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2017, Hastings Center Report
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3 pages
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AI-generated Abstract
The paper discusses the intersection of de-extinction and conservation in the context of the ongoing sixth major extinction crisis. It examines the shifting paradigms within conservation philosophy, particularly as they pertain to biotechnology and human influence on nature. Key debates include the role of humans as caregivers of the environment versus traditional preservationist approaches, the implications of de-extinction for conservation ethics, and the necessity of reevaluating conservation values in light of advancements in genetic technologies.
Functional Ecology, 2017
Responses to technical innovations are varied, with some people engaging early with new technology and pushing the envelope to see what could be achieved, whereas others push back against change. Then there are those who are most interested in the implications of a new way of doing something. Often the reality of a technical advance means users are obliged to adjust; for example, to electronic money transfer (Freedman 2000). Sometimes, the mere promise or potential of something revolutionary is enough to force a reaction, for example, cold fusion (Close 1991). De-extinction, the resurrection of extinct species, sits in this second category. Not so much a single technical advance (though the new gene-editing tool CRISPR will be transformative), as a coming together of developing techniques that make a new application possibleand it is possible, make no mistake. The next decade will see the cloning or genetic reconstruction of some version of a formerly extinct species; one that will live long enough to breathe and shake its fur, feathers, or scales, or to unfurl a leaf. The technical challenges that remain are formidable, but so very much has already been achieved along the de-extinction pathway. I'm often asked, 'Is this really possible?' My answer is yesde-extinction has moved from science fiction to science feasibility-and I point to the case of the successful cloning using tissue from the extinct Pyrenean ibex and a hybrid goat as a gestational surrogate (Folch et al. 2009). It was only 6 years ago that a New Zealand politician was mocked by his Parliamentary colleagues for mooting the idea of de-extincting (we still need to get the verb right) the moa (Smith 2014). Since then some serious and seriously smart people have been working towards resurrecting (a better word) the moa, the passenger pigeon, even the woolly mammoth. The prospect of de-extinction has stimulated the public debate and galvanized the media. True, they have to get past the obsession with mammoths, but at least, it is widely understood that dinosaurs are not on any de-extinction candidate lists. Much of the general discussion has dealt with ethical issues, revisiting the genetically modified organism (GMO) debate and questioning the hubris of 'playing God', our duty to right past wrongs, and the moral hazards of changing the public perceptions of the finality of species extinction (Sandler 2013). On the other side, much of the technical material concerns how de-extinction might be achieved, and there are many who
Biodiversity and Conservation 2015, 2015
The human race faces many global to local challenges in the near future. Among these are massive biodiversity losses. The 2012 IUCN/SSC Red List reported evaluations of *56 % of all vertebrates. This included 97 % of amphibians, mammals, birds, cartilaginous fishes, and hagfishes. It also contained evaluations of *50 % of lampreys, *38 % of reptiles, and *29 % of bony fishes. A cursory examination of extinction magnitudes does not immediately reveal the severity of current biodiversity losses because the extinctions we see today have happened in such a short time compared to earlier events in the fossil record. So, we still must ask how current losses of species compare to losses in mass extinctions from the geological past. The most recent and best understood mass extinction is the Cretaceous terminal extinction which ends at the Cretaceous–Paleogene (K–Pg) border, 65 MYA. This event had massive losses of biodiversity (*17 % of families, [50 % of genera, and [70 % of species) and exterminated the dinosaurs. Extinction estimates for non-dinosaurian vertebrates at the K–Pg boundary range from 36 to 43 %. However, there remains much uncertainty regarding the completeness, preservation rates, and extinction magnitudes of the different classes of vertebrates. Fuzzy arithmetic was used to compare recent vertebrate extinction reported in the 2012 IUCN/SSC Red List with biodiversity losses at the end of K–Pg. Comparisons followed 16 different approaches to data compilation and 288 separate calculations. I tabulated the number of extant and extinct species (extinct ? extinct in the wild), extant island endemics, data deficient species, and so-called impaired species [species with IUCN/SSC Red List designations from vulnerable (VU) to critically endangered (CR)]. Species that went extinct since 1500 and since 1980 were tabulated. Vertebrate extinction moved forward 24–85 times faster since 1500 than during the Cretaceous mass extinction. The magnitude of extinction has exploded since 1980, with losses about 71–297 times larger than during the K–Pg event. If species identified by the IUCN/SSC as critically endangered through vulnerable, and those that are data deficient are assumed extinct by geological standards, then vertebrate extinction approaches 8900–18,500 times the magnitude during that mass extinction. These extreme values and the great speed with which vertebrate biodiversity is being decimated are comparable to the devastation of previous extinction events. If recent levels of extinction were to continue, the magnitude is sufficient to drive these groups extinct in less than a century.
Hastings Center Report, 2017
Decades of globally coordinated work in conservation have failed to slow the loss of biodiversity. To do better—even if that means nothing more than failing less spectacularly—bolder thinking is necessary. One of the first possible conservation applications of synthetic biology to be debated is the use of genetic tools to resurrect once‐extinct species. Since the currency of conservation is biodiversity and the discipline of conservation biology was formed around the prevention of species extinctions, the prospect of reversing extinctions might have been expected to generate unreserved enthusiasm. But it was not universal acclaim that greeted the coming‐out party for “de‐extinction” that was the TEDx conference and accompanying National Geographic feature in 2013. Why the concern, the skepticism, even the hostility among many conservationists about the idea of restoring lost species? And how does this professional concern relate to public perception and support for conservation? Thi...
