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Conservation biology
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Conservation biology is the study of the conservation of nature and of Earth's biodiversity with the aim of protecting species, their habitats, and ecosystems from excessive rates of extinction and the erosion of biotic interactions.[1][2][3] It is an interdisciplinary subject drawing on natural and social sciences, and the practice of natural resource management.[4][5][page needed][6][7]
The conservation ethic is based on the findings of conservation biology.
Origins
[edit]
The term conservation biology and its conception as a new field originated with the convening of "The First International Conference on Research in Conservation Biology" held at the University of California, San Diego in La Jolla, California, in 1978 led by American biologists Bruce A. Wilcox and Michael E. Soulé with a group of leading university and zoo researchers and conservationists including Kurt Benirschke, Sir Otto Frankel, Thomas Lovejoy, and Jared Diamond. The meeting was prompted due to concern over tropical deforestation, disappearing species, and eroding genetic diversity within species.[8] The conference and proceedings that resulted[2] sought to initiate the bridging of a gap between theory in ecology and evolutionary genetics on the one hand and conservation policy and practice on the other.[9]
Conservation biology and the concept of biological diversity (biodiversity) emerged together, helping crystallize the modern era of conservation science and policy.[10] The inherent multidisciplinary basis for conservation biology has led to new subdisciplines including conservation social science, conservation behavior and conservation physiology.[11] It stimulated further development of conservation genetics which Otto Frankel had originated first but is now often considered a subdiscipline as well.[12]
Description
[edit]The rapid decline of established biological systems around the world means that conservation biology is often referred to as a "Discipline with a deadline".[13] Conservation biology is tied closely to ecology in researching the population ecology (dispersal, migration, demographics, effective population size, inbreeding depression, and minimum population viability) of rare or endangered species.[14][15] Conservation biology is concerned with phenomena that affect the maintenance, loss, and restoration of biodiversity and the science of sustaining evolutionary processes that engender genetic, population, species, and ecosystem diversity.[5][6][7][15] The concern stems from estimates suggesting that up to 50% of all species on the planet will disappear within the next 50 years,[16] which will increase poverty and starvation, and will reset the course of evolution on this planet.[17][18] Researchers acknowledge that projections are difficult, given the unknown potential impacts of many variables, including species introduction to new biogeographical settings and a non-analog climate.[19]
Conservation biologists research and educate on the trends and process of biodiversity loss, species extinctions, and the negative effect these are having on our capabilities to sustain the well-being of human society. Conservation biologists work in the field and office, in government, universities, non-profit organizations and industry. The topics of their research are diverse, because this is an interdisciplinary network with professional alliances in the biological as well as social sciences. Those dedicated to the cause and profession advocate for a global response to the current biodiversity crisis based on morals, ethics, and scientific reason. Organizations and citizens are responding to the biodiversity crisis through conservation action plans that direct research, monitoring, and education programs that engage concerns at local through global scales.[4][5][6][7] There is increasing recognition that conservation is not just about what is achieved but how it is done.[20]
History
[edit]The conservation of natural resources is the fundamental problem. Unless we solve that problem, it will avail us little to solve all others.
Natural resource conservation
[edit]Conscious efforts to conserve and protect global biodiversity are a recent phenomenon.[7][22] Natural resource conservation, however, has a history that extends prior to the age of conservation. Resource ethics grew out of necessity through direct relations with nature. Regulation or communal restraint became necessary to prevent selfish motives from taking more than could be locally sustained, therefore compromising the long-term supply for the rest of the community.[7] This social dilemma with respect to natural resource management is often called the "Tragedy of the Commons".[23][24]
From this principle, conservation biologists can trace communal resource based ethics throughout cultures as a solution to communal resource conflict.[7] For example, the Alaskan Tlingit peoples and the Haida of the Pacific Northwest had resource boundaries, rules, and restrictions among clans with respect to the fishing of sockeye salmon. These rules were guided by clan elders who knew lifelong details of each river and stream they managed.[7][25] There are numerous examples in history where cultures have followed rules, rituals, and organized practice with respect to communal natural resource management.[26][27]
The Mauryan emperor Ashoka around 250 BC issued edicts restricting the slaughter of animals and certain kinds of birds, as well as opened veterinary clinics.[citation needed]
Conservation ethics are also found in early religious and philosophical writings. There are examples in the Tao, Shinto, Hindu, Islamic and Buddhist traditions.[7][28] In Greek philosophy, Plato lamented about pasture land degradation: "What is left now is, so to say, the skeleton of a body wasted by disease; the rich, soft soil has been carried off and only the bare framework of the district left."[29] In the bible, through Moses, God commanded to let the land rest from cultivation every seventh year.[7][30] Before the 18th century, however, much of European culture considered it a pagan view to admire nature. Wilderness was denigrated while agricultural development was praised.[31] However, as early as AD 680 a wildlife sanctuary was founded on the Farne Islands by St Cuthbert in response to his religious beliefs.[7]
Early naturalists
[edit]

Natural history was a major preoccupation in the 18th century, with grand expeditions and the opening of popular public displays in Europe and North America. By 1900 there were 150 natural history museums in Germany, 250 in Great Britain, 250 in the United States, and 300 in France.[32] Preservationist or conservationist sentiments are a development of the late 18th to early 20th centuries.
Before Charles Darwin set sail on HMS Beagle, most people in the world, including Darwin, believed in special creation and that all species were unchanged.[33] George-Louis Leclerc was one of the first naturalist that questioned this belief. He proposed in his 44 volume natural history book that species evolve due to environmental influences.[33] Erasmus Darwin was also a naturalist who also suggested that species evolved. Erasmus Darwin noted that some species have vestigial structures which are anatomical structures that have no apparent function in the species currently but would have been useful for the species' ancestors.[33] The thinking of these early 18th century naturalists helped to change the mindset and thinking of the early 19th century naturalists.
By the early 19th century biogeography was ignited through the efforts of Alexander von Humboldt, Charles Lyell and Charles Darwin.[34] The 19th-century fascination with natural history engendered a fervor to be the first to collect rare specimens with the goal of doing so before they became extinct by other such collectors.[31][32] Although the work of many 18th and 19th century naturalists were to inspire nature enthusiasts and conservation organizations, their writings, by modern standards, showed insensitivity towards conservation as they would kill hundreds of specimens for their collections.[32]
Conservation movement
[edit]The modern roots of conservation biology can be found in the late 18th-century Enlightenment period particularly in England and Scotland.[31][35] Thinkers including Lord Monboddo described the importance of "preserving nature"; much of this early emphasis had its origins in Christian theology.[35]
Scientific conservation principles were first practically applied to the forests of British India. The conservation ethic that began to evolve included three core principles: that human activity damaged the environment, that there was a civic duty to maintain the environment for future generations, and that scientific, empirically based methods should be applied to ensure this duty was carried out. Sir James Ranald Martin was prominent in promoting this ideology, publishing many medico-topographical reports that demonstrated the scale of damage wrought through large-scale deforestation and desiccation, and lobbying extensively for the institutionalization of forest conservation activities in British India through the establishment of Forest Departments.[36]
The Madras Board of Revenue started local conservation efforts in 1842, headed by Alexander Gibson, a professional botanist who systematically adopted a forest conservation program based on scientific principles. This was the first case of state conservation management of forests in the world.[37] Governor-General Lord Dalhousie introduced the first permanent and large-scale forest conservation program in the world in 1855, a model that soon spread to other colonies, as well the United States,[38][39][40] where Yellowstone National Park was opened in 1872 as the world's first national park.[41][page needed]
The term conservation came into widespread use in the late 19th century and referred to the management, mainly for economic reasons, of such natural resources as timber, fish, game, topsoil, pastureland, and minerals. In addition it referred to the preservation of forests (forestry), wildlife (wildlife refuge), parkland, wilderness, and watersheds. This period also saw the passage of the first conservation legislation and the establishment of the first nature conservation societies. The Sea Birds Preservation Act of 1869 was passed in Britain as the first nature protection law in the world[42] after extensive lobbying from the Association for the Protection of Seabirds[43] and the respected ornithologist Alfred Newton.[44] Newton was also instrumental in the passage of the first Game laws from 1872, which protected animals during their breeding season so as to prevent the stock from being brought close to extinction.[45]
One of the first conservation societies was the Royal Society for the Protection of Birds, founded in 1889 in Manchester[46] as a protest group campaigning against the use of great crested grebe and kittiwake skins and feathers in fur clothing. Originally known as "the Plumage League",[47] the group gained popularity and eventually amalgamated with the Fur and Feather League in Croydon, and formed the RSPB.[48] The National Trust formed in 1895 with the manifesto to "...promote the permanent preservation, for the benefit of the nation, of lands, ... to preserve (so far practicable) their natural aspect." In May 1912, a month after the Titanic sank, banker and expert naturalist Charles Rothschild held a meeting at the Natural History Museum in London to discuss his idea for a new organisation to save the best places for wildlife in the British Isles. This meeting led to the formation of the Society for the Promotion of Nature Reserves, which later became the Wildlife Trusts.[citation needed]

In the United States, the Forest Reserve Act of 1891 gave the President power to set aside forest reserves from the land in the public domain. John Muir founded the Sierra Club in 1892, and the New York Zoological Society was set up in 1895. A series of national forests and preserves were established by Theodore Roosevelt from 1901 to 1909.[50][51] The 1916 National Parks Act, included a 'use without impairment' clause, sought by John Muir, which eventually resulted in the removal of a proposal to build a dam in Dinosaur National Monument in 1959.[52]

In the 20th century, Canadian civil servants, including Charles Gordon Hewitt[53] and James Harkin, spearheaded the movement toward wildlife conservation.[54][page needed]
In the 21st century professional conservation officers have begun to collaborate with indigenous communities for protecting wildlife in Canada.[55] Some conservation efforts are yet to fully take hold due to ecological neglect.[56][57][58] For example in the USA, 21st century bowfishing of native fishes, which amounts to killing wild animals for recreation and disposing of them immediately afterwards, remains unregulated and unmanaged.[49]
Global conservation efforts
[edit]In the mid-20th century, efforts arose to target individual species for conservation, notably efforts in big cat conservation in South America led by the New York Zoological Society.[59] In the early 20th century the New York Zoological Society was instrumental in developing concepts of establishing preserves for particular species and conducting the necessary conservation studies to determine the suitability of locations that are most appropriate as conservation priorities; the work of Henry Fairfield Osborn Jr., Carl E. Akeley, Archie Carr and his son Archie Carr III is notable in this era.[60][61][62] Akeley for example, having led expeditions to the Virunga Mountains and observed the mountain gorilla in the wild, became convinced that the species and the area were conservation priorities. He was instrumental in persuading Albert I of Belgium to act in defense of the mountain gorilla and establish Albert National Park (since renamed Virunga National Park) in what is now Democratic Republic of Congo.[63]
By the 1970s, led primarily by work in the United States under the Endangered Species Act[64] along with the Species at Risk Act (SARA) of Canada, Biodiversity Action Plans developed in Australia, Sweden, the United Kingdom, hundreds of species specific protection plans ensued. Notably the United Nations acted to conserve sites of outstanding cultural or natural importance to the common heritage of mankind. The programme was adopted by the General Conference of UNESCO in 1972. As of 2006, a total of 830 sites are listed: 644 cultural, 162 natural. The first country to pursue aggressive biological conservation through national legislation was the United States, which passed back to back legislation in the Endangered Species Act[65] (1966) and National Environmental Policy Act (1970),[66] which together injected major funding and protection measures to large-scale habitat protection and threatened species research. Other conservation developments, however, have taken hold throughout the world. India, for example, passed the Wildlife Protection Act of 1972.[67]
In 1980, a significant development was the emergence of the urban conservation movement. A local organization was established in Birmingham, UK, a development followed in rapid succession in cities across the UK, then overseas. Although perceived as a grassroots movement, its early development was driven by academic research into urban wildlife. Initially perceived as radical, the movement's view of conservation being inextricably linked with other human activity has now become mainstream in conservation thought. Considerable research effort is now directed at urban conservation biology. The Society for Conservation Biology originated in 1985.[7]: 2
By 1992, most of the countries of the world had become committed to the principles of conservation of biological diversity with the Convention on Biological Diversity;[68] subsequently many countries began programmes of Biodiversity Action Plans to identify and conserve threatened species within their borders, as well as protect associated habitats. The late 1990s saw increasing professionalism in the sector, with the maturing of organisations such as the Institute of Ecology and Environmental Management and the Society for the Environment.
