source sites were defined as having the potential to maintain >25 breeding females, being embedded in a larger landscape with the potential to contain >50 breeding females, having an existing conservation infrastructure, and having a legal mandate for protection (Text S1). These sites contain the majority of the world's remaining tigers. 10.1371/journal.pbio.1000485.g001 Figure 1 Location of 42 source sites, embedded within the larger tiger conservation landscapes (TCLs), areas that encompass the ecological habitats suitable for tigers. Strategies to save the tiger must focus first and foremost on protecting these remaining concentrations of tigers. These 42 sites contain almost 70% of all remaining wild tigers ([13], Table S1) so have a disproportionate importance to the survival and recovery of the species. Nevertheless, collectively they cover 80%) to their estimated carrying capacity [13]. Thus, the recovery of populations in source sites alone would result in a 70% increase in the world's tiger population. While recognizing that the long-term goal is to conserve an Asia-wide network of large, tiger-permeable landscapes, the immediate priority must be to ensure that the last remaining breeding populations are protected and continuously monitored. Without such protection, all other efforts are bound to fail. The similarly dramatic decline in African rhinoceros in the 1980s provides useful lessons on how best to respond to a decline in a species of high commercial value. Where conservation efforts were geographically diffuse, the cost–risk ratio greatly favored the illegal hunter [14]. Only where protection efforts either were focused on small- to medium-sized areas (e.g., Kenya's rhino sanctuaries), or were well financed (e.g., Kruger National Park), did rhinos persist [15]. While tigers have larger spatial requirements than rhinos, the challenge is the same. Actively protecting tigers at source sites is feasible and pragmatic, and has been demonstrably successful in many reserves across India between 1974 and 1986 [16]. The Malenad-Mysore tiger landscape currently maintains >220 adult tigers, one of the greatest concentrations in the world, mainly due to intensive protection of its source sites such as Nagarahole National Park, where tiger numbers have increased by 400% after protection began in the early 1970s [17],[18], and has now maintained a high density for 30 years ([19], unpublished data). Across India, tiger abundance is strongly correlated with prey density [20] and both depend on strict controls on hunting. The Tigers Forever program [21] has supported governmental protection effort, aided by MIST (Management Information SysTem) law enforcement monitoring [22], in Thailand, Lao PDR, and Malaysia, and hunting has been reduced and tiger populations stabilized. However, these results require greater levels of law enforcement, surveillance, and monitoring than typically is found in national protected areas. In the Russian Far East, traditionally a stronghold for tigers, annual monitoring detected a dramatic decline in tiger numbers over the last five years, which was associated with a decline in enforcement [23],[24]. Recent declines in tiger numbers in the once thriving source sites in Nepal were also associated with reduced emphasis on protection [25]. The Cost of Protection We assessed the costs of protecting source sites, including increased law enforcement, biological and law enforcement monitoring, and where appropriate, community engagement, informant networks, and trade monitoring. Costs were sourced, where possible, from those responsible for managing source sites such as protected area authorities, supplemented by published national government figures. Included costs were limited to those supporting the core activities of protection and monitoring of source sites. These include law enforcement, law enforcement monitoring, general management, and the monitoring of tigers and their prey. One-time conservation infrastructure development, and costs related to the relocation of communities within source sites, were not included in the analysis (Text S2). Protecting source sites is financially attainable. Our analysis [13] estimates the average cost of protecting and monitoring tigers effectively at all 42 source sites at $82 million per year or $930/km2 per year, within the range of effective protected area costs in general (from $130 to >$5,000/square kilometer/year for densely settled regions in Asia) [26]. More than half of these funds ($47 million, almost US$500/km2) is already being committed by range-state governments and, to a far lesser extent, international donors and NGOs. However, much of the total governmental financial commitment comes from and is spent in India. When India is excluded from the analysis, the average current commitment drops to US$365/km2 per year. This leaves an overall shortfall of US$35 million a year for all source sites. A Pragmatic Strategy While protecting source sites is essential to reverse tiger declines, this is but one element of a long-term recovery strategy. For wide-ranging, low-density species like the tiger, conservation planning at the landscape level is necessary, landscapes need to remain permeable to tiger movements, and source sites have to remain embedded in those larger landscapes. This will require strict limits on habitat conversion and infrastructure development. In addition, conservation efforts need to target the illegal trade, as site-based protection will be increasingly costly if the global demand for tiger products is not curtailed [27],[28]. All of this will require concerted, orchestrated and politically bold commitments by range-state governments, supported by the general public and the international community, and sustained over decades. However, with so few wild tigers remaining, almost entirely clustered in a few small areas, the most immediate need is to protect populations in the remaining source sites. For financially valuable species like the tiger, intensive protection is paramount, and the success of such protection has been demonstrated. Commitments made at the Russian Summit must refocus on the protection of source sites—a strategy that is financially realistic, politically feasible, and will deliver the greatest return on conservation investments. Only when we are able to stop the slide in tiger numbers at source sites will we be successful at managing tigers across the wider landscape. Supporting Information Table S1 Source sites listed by country. (0.07 MB XLS) Click here for additional data file. Text S1 Definition of source sites. (0.08 MB DOC) Click here for additional data file. Text S2 Estimating financial costs for effective protection and monitoring at source sites, and present expenditures. (0.06 MB DOC) Click here for additional data file.
              Bookmark
              • Record: found
              • Abstract: not found
              • Article: not found

              Biotelemetry and biologging in endangered species research and animal conservation: relevance to regional, national, and IUCN Red List threat assessments

              SJ Cooke (2008)
                Bookmark

                Author and article information

                Journal
                J Appl Ecol
                J Appl Ecol
                10.1111/(ISSN)1365-2664
                JPE
                The Journal of Applied Ecology
                John Wiley and Sons Inc. (Hoboken )
                0021-8901
                1365-2664
                February 2016
                24 July 2015
                : 53
                : 1 ( doiID: 10.1111/jpe.2016.53.issue-1 )
                : 5-10
                Affiliations
                [ 1 ] Faculty of Applied ScienceUniversity of Chester ChesterUK
                [ 2 ] School of BiologyUniversity of St Andrews St AndrewsUK
                Author notes
                [*] [* ]Correspondence author. E‐mail: christian.rutz@ 123456st-andrews.ac.uk
                [†]

                Both authors contributed equally to this work.

                Article
                JPE12452
                10.1111/1365-2664.12452
                4949716
                27478204
                4dcb83fa-7bde-4a2e-b7eb-08dd973b8a33
                © 2015 The Authors. Journal of Applied Ecology published by John Wiley & Sons Ltd on behalf of British Ecological Society

                This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.

                History
                : 22 August 2014
                : 24 April 2015
                Page count
                Pages: 6
                Funding
                Funded by: Biotechnology and Biological Sciences Research Council
                Award ID: BB/G023913/2
                Categories
                Practitioner's Perspective
                Practitioner's Perspective
                Custom metadata
                2.0
                jpe12452
                February 2016
                Converter:WILEY_ML3GV2_TO_NLMPMC version:4.9.2 mode:remove_FC converted:19.07.2016

                Ecology
                anti‐poaching measures,biologging,elephant,environmental education,illegal trade,ivory,poaching,rhino,tiger,wildlife crime

                Comments

                Comment on this article