The Extinction Crisis Extinctions are nothing new in nature. Over 98 percent of all species that ever existed on earth are now extinct. Over the past 500 million years, at least five great mass extinctions have occurred. The largest was the end-Permian extinction, which occurred roughly 252 million years ago. Nearly ninety percent of all plant and animal species were wiped out then, probably as a result of rapid global warming. 1 A more famous mass extinction occurred 65 million years ago when the dinosaurs died out, perhaps due to a large asteroid strike that plunged the earth into a prolonged period of darkness and cold. After each mass extinction, it took at least 20 million years for previous levels of biodiversity to be restored. 2 Today we are in the midst of a sixth great extinction-one caused almost entirely by us. Normally in nature, roughly one to five species become extinct each year. Today, dozens, if not hundreds, of species of plants and animals are vanishing every single day. And because of factors such as habitat destruction, climate change, overharvesting, pollution, and invasive species, the extinction crisis is rapidly worsening. According to a recent landmark United Nations report, about a million species are at risk of extinction over the next few decades. 3 Worldwide, humans have wiped out 60% of all mammals, birds, insects, and reptiles since 1970. 4 A quarter of all mammals and a third of all amphibians are now listed as "threatened." In this chapter, we explore why biodiversity matters and how we should respond to the extinction crisis.
We live in the Anthropocene, an era characterized by widespread extinction and landscapes that are less habitable for most large mammals. Over 25 percent of terrestrial mammals are now in decline and 66 percent of top carnivores—creatures with profound ecological roles—are threatened with extinction. As habitat is fragmented and destroyed, wildlife across the world are left with both less and lower quality habitat and lack the resources necessary for survival. De-extinction is an option under consideration as the world undergoes this mass extinction event—the sixth such event in Earth’s history. However, if there is currently no room for the magnificent Bengal Tiger or African Elephant, why are we considering bringing back Woolly Mammoths?
Functional Ecology, 2016
populations as « evolutionary proxies » of extinct species is meaningless; (2) their phylogenetic originality is likely to be limited by the selection of inappropriate candidate species, and the fact that the original species might be those for which deextinction is the most difficult to achieve practically; (3) the resurrection of a few extinct species does not have the potential to conserve as much evolutionary history as traditional conservation strategies, such as the reduction of ongoing species declines and extinction debts. 6. De-extinction is a stimulating idea, which is not intrinsically antagonistic to the conservation of evolutionary processes. However, poor choice of candidate species, and most importantly, too long time scales between a species' extinction and its resurrection are associated with low expected evolutionary benefits and likely unacceptable eco-evolutionary risks.
1. De-extinction, the process of resurrecting extinct species, is in an early stage of scientific implementation. However, its potential to contribute effectively to biodiversity conservation remains unexplored, especially from an evolutionary perspective. 2. We review and discuss the application of the existing evolutionary conservation framework to potential de-extinction projects. We aim to understand how evolutionary processes can influence the dynamics of resurrected populations and to place de-extinction within micro-and macro-evolutionary conservation perspectives. 3. In programmes aiming to revive long-extinct species, the most important constraints to the short-term viability of any resurrected population are (i) their intrinsically low evolutionary resilience and (ii) their poor eco-evolutionary experience, in relation to the absence of (co)adaption to biotic and abiotic changes in the recipient environment. 4. Assuming that some populations of resurrected species can persist locally, they have the potential to bring substantial benefits to biodiversity if the time since initial extinction is short relative to evolutionary dynamics. The restoration of lost genetic information could lead, along with the reinstatement of lost ecological functions, to the restoration of some evolutionary pat-rimony and processes, such as adaptation and diversification. 5. However, substantial evolutionary costs might occur, including unintended eco-evolutionary changes in the local system and unintended spread of the species. Further, evolutionary benefits are limited because (i) the use of resurrected populations as 'evolutionary proxies' of extinct species is meaningless; (ii) their phylogenetic originality is likely to be limited by the selection of inappropriate candidate species and the fact that the original species might be those for which de-extinction is the most difficult to achieve practically; (iii) the resurrection of a few extinct species does not have the potential to conserve as much evolutionary history as traditional conservation strategies, such as the reduction of ongoing species declines and extinction debts. 6. De-extinction is a stimulating idea, which is not intrinsically antagonistic to the conservation of evolutionary processes. However, poor choice of candidate species, and most importantly , too long time scales between a species' extinction and its resurrection are associated with low expected evolutionary benefits and likely unacceptable eco-evolutionary risks.
2021
Each account is centred around a single species, but invariably combined with a broader review of multiple species with something important in common. The result will hopefully be a more robust understanding of the current biodiversity crisis by the reader. And a greater appreciation of the diversity of the natural world more generally. Having recently lost so much biodiversity already, it is critical to bring attention to the incredible array of species that survive, and hence the need to protect them now more than ever.
https://www.routledge.com/The-Routledge-Companion-to-Northeast-India/Wouters-Subba/p/book/9780367725662
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