Since 2000, the concept of landscape scale conservation has risen to prominence, with less emphasis being given to single-species or even single-habitat focused actions. Instead an ecosystem approach is advocated by most mainstream conservationists, although concerns have been expressed by those working to protect some high-profile species.
Ecology has clarified the workings of the biosphere; i.e., the complex interrelationships among humans, other species, and the physical environment. The burgeoning human population and associated agriculture, industry, and the ensuing pollution, have demonstrated how easily ecological relationships can be disrupted.[69]
The last word in ignorance is the man who says of an animal or plant: "What good is it?" If the land mechanism as a whole is good, then every part is good, whether we understand it or not. If the biota, in the course of aeons, has built something we like but do not understand, then who but a fool would discard seemingly useless parts? To keep every cog and wheel is the first precaution of intelligent tinkering.
Concepts and foundations
[edit]Measuring extinction rates
[edit]Extinction rates are measured in a variety of ways. Conservation biologists measure and apply statistical measures of fossil records,[1][70] rates of habitat loss, and a multitude of other variables such as loss of biodiversity as a function of the rate of habitat loss and site occupancy[71] to obtain such estimates.[72] The Theory of Island Biogeography[73] is possibly the most significant contribution toward the scientific understanding of both the process and how to measure the rate of species extinction. The current background extinction rate is estimated to be one species every few years.[74] Actual extinction rates are estimated to be orders of magnitudes higher.[75] While this is important, it's worth noting that there are no models in existence that account for the complexity of unpredictable factors like species movement, a non-analog climate, changing species interactions, evolutionary rates on finer time scales, and many other stochastic variables.[76][19]
The measure of ongoing species loss is made more complex by the fact that most of the Earth's species have not been described or evaluated. Estimates vary greatly on how many species actually exist (estimated range: 3,600,000–111,700,000)[77] to how many have received a species binomial (estimated range: 1.5–8 million).[77] Less than 1% of all species that have been described beyond simply noting its existence.[77] From these figures, the IUCN reports that 23% of vertebrates, 5% of invertebrates and 70% of plants that have been evaluated are designated as endangered or threatened.[78][79] Better knowledge is being constructed by The Plant List for actual numbers of species.
Systematic conservation planning
[edit]Systematic conservation planning is an effective way to seek and identify efficient and effective types of reserve design to capture or sustain the highest priority biodiversity values and to work with communities in support of local ecosystems. Margules and Pressey identify six interlinked stages in the systematic planning approach:[80]
- Compile data on the biodiversity of the planning region
- Identify conservation goals for the planning region
- Review existing conservation areas
- Select additional conservation areas
- Implement conservation actions
- Maintain the required values of conservation areas
Conservation biologists regularly prepare detailed conservation plans for grant proposals or to effectively coordinate their plan of action and to identify best management practices (e.g.[81]). Systematic strategies generally employ the services of Geographic Information Systems to assist in the decision-making process. The SLOSS debate is often considered in planning.
Conservation physiology: a mechanistic approach to conservation
[edit]Conservation physiology was defined by Steven J. Cooke and colleagues as:[11]
An integrative scientific discipline applying physiological concepts, tools, and knowledge to characterizing biological diversity and its ecological implications; understanding and predicting how organisms, populations, and ecosystems respond to environmental change and stressors; and solving conservation problems across the broad range of taxa (i.e. including microbes, plants, and animals). Physiology is considered in the broadest possible terms to include functional and mechanistic responses at all scales, and conservation includes the development and refinement of strategies to rebuild populations, restore ecosystems, inform conservation policy, generate decision-support tools, and manage natural resources.
Conservation physiology is particularly relevant to practitioners in that it has the potential to generate cause-and-effect relationships and reveal the factors that contribute to population declines.
Conservation biology as a profession
[edit]The Society for Conservation Biology is a global community of conservation professionals dedicated to advancing the science and practice of conserving biodiversity. Conservation biology as a discipline reaches beyond biology, into subjects such as philosophy, law, economics, humanities, arts, anthropology, and education.[5][6] Within biology, conservation genetics and evolution are immense fields unto themselves, but these disciplines are of prime importance to the practice and profession of conservation biology.
Conservationists introduce bias when they support policies using qualitative description, such as habitat degradation, or healthy ecosystems. Conservation biologists advocate for reasoned and sensible management of natural resources and do so with a disclosed combination of science, reason, logic, and values in their conservation management plans.[5] This sort of advocacy is similar to the medical profession advocating for healthy lifestyle options, both are beneficial to human well-being yet remain scientific in their approach.
There is a movement in conservation biology suggesting a new form of leadership is needed to mobilize conservation biology into a more effective discipline that is able to communicate the full scope of the problem to society at large.[82] The movement proposes an adaptive leadership approach that parallels an adaptive management approach. The concept is based on a new philosophy or leadership theory steering away from historical notions of power, authority, and dominance. Adaptive conservation leadership is reflective and more equitable as it applies to any member of society who can mobilize others toward meaningful change using communication techniques that are inspiring, purposeful, and collegial. Adaptive conservation leadership and mentoring programs are being implemented by conservation biologists through organizations such as the Aldo Leopold Leadership Program.[83]
Approaches
[edit]Conservation may be classified as either in-situ conservation, which is protecting an endangered species in its natural habitat, or ex-situ conservation, which occurs outside the natural habitat.[84] In-situ conservation involves protecting or restoring the habitat. Ex-situ conservation, on the other hand, involves protection outside of an organism's natural habitat, such as on reservations or in gene banks, in circumstances where viable populations may not be present in the natural habitat.[84]
The conservation of habitats like forest, water or soil in its natural state is crucial for any species depending in it to thrive. Instead of making the whole new environment looking alike the original habitat of wild animals is less effective than preserving the original habitats. An approach in Nepal named reforestation campaign has helped increase the density and area covered by the original forests which proved to be better than creating entirely new environment after original one is let to lost. Old Forests Store More Carbon than Young Ones as proved by latest researches, so it is more crucial to protect the old ones. The reforestation campaign launched by Himalayan Adventure Therapy in Nepal basically visits the old forests in periodic basis which are vulnerable to loss of density and the area covered due to unplanned urbanization activities. Then they plant the new saplings of same tree families of that existing forest in the areas where the old forest has been lost and also plant those saplings to the barren areas connected to the forest. This maintains the density and area covered by the forest.
Also, non-interference may be used, which is termed a preservationist method. Preservationists advocate for giving areas of nature and species a protected existence that halts interference from the humans.[5] In this regard, conservationists differ from preservationists in the social dimension, as conservation biology engages society and seeks equitable solutions for both society and ecosystems. Some preservationists emphasize the potential of biodiversity in a world without humans.
Ecological monitoring in conservation
[edit]Ecological monitoring is the systematic collection of data relevant to the ecology of a species or habitat at repeating intervals with defined methods.[85] Long-term monitoring for environmental and ecological metrics is an important part of any successful conservation initiative. Unfortunately, long-term data for many species and habitats is not available in many cases.[86] A lack of historical data on species populations, habitats, and ecosystems means that any current or future conservation work will have to make assumptions to determine if the work is having any effect on the population or ecosystem health. Ecological monitoring can provide early warning signals of deleterious effects (from human activities or natural changes in an environment) on an ecosystem and its species.[85] In order for signs of negative trends in ecosystem or species health to be detected, monitoring methods must be carried out at appropriate time intervals, and the metric must be able to capture the trend of the population or habitat as a whole.
