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Dive into the research topics where James R. Allan is active.

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Featured researches published by James R. Allan.


Nature Communications | 2016

Sixteen years of change in the global terrestrial human footprint and implications for biodiversity conservation

Oscar Venter; Eric W. Sanderson; Ainhoa Magrach; James R. Allan; Jutta Beher; Kendall R. Jones; Hugh P. Possingham; William F. Laurance; Peter Wood; B M Fekete; Marc A. Levy; James E. M. Watson

Human pressures on the environment are changing spatially and temporally, with profound implications for the planets biodiversity and human economies. Here we use recently available data on infrastructure, land cover and human access into natural areas to construct a globally standardized measure of the cumulative human footprint on the terrestrial environment at 1u2009km2 resolution from 1993 to 2009. We note that while the human population has increased by 23% and the world economy has grown 153%, the human footprint has increased by just 9%. Still, 75% the planets land surface is experiencing measurable human pressures. Moreover, pressures are perversely intense, widespread and rapidly intensifying in places with high biodiversity. Encouragingly, we discover decreases in environmental pressures in the wealthiest countries and those with strong control of corruption. Clearly the human footprint on Earth is changing, yet there are still opportunities for conservation gains.


Scientific Data | 2016

Global terrestrial Human Footprint maps for 1993 and 2009.

Oscar Venter; Eric W. Sanderson; Ainhoa Magrach; James R. Allan; Jutta Beher; Kendall R. Jones; Hugh P. Possingham; William F. Laurance; Peter Wood; B M Fekete; Marc A. Levy; James E. M. Watson

Remotely-sensed and bottom-up survey information were compiled on eight variables measuring the direct and indirect human pressures on the environment globally in 1993 and 2009. This represents not only the most current information of its type, but also the first temporally-consistent set of Human Footprint maps. Data on human pressures were acquired or developed for: 1) built environments, 2) population density, 3) electric infrastructure, 4) crop lands, 5) pasture lands, 6) roads, 7) railways, and 8) navigable waterways. Pressures were then overlaid to create the standardized Human Footprint maps for all non-Antarctic land areas. A validation analysis using scored pressures from 3114×1u2009km2 random sample plots revealed strong agreement with the Human Footprint maps. We anticipate that the Human Footprint maps will find a range of uses as proxies for human disturbance of natural systems. The updated maps should provide an increased understanding of the human pressures that drive macro-ecological patterns, as well as for tracking environmental change and informing conservation science and application.


Conservation Biology | 2017

Developing a theory of change for a community-based response to illegal wildlife trade

Duan Biggs; Rosie Cooney; Dilys Roe; Holly T. Dublin; James R. Allan; Daniel W.S. Challender; Diane Skinner

The escalating illegal wildlife trade (IWT) is one of the most high-profile conservation challenges today. The crisis has attracted over US


Science | 2018

One-third of global protected land is under intense human pressure

Kendall R. Jones; Oscar Venter; Richard A. Fuller; James R. Allan; Sean L. Maxwell; Pablo Jose Negret; James E. M. Watson

350 million in donor and government funding in recent years, primarily directed at increased enforcement. There is growing recognition among practitioners and policy makers of the need to engage rural communities that neighbor or live with wildlife as key partners in tackling IWT. However, a framework to guide such community engagement is lacking. We developed a theory of change (ToC) to guide policy makers, donors, and practitioners in partnering with communities to combat IWT. We identified 4 pathways for community-level actions: strengthen disincentives for illegal behavior, increase incentives for wildlife stewardship, decrease costs of living with wildlife, and support livelihoods that are not related to wildlife. To succeed the pathways, all require strengthening of enabling conditions, including capacity building, and of governance. Our ToC serves to guide actions to tackle IWT and to inform the evaluation of policies. Moreover, it can be used to foster dialogue among IWT stakeholders, from local communities to governments and international donors, to develop a more effective, holistic, and sustainable community-based response to the IWT crisis.