Long-term monitoring can include the continued measuring of many biological, ecological, and environmental metrics including annual breeding success, population size estimates, water quality, biodiversity (which can be measured in many way, i.e. Shannon Index), and many other methods. When determining which metrics to monitor for a conservation project, it is important to understand how an ecosystem functions and what role different species and abiotic factors have within the system.[87] It is important to have a precise reason for why ecological monitoring is implemented; within the context of conservation, this reasoning is often to track changes before, during, or after conservation measures are put in place to help a species or habitat recover from degradation and/or maintain integrity.[85]
Another benefit of ecological monitoring is the hard evidence it provides scientists to use for advising policy makers and funding bodies about conservation efforts. Not only is ecological monitoring data important for convincing politicians, funders, and the public why a conservation program is important to implement, but also to keep them convinced that a program should be continued to be supported.[86]
There is plenty of debate on how conservation resources can be used most efficiently; even within ecological monitoring, there is debate on which metrics that money, time and personnel should be dedicated to for the best chance of making a positive impact. One specific general discussion topic is whether monitoring should happen where there is little human impact (to understand a system that has not been degraded by humans), where there is human impact (so the effects from humans can be investigated), or where there is data deserts and little is known about the habitats' and communities' response to human perturbations.[85]
The concept of bioindicators / indicator species can be applied to ecological monitoring as a way to investigate how pollution is affecting an ecosystem.[88] Species like amphibians and birds are highly susceptible to pollutants in their environment due to their behaviours and physiological features that cause them to absorb pollutants at a faster rate than other species. Amphibians spend parts of their time in the water and on land, making them susceptible to changes in both environments.[89] They also have very permeable skin that allows them to breathe and intake water, which means they also take any air or water-soluble pollutants in as well. Birds often cover a wide range in habitat types annually, and also generally revisit the same nesting site each year. This makes it easier for researchers to track ecological effects at both an individual and a population level for the species.[90]
Many conservation researchers believe that having a long-term ecological monitoring program should be a priority for conservation projects, protected areas, and regions where environmental harm mitigation is used.[91]
Ethics and values
[edit]Conservation biologists are interdisciplinary researchers that practice ethics in the biological and social sciences. Chan states[92] that conservationists must advocate for biodiversity and can do so in a scientifically ethical manner by not promoting simultaneous advocacy against other competing values.
A conservationist may be inspired by the resource conservation ethic,[7]: 15 which seeks to identify what measures will deliver "the greatest good for the greatest number of people for the longest time."[5]: 13 In contrast, some conservation biologists argue that nature has an intrinsic value that is independent of anthropocentric usefulness or utilitarianism.[7]: 3, 12, 16–17 Aldo Leopold was a classical thinker and writer on such conservation ethics whose philosophy, ethics and writings are still valued and revisited by modern conservation biologists.[7]: 16–17
Conservation priorities
[edit]
The International Union for Conservation of Nature (IUCN) has organized a global assortment of scientists and research stations across the planet to monitor the changing state of nature in an effort to tackle the extinction crisis. The IUCN provides annual updates on the status of species conservation through its Red List.[93] The IUCN Red List serves as an international conservation tool to identify those species most in need of conservation attention and by providing a global index on the status of biodiversity.[94] More than the dramatic rates of species loss, however, conservation scientists note that the sixth mass extinction is a biodiversity crisis requiring far more action than a priority focus on rare, endemic or endangered species. Concerns for biodiversity loss covers a broader conservation mandate that looks at ecological processes, such as migration, and a holistic examination of biodiversity at levels beyond the species, including genetic, population and ecosystem diversity.[95] Extensive, systematic, and rapid rates of biodiversity loss threatens the sustained well-being of humanity by limiting supply of ecosystem services that are otherwise regenerated by the complex and evolving holistic network of genetic and ecosystem diversity. While the conservation status of species is employed extensively in conservation management,[94] some scientists highlight that it is the common species that are the primary source of exploitation and habitat alteration by humanity. Moreover, common species are often undervalued despite their role as the primary source of ecosystem services.[96][97]
While most in the community of conservation science "stress the importance" of sustaining biodiversity,[98] there is debate on how to prioritize genes, species, or ecosystems, which are all components of biodiversity (e.g. Bowen, 1999). While the predominant approach to date has been to focus efforts on endangered species by conserving biodiversity hotspots, some scientists (e.g)[99] and conservation organizations, such as the Nature Conservancy, argue that it is more cost-effective, logical, and socially relevant to invest in biodiversity coldspots.[100] The costs of discovering, naming, and mapping out the distribution of every species, they argue, is an ill-advised conservation venture. They reason it is better to understand the significance of the ecological roles of species.[95]
Biodiversity hotspots and coldspots are a way of recognizing that the spatial concentration of genes, species, and ecosystems is not uniformly distributed on the Earth's surface.[101] For example, "... 44% of all species of vascular plants and 35% of all species in four vertebrate groups are confined to 25 hotspots comprising only 1.4% of the land surface of the Earth."[102]
Those arguing in favor of setting priorities for coldspots point out that there are other measures to consider beyond biodiversity. They point out that emphasizing hotspots downplays the importance of the social and ecological connections to vast areas of the Earth's ecosystems where biomass, not biodiversity, reigns supreme.[103] It is estimated that 36% of the Earth's surface, encompassing 38.9% of the worlds vertebrates, lacks the endemic species to qualify as biodiversity hotspot.[104] Moreover, measures show that maximizing protections for biodiversity does not capture ecosystem services any better than targeting randomly chosen regions.[105] Population level biodiversity (mostly in coldspots) are disappearing at a rate that is ten times that at the species level.[99][106] The level of importance in addressing biomass versus endemism as a concern for conservation biology is highlighted in literature measuring the level of threat to global ecosystem carbon stocks that do not necessarily reside in areas of endemism.[107][108] A hotspot priority approach[109] would not invest so heavily in places such as steppes, the Serengeti, the Arctic, or taiga. These areas contribute a great abundance of population (not species) level biodiversity[106] and ecosystem services, including cultural value and planetary nutrient cycling.[100]

Those in favor of the hotspot approach point out that species are irreplaceable components of the global ecosystem, they are concentrated in places that are most threatened, and should therefore receive maximal strategic protections.[110] This is a hotspot approach because the priority is set to target species level concerns over population level or biomass.[106][failed verification] Species richness and genetic biodiversity contributes to and engenders ecosystem stability, ecosystem processes, evolutionary adaptability, and biomass.[111] Both sides agree, however, that conserving biodiversity is necessary to reduce the extinction rate and identify an inherent value in nature; the debate hinges on how to prioritize limited conservation resources in the most cost-effective way.
Economic values and natural capital
[edit]
Conservation biologists have started to collaborate with leading global economists to determine how to measure the wealth and services of nature and to make these values apparent in global market transactions.[112] This system of accounting is called natural capital and would, for example, register the value of an ecosystem before it is cleared to make way for development.[113] The WWF publishes its Living Planet Report and provides a global index of biodiversity by monitoring approximately 5,000 populations in 1,686 species of vertebrate (mammals, birds, fish, reptiles, and amphibians) and report on the trends in much the same way that the stock market is tracked.[114]
This method of measuring the global economic benefit of nature has been endorsed by the G8+5 leaders and the European Commission.[112] Nature sustains many ecosystem services[115] that benefit humanity.[116] Many of the Earth's ecosystem services are public goods without a market and therefore no price or value.[112] When the stock market registers a financial crisis, traders on Wall Street are not in the business of trading stocks for much of the planet's living natural capital stored in ecosystems. There is no natural stock market with investment portfolios into sea horses, amphibians, insects, and other creatures that provide a sustainable supply of ecosystem services that are valuable to society.[116] The ecological footprint of society has exceeded the bio-regenerative capacity limits of the planet's ecosystems by about 30 percent, which is the same percentage of vertebrate populations that have registered decline from 1970 through 2005.[114]
The ecological credit crunch is a global challenge. The Living Planet Report 2008 tells us that more than three-quarters of the world's people live in nations that are ecological debtors – their national consumption has outstripped their country's biocapacity. Thus, most of us are propping up our current lifestyles, and our economic growth, by drawing (and increasingly overdrawing) upon the ecological capital of other parts of the world.
The inherent natural economy plays an essential role in sustaining humanity,[117] including the regulation of global atmospheric chemistry, pollinating crops, pest control,[118] cycling soil nutrients, purifying our water supply,[119] supplying medicines and health benefits,[120] and unquantifiable quality of life improvements. There is a relationship, a correlation, between markets and natural capital, and social income inequity and biodiversity loss. This means that there are greater rates of biodiversity loss in places where the inequity of wealth is greatest,[121] an example of this would be the Perdido Key beach mouse. This is an endangered species that its demis started because of continued development along beaches, these mice leave in sand dunes and play an important role within this ecosystem. These mice help the grass grow inside the sandunes, they eat this grass and then this leads to then spreading seeds throughout the beach creating more grass. Sand dunes may not seem that important but they do act as a barrier for any sort of storm coming from the ocean such as hurricanes.[122][123]
Although a direct market comparison of natural capital is likely insufficient in terms of human value, one measure of ecosystem services suggests the contribution amounts to trillions of dollars yearly.[124][125][126][127] For example, one segment of North American forests has been assigned an annual value of 250 billion dollars;[128] as another example, honey bee pollination is estimated to provide between 10 and 18 billion dollars of value yearly.[129] The value of ecosystem services on one New Zealand island has been imputed to be as great as the GDP of that region.[130] This planetary wealth is being lost at an incredible rate as the demands of human society is exceeding the bio-regenerative capacity of the Earth. While biodiversity and ecosystems are resilient, the danger of losing them is that humans cannot recreate many ecosystem functions through technological innovation.
Strategic species concepts
[edit]Keystone species
[edit]Some species, called a keystone species form a central supporting hub unique to their ecosystem.[131] The loss of such a species results in a collapse in ecosystem function, as well as the loss of coexisting species.[5] Keystone species are usually predators due to their ability to control the population of prey in their ecosystem.[131] The importance of a keystone species was shown by the extinction of the Steller's sea cow (Hydrodamalis gigas) through its interaction with sea otters, sea urchins, and kelp. Kelp beds grow and form nurseries in shallow waters to shelter creatures that support the food chain. Sea urchins feed on kelp, while sea otters feed on sea urchins. With the rapid decline of sea otters due to overhunting, sea urchin populations grazed unrestricted on the kelp beds and the ecosystem collapsed. Left unchecked, the urchins destroyed the shallow water kelp communities that supported the Steller's sea cow's diet and hastened their demise.[132] The sea otter was thought to be a keystone species because the coexistence of many ecological associates in the kelp beds relied upon otters for their survival. However this was later questioned by Turvey and Risley,[133] who showed that hunting alone would have driven the Steller's sea cow extinct.
Indicator species
[edit]An indicator species has a narrow set of ecological requirements, therefore they become useful targets for observing the health of an ecosystem. Some animals, such as amphibians with their semi-permeable skin and linkages to wetlands, have an acute sensitivity to environmental harm and thus may serve as a miner's canary. Indicator species are monitored in an effort to capture environmental degradation through pollution or some other link to proximate human activities.[5] Monitoring an indicator species is a measure to determine if there is a significant environmental impact that can serve to advise or modify practice, such as through different forest silviculture treatments and management scenarios, or to measure the degree of harm that a pesticide may impart on the health of an ecosystem.
Government regulators, consultants, or NGOs regularly monitor indicator species, however, there are limitations coupled with many practical considerations that must be followed for the approach to be effective.[134] It is generally recommended that multiple indicators (genes, populations, species, communities, and landscape) be monitored for effective conservation measurement that prevents harm to the complex, and often unpredictable, response from ecosystem dynamics (Noss, 1997[135]: 88–89 ).
Umbrella and flagship species
[edit]An example of an umbrella species is the monarch butterfly, because of its lengthy migrations and aesthetic value. The monarch migrates across North America, covering multiple ecosystems and so requires a large area to exist. Any protections afforded to the monarch butterfly will at the same time umbrella many other species and habitats. An umbrella species is often used as flagship species, which are species, such as the giant panda, the blue whale, the tiger, the mountain gorilla and the monarch butterfly, that capture the public's attention and attract support for conservation measures.[5] Paradoxically, however, conservation bias towards flagship species sometimes threatens other species of chief concern.[136]
Context and trends
[edit]Conservation biologists study trends and process from the paleontological past to the ecological present as they gain an understanding of the context related to species extinction.[1] It is generally accepted that there have been five major global mass extinctions that register in Earth's history. These include: the Ordovician (440 mya), Devonian (370 mya), Permian–Triassic (252 mya), Triassic–Jurassic (201 mya), and Cretaceous–Paleogene extinction event (66 mya) extinction spasms. Within the last 10,000 years, human influence over the Earth's ecosystems has been so extensive that scientists have difficulty estimating the number of species lost;[137] that is to say the rates of deforestation, reef destruction, wetland draining and other human acts are proceeding much faster than human assessment of species. The latest Living Planet Report by the World Wide Fund for Nature estimates that we have exceeded the bio-regenerative capacity of the planet, requiring 1.6 Earths to support the demands placed on our natural resources.[138]
Holocene extinction
[edit]
Conservation biologists are dealing with and have published evidence from all corners of the planet indicating that humanity may be causing the sixth and fastest planetary extinction event.[139][140][141] It has been suggested that an unprecedented number of species is becoming extinct in what is known as the Holocene extinction event.[142] The global extinction rate may be approximately 1,000 times higher than the natural background extinction rate.[143] It is estimated that two-thirds of all mammal genera and one-half of all mammal species weighing at least 44 kilograms (97 lb) have gone extinct in the last 50,000 years.[133][144][145][146] The Global Amphibian Assessment[147] reports that amphibians are declining on a global scale faster than any other vertebrate group, with over 32% of all surviving species being threatened with extinction. The surviving populations are in continual decline in 43% of those that are threatened. Since the mid-1980s the actual rates of extinction have exceeded 211 times rates measured from the fossil record.[148] However, "The current amphibian extinction rate may range from 25,039 to 45,474 times the background extinction rate for amphibians."[148] The global extinction trend occurs in every major vertebrate group that is being monitored. For example, 23% of all mammals and 12% of all birds are Red Listed by the International Union for Conservation of Nature (IUCN), meaning they too are threatened with extinction. Even though extinction is natural, the decline in species is happening at such an incredible rate that evolution can simply not match, therefore, leading to the greatest continual mass extinction on Earth.[149] Humans have dominated the planet and our high consumption of resources, along with the pollution generated is affecting the environments in which other species live.[149][150] There are a wide variety of species that humans are working to protect such as the Hawaiian Crow and the Whooping Crane of Texas.[151] People can also take action on preserving species by advocating and voting for global and national policies that improve climate, under the concepts of climate mitigation and climate restoration. The Earth's oceans demand particular attention as climate change continues to alter pH levels, making it uninhabitable for organisms with shells which dissolve as a result.[143]
Status of oceans and reefs
[edit]Global assessments of coral reefs of the world continue to report drastic and rapid rates of decline. By 2000, 27% of the world's coral reef ecosystems had effectively collapsed. The largest period of decline occurred in a dramatic "bleaching" event in 1998, where approximately 16% of all the coral reefs in the world disappeared in less than a year. Coral bleaching is caused by a mixture of environmental stresses, including increases in ocean temperatures and acidity, causing both the release of symbiotic algae and death of corals.[152] Decline and extinction risk in coral reef biodiversity has risen dramatically in the past ten years. The loss of coral reefs, which are predicted to go extinct in the next century, threatens the balance of global biodiversity, will have huge economic impacts, and endangers food security for hundreds of millions of people.[153] Conservation biology plays an important role in international agreements covering the world's oceans[152] and other issues pertaining to biodiversity.
These predictions will undoubtedly appear extreme, but it is difficult to imagine how such changes will not come to pass without fundamental changes in human behavior.
The oceans are threatened by acidification due to an increase in CO2 levels. This is a most serious threat to societies relying heavily upon oceanic natural resources. A concern is that the majority of all marine species will not be able to evolve or acclimate in response to the changes in the ocean chemistry.[154]
The prospects of averting mass extinction seems unlikely when "90% of all of the large (average approximately ≥50 kg), open ocean tuna, billfishes, and sharks in the ocean"[18] are reportedly gone. Given the scientific review of current trends, the ocean is predicted to have few surviving multi-cellular organisms with only microbes left to dominate marine ecosystems.[18]
Groups other than vertebrates
[edit]Serious concerns also being raised about taxonomic groups that do not receive the same degree of social attention or attract funds as the vertebrates. These include fungal (including lichen-forming species),[155] invertebrate (particularly insect[16][156][157]) and plant communities[158] where the vast majority of biodiversity is represented. Conservation of fungi and conservation of insects, in particular, are both of pivotal importance for conservation biology. As mycorrhizal symbionts, and as decomposers and recyclers, fungi are essential for sustainability of forests.[155] The value of insects in the biosphere is enormous because they outnumber all other living groups in measure of species richness. The greatest bulk of biomass on land is found in plants, which is sustained by insect relations. This great ecological value of insects is countered by a society that often reacts negatively toward these aesthetically 'unpleasant' creatures.[159][160]
One area of concern in the insect world that has caught the public eye is the mysterious case of missing honey bees (Apis mellifera). Honey bees provide an indispensable ecological services through their acts of pollination supporting a huge variety of agriculture crops. The use of honey and wax have become vastly used throughout the world.[161] The sudden disappearance of bees leaving empty hives or colony collapse disorder (CCD) is not uncommon. However, in 16-month period from 2006 through 2007, 29% of 577 beekeepers across the United States reported CCD losses in up to 76% of their colonies. This sudden demographic loss in bee numbers is placing a strain on the agricultural sector. The cause behind the massive declines is puzzling scientists. Pests, pesticides, and global warming are all being considered as possible causes.[162][163]
Another highlight that links conservation biology to insects, forests, and climate change is the mountain pine beetle (Dendroctonus ponderosae) epidemic of British Columbia, Canada, which has infested 470,000 km2 (180,000 sq mi) of forested land since 1999.[107] An action plan has been prepared by the Government of British Columbia to address this problem.[164][165]
This impact [pine beetle epidemic] converted the forest from a small net carbon sink to a large net carbon source both during and immediately after the outbreak. In the worst year, the impacts resulting from the beetle outbreak in British Columbia were equivalent to 75% of the average annual direct forest fire emissions from all of Canada during 1959–1999.
— Kurz et al.[108]
Conservation biology of parasites
[edit]A large proportion of parasite species are threatened by extinction. A few of them are being eradicated as pests of humans or domestic animals; however, most of them are harmless. Parasites also make up a significant amount of global biodiversity, given that they make up a large proportion of all species on earth,[166] making them of increasingly prevalent conservation interest. Threats include the decline or fragmentation of host populations,[167] or the extinction of host species. Parasites are intricately woven into ecosystems and food webs, thereby occupying valuable roles in ecosystem structure and function.[168][166]
Threats to biodiversity
[edit]Today, many threats to biodiversity exist. An acronym that can be used to express the top threats of present-day H.I.P.P.O stands for Habitat Loss, Invasive Species, Pollution, Human Population, and Overharvesting.[169] The primary threats to biodiversity are habitat destruction (such as deforestation, agricultural expansion, urban development), and overexploitation (such as wildlife trade).[137][170][171][172][173][174] Habitat fragmentation also poses challenges, because the global network of protected areas only covers 11.5% of the Earth's surface.[175] A significant consequence of fragmentation and lack of linked protected areas is the reduction of animal migration on a global scale.[176] Considering that billions of tonnes of biomass are responsible for nutrient cycling across the earth, the reduction of migration is a serious matter for conservation biology.[177][178]
Human activities are associated directly or indirectly with nearly every aspect of the current extinction spasm.
However, human activities need not necessarily cause irreparable harm to the biosphere. With conservation management and planning for biodiversity at all levels, from genes to ecosystems, there are examples where humans mutually coexist in a sustainable way with nature.[179] Even with the current threats to biodiversity there are ways we can improve the current condition and start anew.
Many of the threats to biodiversity, including disease and climate change, are reaching inside borders of protected areas, leaving them 'not-so protected' (e.g. Yellowstone National Park).[180] Climate change, for example, is often cited as a serious threat in this regard, because there is a feedback loop between species extinction and the release of carbon dioxide into the atmosphere.[107][108] Ecosystems store and cycle large amounts of carbon which regulates global conditions.[181] In present day, there have been major climate shifts with temperature changes making survival of some species difficult.[169] The effects of global warming add a catastrophic threat toward a mass extinction of global biological diversity.[182] Numerous more species are predicted to face unprecedented levels of extinction risk due to population increase, climate change and economic development in the future.[183] Conservationists have claimed that not all the species can be saved, and they have to decide which their efforts should be used to protect. This concept is known as the Conservation Triage.[169] The extinction threat is estimated to range from 15 to 37 percent of all species by 2050,[182] or 50 percent of all species over the next 50 years.[16] The current extinction rate is 100–100,000 times more rapid today than the last several billion years.[169]
See also
[edit]- Applied ecology
- Bird observatory – Ornithological station
- Conservation-reliant species – Type of species requiring human intervention
- Ecological extinction – Ecology term
- Gene pool – Set of all genes in a population
- Genetic erosion – Genetic phenomenon
- Genetic pollution – Uncontrolled gene flow into wild populations
- In-situ conservation – Conservation process
- Indigenous peoples: environmental benefits
- List of basic biology topics
- List of biological websites
- List of biology topics
- List of conservation organisations
- List of conservation topics
- Mutualisms and conservation – Mutualism in biological conservation
- Natural environment – Living and non-living things on Earth
- Nature conservation – Movement to protect the biosphere
- Protected area – Areas protected for having ecological or cultural importance
- Regional Red List
- Renewable resource – Natural resource that is replenished relatively quickly
- Restoration ecology – Scientific study of renewing and restoring ecosystems
- Tyranny of small decisions – Economic phenomenon
- Water conservation – Policies for sustainable development of water use
- Welfare biology – Proposed field of research
- Wildlife disease
- Wildlife management – Management and control of wildlife populations
- World Conservation Monitoring Centre – Collaboration centre of UN Environment Programme
- Category:Nature conservation organizations by country
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Bowen, B. W. (December 1999). "Preserving genes, species, or ecosystems? Healing the fractured foundations of conservation policy" (PDF). Molecular Ecology. 8 (12 Suppl 1): S5–10. Bibcode:1999MolEc...8.....B. doi:10.1046/j.1365-294X.1999.00798.x. PMID 10703547. S2CID 33096004.