Conservation Biology | 2017

Need for conservation planning in postconflict Colombia

Pablo Jose Negret; James R. Allan; Alexander R. Braczkowski; Martine Maron; James E. M. Watson

Protected yet pressured Protected areas are increasingly recognized as an essential way to safeguard biodiversity. Although the percentage of land included in the global protected area network has increased from 9 to 15%, Jones et al. found that a third of this area is influenced by intensive human activity. Thus, even landscapes that are protected are experiencing some human pressure, with only the most remote northern regions remaining almost untouched. Science, this issue p. 788 Human pressure is present in a third of the land designated as protected, globally. In an era of massive biodiversity loss, the greatest conservation success story has been the growth of protected land globally. Protected areas are the primary defense against biodiversity loss, but extensive human activity within their boundaries can undermine this. Using the most comprehensive global map of human pressure, we show that 6 million square kilometers (32.8%) of protected land is under intense human pressure. For protected areas designated before the Convention on Biological Diversity was ratified in 1992, 55% have since experienced human pressure increases. These increases were lowest in large, strict protected areas, showing that they are potentially effective, at least in some nations. Transparent reporting on human pressure within protected areas is now critical, as are global targets aimed at efforts required to halt biodiversity loss.


Emu | 2016

The distribution and protection of intertidal habitats in Australia

Kiran L. Dhanjal-Adams; Jeffrey O. Hanson; Nicholas J. Murray; Stuart R. Phinn; Vladimir R. Wingate; Karen Mustin; Jasmine R. Lee; James R. Allan; Jessica L. Cappadonna; Colin E. Studds; Robert S. Clemens; Chris Roelfsema; Richard A. Fuller

More than 80% of recent major armed conflicts have taken place in biodiversity hotspots, including the Tropical Andes which is home to the worlds highest concentrations of bird, mammal, and amphibian species, and more than ten percent of all vascular plant species (Mittermeier etxa0al. 2004; Hanson etxa0al. 2009). Armed conflicts not only seriously impact social and political systems, but also have important ramifications for biodiversity, from the time preparations for conflict start through to the post-conflict period (Machlis & Hanson 2008). Tropical forests have been identified as particularly vulnerable during the post-conflict period, when areas made inaccessible during hostilities become open to development (McNeely 2003). This article is protected by copyright. All rights reserved.


Scientific Data | 2017

Temporally inter-comparable maps of terrestrial wilderness and the Last of the Wild

James R. Allan; Oscar Venter; James E. M. Watson

Abstract Shorebirds have declined severely across the East Asian—Australasian Flyway. Many species rely on intertidal habitats for foraging, yet the distribution and conservation status of these habitats across Australia remain poorly understood. Here, we utilised freely available satellite imagery to produce the first map of intertidal habitats across Australia. We estimated a minimum intertidal area of 9856 km2, with Queensland and Western Australia supporting the largest areas. Thirty-nine percent of intertidal habitats were protected in Australia, with some primarily within marine protected areas (e.g. Queensland) and others within terrestrial protected areas (e.g. Victoria). Three percent of all intertidal habitats were protected by both marine and terrestrial protected areas. To achieve conservation targets, protected area boundaries must align more accurately with intertidal habitats. Shorebirds use intertidal areas to forage and supratidal areas to roost, so a coordinated management approach is required to account for movement of birds between terrestrial and marine habitats. Ultimately, shorebird declines are occurring despite high levels of habitat protection in Australia. There is a need for a concerted effort both nationally and internationally to map and understand how intertidal habitats are changing, and how habitat conservation can be implemented more effectively.


Science | 2017

Breaking the deadlock on ivory

Duan Biggs; Matthew H. Holden; Alexander R. Braczkowski; Carly N. Cook; E. J. Milner-Gulland; Jacob Phelps; Robert J. Scholes; Robert J. Smith; Fiona M. Underwood; Vanessa M. Adams; James R. Allan; Henry Brink; Rosie Cooney; Yufang Gao; Jon Hutton; Eve Macdonald-Madden; Martine Maron; Kent H. Redford; William J. Sutherland; Hugh P. Possingham

Wilderness areas, defined as areas free of industrial scale activities and other human pressures which result in significant biophysical disturbance, are important for biodiversity conservation and sustaining the key ecological processes underpinning planetary life-support systems. Despite their importance, wilderness areas are being rapidly eroded in extent and fragmented. Here we present the most up-to-date temporally inter-comparable maps of global terrestrial wilderness areas, which are essential for monitoring changes in their extent, and for proactively planning conservation interventions to ensure their preservation. Using maps of human pressure on the natural environment for 1993 and 2009, we identified wilderness as all ‘pressure free’ lands with a contiguous area >10,000u2009km2. These places are likely operating in a natural state and represent the most intact habitats globally. We then created a regionally representative map of wilderness following the well-established ‘Last of the Wild’ methodology; which identifies the 10% area with the lowest human pressure within each of Earth’s 60 biogeographic realms, and identifies the ten largest contiguous areas, along with all contiguous areas >10,000u2009km2.