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Further reading
[edit]Scientific literature
- Bowen, Brian W. (1999). "Preserving genes, species, or ecosystems? Healing the fractured foundations of conservation policy". Molecular Ecology. 8 (s1): S5 – S10. Bibcode:1999MolEc...8.....B. doi:10.1046/j.1365-294X.1999.00798.x. PMID 10703547. S2CID 33096004.
- Brooks T. M.; Mittermeier R. A.; Gerlach J.; Hoffmann M.; Lamoreux J. F.; Mittermeier C. G.; Pilgrim J. D.; Rodrigues A. S. L. (2006). "Global Biodiversity Conservation Priorities". Science. 313 (5783): 58–61. Bibcode:2006Sci...313...58B. doi:10.1126/science.1127609. PMID 16825561. S2CID 5133902.
- Kareiva P.; Marvier M. (2003). "Conserving Biodiversity Coldspots" (PDF). American Scientist. 91 (4): 344–351. doi:10.1511/2003.4.344. Archived from the original (PDF) on September 6, 2006.
- Manlik, Oliver (2019). "The Importance of Reproduction for the Conservation of Slow-Growing Animal Populations". In Pierre Comizzoli; Janine L. Brown; William V. Holt (eds.). Reproductive Sciences in Animal Conservation. Advances in Experimental Medicine and Biology. Vol. 1200. Springer. pp. 13–39. doi:10.1007/978-3-030-23633-5_2. ISBN 978-3-030-23633-5. PMID 31471793. S2CID 201756810.
- McCallum M. L. (2008). "Amphibian Decline or Extinction? Current Declines Dwarf Background Extinction Rate" (PDF). Journal of Herpetology. 41 (3): 483–491. doi:10.1670/0022-1511(2007)41[483:ADOECD]2.0.CO;2. S2CID 30162903. Archived from the original (PDF) on 2008-12-17.
- McCallum M. L. (2015). "Vertebrate biodiversity losses point to a sixth mass extinction". Biodiversity and Conservation. 24 (10): 2497–2519. Bibcode:2015BiCon..24.2497M. doi:10.1007/s10531-015-0940-6. S2CID 254285797.
- McCallum, Malcolm L. (2021). "Turtle biodiversity losses suggest coming sixth mass extinction". Biodiversity and Conservation. 30 (5): 1257–1275. Bibcode:2021BiCon..30.1257M. doi:10.1007/s10531-021-02140-8. S2CID 233903598.
- Myers, Norman; Mittermeier, Russell A.; Mittermeier, Cristina G.; da Fonseca, Gustavo A. B.; Kent, Jennifer (2000). "Biodiversity hotspots for conservation priorities". Nature. 403 (6772): 853–8. Bibcode:2000Natur.403..853M. doi:10.1038/35002501. PMID 10706275. S2CID 4414279.
- Brooks T. M.; Mittermeier R. A.; Gerlach J.; Hoffmann M.; Lamoreux J. F.; Mittermeier C. G.; Pilgrim J. D.; Rodrigues A. S. L. (2006). "Global Biodiversity Conservation Priorities". Science. 313 (5783): 58–61. Bibcode:2006Sci...313...58B. doi:10.1126/science.1127609. PMID 16825561. S2CID 5133902.
- Kareiva P.; Marvier M. (2003). "Conserving Biodiversity Coldspots" (PDF). American Scientist. 91 (4): 344–351. doi:10.1511/2003.4.344. Archived from the original (PDF) on September 6, 2006.
- Mccallum, Malcolm L.; Bury, Gwendolyn W. (2013). "Google search patterns suggest declining interest in the environment". Biodiversity and Conservation. 22 (6–7): 1355–67. Bibcode:2013BiCon..22.1355M. doi:10.1007/s10531-013-0476-6. S2CID 15593201.
- Myers, Norman; Mittermeier, Russell A.; Mittermeier, Cristina G.; da Fonseca, Gustavo A. B.; Kent, Jennifer (2000). "Biodiversity hotspots for conservation priorities". Nature. 403 (6772): 853–8. Bibcode:2000Natur.403..853M. doi:10.1038/35002501. PMID 10706275. S2CID 4414279.
- Wake, D. B.; Vredenburg, V. T. (2008). "Are we in the midst of the sixth mass extinction? A view from the world of amphibians". Proceedings of the National Academy of Sciences. 105 (Suppl 1): 11466–73. Bibcode:2008PNAS..10511466W. doi:10.1073/pnas.0801921105. PMC 2556420. PMID 18695221.
Textbooks
- Groom, Martha J.; Meffe, Gary K.; Carroll, C. Ronald. (2006). Principles of Conservation Biology. Sunderland, Mass: Sinauer Associates. ISBN 978-0-87893-597-0.
- Norse, Elliott A.; Crowder, Larry B., eds. (2005). Marine conservation biology: the science of maintaining the sea's biodiversity. Washington, DC: Island Press. ISBN 978-1-55963-662-9.
- Primack, Richard B. (2004). A primer of Conservation Biology. Sunderland, Mass: Sinauer Associates. ISBN 978-0-87893-728-8.
- Primack, Richard B. (2006). Essentials of Conservation Biology. Sunderland, Mass: Sinauer Associates. ISBN 978-0-87893-720-2.
- Wilcox, Bruce A.; Soulé, Michael E.; Soulé, Michael E. (1980). Conservation Biology: an evolutionary-ecological perspective. Sunderland, Mass: Sinauer Associates. ISBN 978-0-87893-800-1.
- Kleiman, Devra G.; Thompson, Katerina V.; Baer, Charlotte Kirk (2010). Wild Mammals in Captivity. Chicago, Illinois: University of Chicago Press. ISBN 978-0-226-44009-5.
- Scheldeman, X.; van Zonneveld, M. (2010). Training Manual on Spatial Analysis of Plant Diversity and Distribution. Bioversity International. Archived from the original on 2011-09-27.
- Sodhi, Navjot S.; Ehrlich, Paul R. (2010). Conservation biology for all. Oxford University Press. A free textbook for download.
- Sutherland, W.; et al. (2015). Sutherland, William J; Dicks, Lynn V; Ockendon, Nancy; Smith, Rebecca K (eds.). What Works in Conservation. Open Book Publishers. doi:10.11647/OBP.0060. ISBN 978-1-78374-157-1. A free textbook for download.
General non-fiction
- Christy, Bryan (2008). The Lizard King: The true crimes and passions of the world's greatest reptile smugglers. New York: Twelve. ISBN 978-0-446-58095-3.
- Nijhuis, Michelle (July 23, 2012). "Conservationists use triage to determine which species to save and not: Like battlefield medics, conservationists are being forced to explicitly apply triage to determine which creatures to save and which to let go". Scientific American. Retrieved 2017-05-07.
Periodicals
- Animal Conservation [2]
- Biological Conservation
- Conservation [3], a quarterly magazine of the Society for Conservation Biology
- Conservation and Society
- Conservation Biology, a peer-reviewed journal of the Society for Conservation Biology
- Conservation Letters
- Diversity and Distributions
- Ecology and Society
Training manuals
- White, James Emery; Kapoor-Vijay, Promila (1992). Conservation biology: a training manual for biological diversity and genetic resources. London: Commonwealth Science Council, Commonwealth Secretariat. ISBN 978-0-85092-392-6.
External links
[edit]- Conservation Biology Institute (CBI)
- United Nations Environment Programme – World Conservation Monitoring Centre (UNEP-WCMC)
- The Center for Biodiversity and Conservation – American Museum of Natural History
- Sarkar, Sahotra. "Conservation Biology". In Zalta, Edward N. (ed.). Stanford Encyclopedia of Philosophy.
- Dictionary of the History of Ideas
- Conservationevidence.com – Free access to conservation studies
Conservation biology
View on GrokipediaHistory
Origins in Natural Resource Management
Natural resource management emerged as a practical response to resource depletion in the 19th century, focusing on sustainable utilization of renewable assets such as timber, fisheries, and game populations to prevent economic collapse from overexploitation. In the United States, this approach gained traction amid rapid industrialization and westward expansion, where unregulated logging and hunting threatened supplies; for instance, by the 1890s, white pine forests in the Great Lakes region had been reduced by over 80% due to clear-cutting without regeneration plans.[14] Early efforts emphasized utilitarian principles, prioritizing long-term yield over preservation, as articulated by figures like Gifford Pinchot, who in 1905 became the first chief of the U.S. Forest Service and championed "multiple-use" policies balancing timber harvest, watershed protection, and grazing on federal lands.[15] These practices drew from European forestry traditions, such as selective cutting and coppicing systems dating to the 18th century in Germany and France, which aimed to maintain productive capacity through calculated rotation cycles.[16] In wildlife and fisheries management, similar principles applied, with state-level game laws enacted from the 1870s onward to regulate bag limits and seasons, driven by observable declines like the near-extirpation of bison herds (from 30-60 million in 1800 to fewer than 1,000 by 1890).[17] Organizations such as the Boone and Crockett Club, founded in 1887 by Theodore Roosevelt and others, promoted science-based hunting regulations to sustain populations for sport and food, funding early censuses and refuges that informed federal policies like the Lacey Act of 1900, which banned interstate trade in illegally taken wildlife.[18] Fisheries management followed suit, with the U.S. Commission of Fish and Fisheries (established 1871) pioneering stock assessments to enforce sustainable quotas, recognizing that unchecked commercial netting in the Great Lakes had halved lake whitefish yields by the 1880s.[17] These initiatives, grounded in empirical observations of population dynamics rather than broader ecological theory, formed the proto-disciplinary core of conservation biology by institutionalizing data-driven interventions to avert local extinctions and resource failure.[19] This management paradigm, however, often operated in silos—forestry separate from fisheries—lacking integration of interspecies dependencies, which later critiques from ecologists highlighted as a limitation; for example, Pinchot's focus on timber yield overlooked biodiversity losses from monoculture plantations.[14] Nonetheless, by establishing precedents for monitoring, regulation, and restoration, natural resource management provided the operational framework that conservation biology would expand into a holistic science amid escalating global threats in the 20th century.[20]Development as a Scientific Discipline
Conservation biology coalesced as a distinct scientific discipline in the late 1970s amid growing empirical evidence of accelerating species extinctions and habitat losses, prompting biologists to integrate ecological, genetic, and evolutionary principles into a unified framework for addressing biodiversity decline. The pivotal event was the First International Conference on Conservation Biology, held in September 1978 at the University of California, San Diego, organized by Michael Soulé, which assembled researchers to confront the "biodiversity crisis" through an evolutionary-ecological lens rather than traditional resource management approaches.[19] Proceedings from this conference, edited by Soulé and Bruce A. Wilcox and published in 1980 as Conservation Biology: An Evolutionary-Ecological Perspective, formalized core concepts such as minimum viable population sizes and the genetic consequences of fragmentation, laying foundational theoretical groundwork.[19] By the mid-1980s, the field advanced through institutionalization, with the founding of the Society for Conservation Biology (SCB) in 1985 by Soulé and colleagues, who served as its first president, establishing a professional network dedicated to applying scientific rigor to conservation imperatives.[21] This was followed by the launch of the peer-reviewed journal Conservation Biology in May 1987, which provided a dedicated outlet for interdisciplinary research integrating population viability analysis, landscape ecology, and policy-relevant modeling, thereby elevating the discipline's academic legitimacy.[22] Early publications emphasized crisis-driven problem-solving, drawing on data from island biogeography theory—evidenced by studies showing extinction rates 100 to 1,000 times background levels in fragmented habitats—to argue for proactive interventions over descriptive ecology alone.[23] The discipline's maturation reflected a shift from ad hoc wildlife management to a synthetic science, incorporating quantitative tools like metapopulation models and phylogenetic diversity metrics by the 1990s, while maintaining a normative commitment to halting anthropogenic biodiversity loss, as articulated in SCB's mission.[24] Despite its rapid growth—evidenced by over 10,000 citations to foundational texts by 2006—critics within ecology noted potential tensions between scientific objectivity and advocacy, though empirical validations, such as predictive successes in reintroduction programs, underscored its causal mechanisms rooted in population dynamics and habitat connectivity.[25] By the early 21st century, conservation biology had produced verifiable advancements, including IUCN Red List protocols informed by probabilistic extinction risk assessments, solidifying its status as a coherent body of theories and technologies.[24]Key Milestones and Influential Figures
The formal emergence of conservation biology as a distinct scientific discipline occurred in the mid-1980s, building on earlier environmental concerns and legislative actions. Precursors include Aldo Leopold's 1949 publication of A Sand County Almanac, which articulated a "land ethic" emphasizing the biotic community's integrity, stability, and beauty as a foundational principle for managing natural resources.[26] Rachel Carson's 1962 book Silent Spring highlighted the ecological impacts of pesticides, catalyzing public awareness of human-induced environmental degradation and influencing subsequent policy like the 1972 DDT ban. The U.S. Endangered Species Act of 1973 marked a key legislative milestone, providing a framework for protecting imperiled species and habitats, which underscored the need for scientific approaches to biodiversity preservation. In 1985, Michael Soulé published "What Is Conservation Biology?", defining the field as "a mission-oriented crisis discipline" focused on the preservation of biodiversity amid scarcity, integrating ecology, genetics, and evolutionary biology to address extinction risks.[27] That same year, the Society for Conservation Biology (SCB) was founded following the Second Conference on Conservation Biology in Ann Arbor, Michigan, establishing an institutional base for research and application.[6] The inaugural issue of the journal Conservation Biology appeared in 1987, providing a dedicated platform for peer-reviewed studies on population viability, habitat fragmentation, and metapopulation dynamics.[28] Influential figures shaped the discipline's theoretical and practical foundations. Soulé, often called the "father of conservation biology," emphasized small population paradigms and the integration of normative values with empirical science. E.O. Wilson advanced sociobiological insights into biodiversity, coining "biophilia" in 1984 to describe innate human affinity for nature, and organizing the 1988 National Forum on BioDiversity, which popularized the term and spurred global action. Thomas Lovejoy pioneered the concept of biological diversity in the 1980s, advocating debt-for-nature swaps and large-scale landscape management to mitigate deforestation in tropical regions.[29] These contributions established conservation biology's interdisciplinary scope, prioritizing evidence-based strategies over purely utilitarian resource management.Core Principles
Definition and Interdisciplinary Scope
Conservation biology is the applied scientific study of Earth's biodiversity, emphasizing the prevention of species extinctions, habitat degradation, and ecosystem collapse through empirical analysis of biological processes under anthropogenic pressures. Formally defined by Michael Soulé in 1985 as a "new synthetic discipline" that provides "principles and tools for preserving biological diversity," it addresses the dynamics of perturbed species, communities, and ecosystems by integrating core biological sciences with practical management strategies.[5][4] This mission-oriented framework, often characterized as a "crisis discipline," prioritizes halting biodiversity loss—evidenced by rates exceeding background extinction levels by factors of 100 to 1,000 since the 1980s—via data-driven interventions rather than normative assumptions alone.[30][2] The field's interdisciplinary scope spans ecology, evolutionary biology, population genetics, and systematics to quantify threats like habitat fragmentation and genetic erosion, while incorporating economics for cost-benefit analyses of conservation actions and policy sciences for implementing regulatory frameworks. For instance, it employs demographic models to predict population viability and landscape genetics to assess connectivity, drawing causal inferences from longitudinal data on factors such as invasive species introductions, which have contributed to 40% of documented animal extinctions since 1500.[31][32] Social sciences inform human dimensions, including behavioral drivers of overexploitation, but empirical validation remains central to distinguish effective measures from ideologically motivated ones, countering biases in source selection where institutional pressures may inflate perceived consensus on unverified interventions.[33] This breadth enables holistic assessments, such as integrating remote sensing data with socioeconomic metrics to prioritize reserves, ensuring decisions rest on verifiable causal mechanisms like trophic cascades rather than anecdotal advocacy.[34] At its core, conservation biology upholds the principle of biological integrity—the sustained operation of evolutionary and ecological processes without irreversible disruption—as a foundational goal, testable through metrics like species richness persistence and genetic diversity retention over decadal scales.[35] While drawing from humanities for ethical framing, its rigor demands falsifiable hypotheses and replicated studies, as seen in meta-analyses confirming that protected areas reduce deforestation by 20-30% in tropical regions when enforcement is robust.[1] This scope distinguishes it from narrower ecology by mandating actionable synthesis, fostering tools like systematic conservation planning that allocate resources based on threat probabilities and habitat representativeness, grounded in first-principles understanding of population bottlenecks and metapopulation dynamics.[8]Biodiversity Metrics and Extinction Risks
Biodiversity metrics in conservation biology primarily encompass measures of species diversity, including richness (the total number of species present), evenness (the distribution of individuals among species), and composite indices that integrate both. Species richness serves as a foundational metric, directly counting distinct taxa within a defined area or community, though it overlooks abundance and is sensitive to sampling effort.[36] The Shannon index (H'), calculated as H' = -∑(p_i * ln(p_i)) where p_i is the proportion of individuals belonging to the i-th species, quantifies entropy-like diversity by weighting rare species more heavily and typically ranges from 1.5 to 3.5 in natural ecosystems.[37] In contrast, the Simpson index (D = 1 - ∑p_i²) emphasizes dominance by common species, interpreting 1 - D as the probability that two randomly selected individuals belong to different species, and is less influenced by rare taxa.[38] Advanced metrics extend to phylogenetic diversity, which accounts for evolutionary history via branch lengths in phylogenies, and functional diversity, measuring trait variability to assess ecosystem service potential.[39] These metrics inform conservation by enabling spatial prioritization, impact assessment, and monitoring of interventions; for instance, areas with high Shannon diversity may warrant protection to preserve informational value against loss.[40] However, their application requires caution due to scale-dependence and data gaps, particularly for underrepresented taxa like insects, where extrapolations from vertebrates can inflate perceived uniformity. Empirical studies show that while local diversity hotspots correlate with global patterns, human-modified landscapes often retain functional redundancy despite reduced richness.[41] Extinction risk assessment standardizes evaluation through the IUCN Red List Categories and Criteria, which classify species into eight categories—Extinct (EX), Extinct in the Wild (EW), Critically Endangered (CR), Endangered (EN), Vulnerable (VU), Near Threatened (NT), Least Concern (LC), and Data Deficient (DD)—based on quantitative thresholds across five criteria: population reduction (A), restricted range (B), small/declining populations (C), very small populations (D), and quantitative analysis (E).[42] Criteria thresholds include, for CR, ≥90% decline over 10 years or three generations, or population <250 mature individuals; these apply globally, with regional guidelines adjusting for rescue effects.[43] As of assessments through 2023, approximately 150,000 species have been evaluated, with over 42,000 deemed threatened (CR, EN, VU), predominantly driven by habitat loss, overexploitation, and invasive species, though assessments cover <2% of described species and rely on expert judgment amid incomplete data.[42] The Red List Index (RLI) aggregates these assessments to track aggregate extinction risk trends, computed as the average conservation status across species groups, with declines indicating worsening risk; for birds, the RLI fell 11% from 1988 to 2018, reflecting persistent pressures despite some recoveries.[44] Background extinction rates from the fossil record average 0.1 to 1 extinctions per million species-years (E/MSY), whereas documented modern rates for vertebrates since 1500 equate to roughly 0.3 E/MSY, though model-based projections for all taxa suggest 100-1,000 times elevation due to habitat conversion.[45] Verified extinctions remain low—fewer than 1,000 species since 1900, mostly islands endemics—challenging narratives of imminent mass extinction, as many "threatened" listings stem from range contractions rather than imminent disappearance, and undescribed species complicate baselines.[46] Conservation efforts, informed by these metrics, have averted ~30-50 extinctions since 1993 per IUCN data, underscoring the value of targeted interventions over aggregate rate alarms.[44]Ethical and Philosophical Underpinnings