Conservation Biology | 2018

Gaps and opportunities for the World Heritage Convention to contribute to global wilderness conservation

James R. Allan; Cyril Kormos; Tilman Jaeger; Oscar Venter; Bastian Bertzky; Yichuan Shi; Brendan Mackey; Remco van Merm; Elena Osipova; James E. M. Watson

An iterative process that recognizes different value systems may help to protect elephants Poaching for ivory has caused a steep decline in African elephant (Loxodonta africana, see the photo) populations over the past decade (1). This crisis has fueled a contentious global debate over which ivory policy would best protect elephants: banning all ivory trade or enabling regulated trade to incentivize and fund elephant conservation (2). The deep-seated deadlock on ivory policy consumes valuable resources and creates an antagonistic environment among elephant conservationists. Successful solutions must begin by recognizing the different values that influence stakeholder cognitive frameworks of how actions lead to outcomes (“mental models”) (3), and therefore their diverging positions on ivory trade (4). Based on successful conflict resolution in other areas, we propose an iterative process through which countries with wild elephant populations may be able to understand their differences and develop workable solutions in a less confrontational manner.


Conservation Biology | 2018

Reach and messages of the world's largest ivory burn

Alexander R. Braczkowski; Matthew H. Holden; Christopher O'Bryan; Chi Yeung Choi; Xiaojing Gan; Nicholas Beesley; Yufang Gao; James R. Allan; Peter Tyrrell; Daniel Stiles; Peadar Brehony; Revocatus Meney; Henry Brink; Nao Takashina; Ming-Ching Lin; Hsien-Yung Lin; Niki A. Rust; Severino G. Salmo; James E. M. Watson; Paula Kahumbu; Martine Maron; Hugh P. Possingham; Duan Biggs

Wilderness areas are ecologically intact landscapes predominantly free of human uses, especially industrial-scale activities that result in substantial biophysical disturbance. This definition does not exclude land and resource use by local communities who depend on such areas for subsistence and bio-cultural connections. Wilderness areas are important for biodiversity conservation and sustain key ecological processes and ecosystem services that underpin planetary life-support systems. Despite these widely recognized benefits and values of wilderness, they are insufficiently protected and are consequently being rapidly eroded. There are increasing calls for multilateral environmental agreements to make a greater and more systematic contribution to wilderness conservation before it is too late. We created a global map of remaining terrestrial wilderness following the established last-of-the-wild method, which identifies the 10% of areas with the lowest human pressure within each of Earths 62 biogeographic realms and identifies the 10 largest contiguous areas and all contiguous areas >10,000 km2 . We used our map to assess wilderness coverage by the World Heritage Convention and to identify gaps in coverage. We then identified large nationally designated protected areas with good wilderness coverage within these gaps. One-quarter of natural and mixed (i.e., sites of both natural and cultural value) World Heritage Sites (WHS) contained wilderness (total of 545,307 km2 ), which is approximately 1.8% of the worlds wilderness extent. Many WHS had excellent wilderness coverage, for example, the Okavango Delta in Botswana (11,914 km2 ) and the Central Suriname Nature Reserve (16,029xa0km2 ). However, 22 (35%) of the worlds terrestrial biorealms had no wilderness representation within WHS. We identified 840 protected areas of >500 km2 that were predominantly wilderness (>50% of their area) and represented 18 of the 22 missing biorealms. These areas offer a starting point for assessing the potential for the designation of new WHSs that could help increase wilderness representation on the World Heritage list. We urge the World Heritage Convention to ensure that the ecological integrity and outstanding universal value of existing WHS with wilderness values are preserved.

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Oscar Venter

University of Northern British Columbia

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Jasmine R. Lee

University of Queensland

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