Conservation biology presupposes the normative imperative to preserve biodiversity, a stance that demands philosophical grounding beyond empirical observation alone.[47] This field grapples with foundational tensions between anthropocentric perspectives, which assign value to nature primarily through its instrumental benefits to humans—such as provisioning ecosystem services like pollination, water purification, and climate regulation—and non-anthropocentric views that posit intrinsic worth in species, ecosystems, or biotic wholes irrespective of human utility.[32] Anthropocentric ethics, rooted in utilitarian traditions, prioritize conservation actions that maximize human welfare, as evidenced by economic valuations of biodiversity loss exceeding $2.5 trillion annually in foregone services by 2011 estimates.[32] In contrast, ecocentric and biocentric frameworks challenge human-centered dominance, arguing that moral extension to non-human entities follows from evolutionary continuity and interdependence, though critics contend such intrinsic valuations lack empirical falsifiability and risk prioritizing abstract ideals over verifiable human needs.[48] A pivotal ecocentric contribution emerged from Aldo Leopold's 1949 essay "The Land Ethic," which reframed ethical membership to include the "land community"—encompassing soils, waters, plants, and animals as co-constituents rather than mere resources.[49] Leopold defined right conduct as that which "tends to preserve the integrity, stability, and beauty of the biotic community," critiquing earlier anthropocentric practices like predator eradication that disrupted ecological balances, as he observed in his shift from 1920s game management advocacy to holistic biotic integrity by the 1940s. This ethic influenced conservation biology's disciplinary ethos, embedding a presumption against actions that erode community fitness, and has been invoked in policy frameworks like the 1973 Endangered Species Act, which implicitly extends protections based on systemic rather than solely utilitarian grounds.[50] Proponents argue it fosters causal realism by recognizing feedback loops where habitat degradation undermines human sustenance, as in documented collapses of fisheries from overexploitation reducing yields by up to 90% in targeted stocks since the mid-20th century.[32] Philosophical debates persist over these underpinnings, with consequentialist approaches weighing aggregate outcomes—like net biodiversity gains against development costs—clashing against deontological claims for species rights or virtue ethics emphasizing stewardship humility.[51] Recent critiques highlight "dogmas" such as prioritizing populations over individuals or assuming novel ecosystems equate to degraded ones, urging empirical reevaluation over unexamined norms; for instance, neutral ecological theory challenges niche-based justifications for intervention by positing stochastic processes as dominant in diversity maintenance.[52][53] While traditional conservation often leans ecocentric to counter anthropocentric exploitation, evidenced by IUCN Red List criteria incorporating stability metrics since 1994, pragmatic syntheses advocate hybrid ethics tying preservation to human resilience, as pure intrinsic value struggles against population pressures projected to strain resources for 10 billion people by 2050.[54] These tensions underscore conservation biology's interdisciplinary mandate to integrate philosophical rigor with causal evidence, avoiding unsubstantiated moralism in favor of testable propositions on biotic persistence.[48]Key Concepts
Ecosystem and Species Interactions
![Biomass distribution in terrestrial ecosystems showing dominance of plants over animals and microbes][float-right] In conservation biology, ecosystem and species interactions encompass the web of relationships including predation, competition, mutualism, and symbiosis that structure communities and maintain ecological processes. These interactions determine the flow of energy and nutrients through food webs, where disruptions can propagate across trophic levels, affecting biodiversity and ecosystem function. For instance, antagonistic interactions like predation regulate population sizes, preventing overexploitation of resources, while mutualistic relationships, such as pollination, sustain reproductive success across species.[55][56] Keystone species exert disproportionate influence on their ecosystems relative to their abundance, often stabilizing structure through trophic cascades. The reintroduction of gray wolves to Yellowstone National Park in 1995 exemplifies this, as wolves reduced elk populations, alleviating browsing pressure on riparian vegetation, which in turn enhanced habitat for songbirds, beavers, and fish, demonstrating cascading benefits to biodiversity. Similarly, sea otters in Pacific kelp forests act as keystone predators by controlling sea urchin densities; their decline due to historical overhunting led to urchin overgrazing and kelp loss, but recovery efforts have restored balance, underscoring the need to prioritize such species in conservation strategies.[57][58] Co-extinctions arise when the loss of one species triggers dependent species' decline, amplifying biodiversity erosion beyond direct threats. Empirical models indicate that co-extinctions could account for a substantial portion of projected vertebrate losses from land-use and climate change, with interactions like host-parasite or pollinator-plant dependencies driving indirect extinctions. A 2023 analysis estimated that ignoring these dependencies underestimates extinction risks by up to 184% for certain taxa, highlighting the causal chain where primary extinctions cascade through interaction networks.[59][60] Higher biodiversity generally enhances ecosystem stability, as evidenced by long-term grassland experiments showing that diverse communities resist perturbations better through statistical averaging of species responses rather than perfect compensation. A 2022 study of a 25-year experiment found that species richness positively correlated with temporal stability, with diverse plots exhibiting 50-100% lower variability in productivity compared to monocultures. However, stability also depends on trophic diversity differences, where mismatches between levels can undermine resilience, informing conservation efforts to preserve interaction integrity over mere species counts.[61][62][63]Strategic Prioritization Frameworks
Strategic prioritization frameworks in conservation biology guide the allocation of scarce resources to achieve measurable biodiversity outcomes, recognizing that funding falls short of requirements estimated at $700 billion annually for nature restoration while current investments remain substantially lower.[64] These frameworks employ quantitative methods, such as optimization algorithms, to evaluate trade-offs between ecological benefits, costs, and feasibility, prioritizing actions that prevent extinctions or maintain ecosystem functions over less impactful alternatives. Empirical assessments indicate that ad hoc approaches often underperform, with systematic methods demonstrating higher efficiency in representing biodiversity features, though real-world implementation frequently lags due to governance and data limitations.[65] Systematic conservation planning (SCP) represents a foundational framework, utilizing spatial analysis to identify priority areas for protection or management that maximize representation of biodiversity surrogates like species ranges or habitats. Core principles include complementarity, which selects sites adding unique value to avoid redundancy; adequacy, ensuring sufficient coverage for long-term persistence; irreplaceability, highlighting sites with no substitutes for meeting targets; and efficiency, minimizing costs such as land acquisition or opportunity expenses.[66] Developed through applications in regions like Australia's forests and South Africa's Cape Floristic Region, SCP has informed reserve networks that achieve representation targets more effectively than arbitrary selections, with software like Marxan enabling scenario testing.[66] However, while planning exercises optimize theoretical outcomes, evidence of on-ground conservation success remains sparse, underscoring the need for integration with monitoring and adaptive management.[65] Conservation triage frameworks adapt medical triage principles to ecology, ranking species, populations, or sites by urgency of threat, potential for recovery, and resource demands to focus interventions where success probabilities are highest. A structured approach incorporates planning for cost-effective actions, governance for stakeholder engagement and policy enforcement, and knowledge co-production blending scientific data with local insights to address biases in expert assessments.[67] Applied in contexts like Chile's biodiversity programs targeting 30% protection by 2030, triage has optimized marine and terrestrial efforts under fiscal constraints, though ethical critiques argue it risks deprioritizing less charismatic taxa without utilitarian justification.[67] Proponents counter that explicit triage enhances realism over implicit neglect, with studies showing it can avert greater aggregate losses when resources are overwhelmed.[68] Despite these advances, frameworks must account for uncertainty in threat projections and implementation barriers to avoid misallocation.[67]Human-Nature Interdependence
Conservation biology underscores the mutual reliance between human societies and natural ecosystems, wherein biodiversity sustains essential services that underpin human survival, health, and economic activity. Ecosystem services are categorized into provisioning (e.g., food, freshwater, timber, and fibers), regulating (e.g., pollination, climate moderation, flood control, and water purification), cultural (e.g., recreation, aesthetic inspiration, and spiritual fulfillment), and supporting (e.g., nutrient cycling, soil formation, and primary production that maintains biodiversity itself). These services emerge from complex interactions within ecosystems, where species diversity enhances resilience against perturbations, ensuring sustained delivery; for instance, diverse microbial communities in soils facilitate nutrient availability critical for agriculture. Loss of biodiversity diminishes this capacity, as evidenced by studies showing that reduced species richness correlates with declining service provision, such as in pollinator-dependent crop yields.[69][70][71] Quantifying this interdependence reveals its scale: global ecosystem services have been valued at approximately $125–145 trillion annually as of 2011 estimates, representing a substantial fraction of human economic output, with losses from 1997 to 2011 amounting to $4.3–20.2 trillion per year due to habitat degradation and biodiversity decline. More recent analyses indicate that over half of global GDP—around $44 trillion in economic value—is moderately or highly dependent on nature, particularly through agriculture, fisheries, and raw materials extraction. Regulating services alone, such as air quality maintenance and erosion control, contribute an estimated $29 trillion annually, derived from biophysical processes reliant on intact habitats. These valuations, while subject to methodological debates over non-market benefits and discounting, derive from meta-analyses of empirical data across biomes, highlighting causal links between ecosystem integrity and human welfare; for example, coral reefs provide $350,000 per hectare yearly in fisheries and tourism support.[72][73][74][75] Human dependence manifests concretely in sectors like medicine and food security, where approximately 50,000–70,000 plant species contribute to pharmaceuticals, and biodiversity supports 75% of leading global food crops via animal pollination. Fisheries, reliant on marine biodiversity, provide protein for over 3 billion people, with overexploitation risking collapse as seen in historical cases like the Atlantic cod decline, where biomass fell 99% from pre-industrial levels, leading to socioeconomic costs exceeding $2 billion in Canada alone. Conservation strategies thus prioritize maintaining this interdependence through sustainable practices, recognizing that anthropocentric incentives—such as averting service failures that exacerbate poverty and disease—complement biodiversity preservation; empirical models show that integrating human demand into planning enhances both service delivery and species protection without trade-offs.[76][77][78]Methods and Technologies
Field Monitoring and Data Collection
Field monitoring and data collection form the empirical foundation of conservation biology, providing quantifiable metrics on species abundance, distribution, habitat condition, and population dynamics to inform evidence-based management. Standardized protocols ensure reproducibility and minimize observer bias, encompassing direct enumeration, indirect sign detection, and technological augmentation. These methods enable estimation of key parameters such as density, survival rates, and trends in biodiversity, which are critical for detecting declines before they reach critical thresholds.[79][80] Traditional field techniques include visual surveys via line transects or point counts, where observers systematically record sightings of animals or plants within defined areas, often adjusted for detectability using distance sampling to account for elusive behaviors. Capture-mark-recapture methods involve trapping individuals, marking them with tags or dyes, and recapturing to estimate population size via Lincoln-Petersen or more advanced models like Jolly-Seber, which incorporate survival and recruitment. Indirect methods detect presence through fecal pellets, tracks, or nests, proving effective for cryptic species like large mammals in dense forests. These approaches demand rigorous sampling designs to avoid pseudoreplication and ensure statistical power.[79][81] Technological innovations have expanded monitoring efficacy, particularly camera traps, which autonomously capture images triggered by motion, yielding non-invasive data on rare or nocturnal species. In comparative studies, camera traps detected 31% more species than alternative methods and generated higher detection rates, making them indispensable for large-scale biodiversity inventories. Passive acoustic monitoring records vocalizations for automated species identification via machine learning, while GPS telemetry collars track individual movements in real-time, revealing habitat use and migration patterns; for instance, such devices have quantified home ranges for over 100 mammalian species since the 1990s. Drones and satellite imagery complement ground efforts by mapping habitat changes at landscape scales.[80][82][83] Citizen science integrates public participation to scale data collection, with volunteers contributing observations through apps or protocols that verify submissions against standards, filling gaps in remote or understudied areas. Programs like eBird have amassed millions of bird records since 2002, enabling trend analyses, while similar efforts for mammals and insects support IUCN assessments. However, data quality requires validation to mitigate errors from untrained observers, often achieved through post-collection filtering or training modules.[84][85][86]Modeling and Planning Tools
Modeling and planning tools in conservation biology employ quantitative simulations and optimization algorithms to forecast ecological dynamics, assess risks, and design interventions that maximize biodiversity outcomes under resource constraints. These approaches draw on demographic, spatial, and environmental data to evaluate scenarios, such as habitat loss impacts or reserve network efficacy, enabling evidence-based prioritization over ad hoc decisions. Peer-reviewed applications demonstrate their utility in reducing uncertainty, though limitations like data scarcity and model assumptions necessitate validation against empirical observations.[87] Population viability analysis (PVA) quantifies extinction risk for focal species by integrating stochastic models of birth, death, migration, and catastrophes, often projecting persistence probabilities over decades. Originating in the 1980s, PVA has informed management for taxa like grizzly bears and Florida panthers, revealing minimum viable population sizes typically exceeding 1,000 individuals for long-term survival amid demographic variance. Criticisms highlight over-reliance on parametric assumptions, yet rigorous implementations, incorporating genetic and environmental stochasticity, enhance predictive accuracy when calibrated with longitudinal field data.[88][89][90] Systematic conservation planning tools, such as Marxan, optimize protected area configurations to achieve representation targets for biodiversity features while minimizing costs and spatial fragmentation. Marxan utilizes heuristic algorithms like simulated annealing to evaluate millions of planning units, generating compact reserve networks that satisfy complementarity and irreplaceability criteria. Deployed in over 100 countries since 2000, it has supported initiatives like Australia's Great Barrier Reef zoning, where solutions balanced ecological goals with socioeconomic factors, outperforming manual designs in efficiency. Complementary software, including Zonation, prioritizes landscapes via connectivity and threat gradients.[91][92][93] Geographic information systems (GIS) underpin spatial planning by integrating raster and vector data for habitat suitability mapping and threat modeling. In conservation, GIS overlays species occurrence with land-use layers to delineate corridors and fragmentation hotspots, as in analyses of Amazonian deforestation patterns revealing 20-30% connectivity losses per decade. Tools like ArcGIS facilitate multi-criteria decision analysis, linking biophysical variables to policy scenarios.[94][95] Species distribution models (SDMs) forecast range shifts using correlative or mechanistic approaches tied to climatic and biotic predictors, aiding proactive planning under global change. Ensemble SDMs, averaging outputs from algorithms like MaxEnt, have projected 15-37% habitat loss for European amphibians by 2050, guiding translocation priorities. Validation against independent data underscores their role, though equilibrium assumptions limit short-term accuracy in dynamic systems.[96][97] Decision support systems synthesize these models into frameworks for adaptive management, incorporating uncertainty via Bayesian updates and multi-objective optimization. Examples include tools evaluating trade-offs in restoration, where cost-benefit ratios inform investments yielding 2-5 times returns in ecosystem services. Despite biases toward quantifiable metrics, hybrid systems integrating qualitative stakeholder input improve implementation fidelity.[98][99][100]Innovations in Genetic and Digital Approaches
Advancements in conservation genomics have revolutionized the assessment of genetic health in wild populations by leveraging next-generation sequencing (NGS) technologies to generate dense genomic datasets. These tools allow researchers to quantify genetic diversity, detect inbreeding, and identify adaptive alleles at unprecedented resolution, informing decisions on population management and translocation. For instance, NGS enables the analysis of thousands of single nucleotide polymorphisms (SNPs) to evaluate effective population sizes and gene flow, which are critical for predicting extinction risks driven by genetic erosion.[101][102] Gene editing technologies, particularly CRISPR-Cas9, offer targeted interventions to bolster species resilience against environmental pressures. In laboratory settings, CRISPR has been used to edit genes in surrogate species resembling endangered ones, such as introducing disease-resistant traits in fish akin to the Delta smelt, demonstrating potential for enhancing survival without altering wild genomes directly. Similarly, gene drives engineered via CRISPR aim to suppress invasive rodent populations on islands by biasing inheritance toward sterility-inducing alleles, potentially reducing ecological damage while minimizing non-target effects through modeling. However, field applications remain limited due to ethical concerns over ecological disruptions and the need for rigorous containment strategies.[103][104] Digital innovations, including environmental DNA (eDNA) analysis powered by machine learning, provide scalable, non-invasive methods for biodiversity surveillance. eDNA captures extracellular genetic material from water, soil, or air, allowing detection of rare or cryptic species with higher sensitivity than visual surveys; metabarcoding of these samples can identify multiple taxa simultaneously from a single filtrate. Artificial intelligence enhances this by automating sequence classification and error correction in large datasets, achieving over 90% accuracy in species identification from eDNA metabarcodes in marine environments. Integration with remote sensors and predictive algorithms further enables real-time threat forecasting, such as invasive species incursions, optimizing resource allocation in conservation efforts.[105][106][107]Major Threats
Habitat Loss and Fragmentation
Habitat loss refers to the reduction in the extent and quality of natural environments essential for species survival, primarily driven by human activities such as agricultural expansion, urbanization, deforestation, and infrastructure development.[108] These processes have converted approximately 75% of terrestrial environments and 66% of marine environments from their original states.[109] Globally, tree cover loss reached a record 30 million hectares in 2024, increasing 5% from 2023, with fires contributing significantly to tropical forest decline.[110] Habitat loss ranks as the leading threat to biodiversity, affecting 88.3% of assessed species and correlating with a 73% average decline in monitored wildlife populations since 1970.[111][112] Habitat fragmentation occurs when continuous habitats are divided into isolated patches by barriers like roads, fields, or settlements, often accompanying loss but exerting effects independent of total area reduction.[113] While habitat loss directly diminishes available space and resources, fragmentation introduces edge effects—such as altered microclimates, heightened predation, and invasive species incursions—that degrade patch interiors.[114] Empirical reviews indicate that fragmentation per se yields weaker impacts on biodiversity compared to loss, with effects equally likely to be positive (e.g., via increased habitat heterogeneity fostering certain species) or negative, challenging assumptions of uniformly detrimental outcomes.[115] Nonetheless, meta-analyses confirm negative consequences for mutualistic interactions, plant richness in some contexts, and overall extinction risk, particularly for habitat specialists and large-ranging species like mammals.[116][117][118] In fragmented landscapes, reduced connectivity impairs dispersal and gene flow, elevating inbreeding depression and local extinctions, especially in small populations vulnerable to stochastic events.[119] For instance, mammalian species in highly fragmented habitats face amplified extinction risks beyond those from area loss alone, with models predicting up to 86 species committed to extinction under current trajectories, 9% attributable to fragmentation effects.[120] African savannah elephants exemplify this, as habitat division by human settlements restricts migration corridors, increasing human-wildlife conflict and population isolation.[121] Between 2000 and 2020, 19% of global protected areas experienced habitat loss, while 34% underwent fragmentation, underscoring the pervasive nature of these threats even in conserved regions.[122] Conservation responses emphasize mitigating fragmentation through corridor restoration and landscape-level planning to enhance connectivity, though empirical evidence stresses prioritizing habitat amount over configuration in resource-limited scenarios, as total loss remains the dominant driver.[115] The matrix surrounding fragments—its quality and permeability—further mediates impacts, with hostile matrices exacerbating isolation more than patch geometry alone.[119] Addressing root causes like agricultural intensification and urban sprawl requires integrating spatial analyses to balance development pressures with biodiversity persistence.[108]Overexploitation and Invasive Species
Overexploitation occurs when human harvesting of wild populations exceeds their capacity for replenishment, resulting in sustained declines that threaten biodiversity and ecosystem stability.[123] In assessments of 20,784 species, overexploitation impacts 26.6%, ranking as the second most prevalent direct threat after habitat loss.[111] This pressure manifests through activities such as commercial fishing, hunting for bushmeat or trophies, and unregulated logging, often amplified by improved technologies like industrial trawlers that deplete stocks faster than natural recovery rates.[124] Marine overfishing exemplifies cascading ecosystem effects, where removal of top predators disrupts food webs and favors less desirable species. Over one-third of shark and ray species face extinction risk primarily from overexploitation, with populations like the thorny skate declining sharply due to targeted fisheries.[124] The collapse of the Newfoundland cod fishery in 1992, following decades of harvests exceeding sustainable yields estimated at 200,000-300,000 tons annually, led to a moratorium and persistent low biomass levels, illustrating how overexploitation can shift ecosystems toward jellyfish-dominated states with reduced productivity.[125] Terrestrial cases include rapid declines in large mammals post-regulatory collapse in Belarus, where hunting surged and populations of elk and wild boar dropped by up to 80% within years due to unchecked exploitation.[126] Invasive species, defined as non-native organisms that establish, spread, and cause ecological or economic harm, exacerbate biodiversity loss by altering native community structures through mechanisms like predation, competition, and habitat modification.[127] Empirical analyses of 1,551 cases reveal significant negative impacts on resident species in 63.3% of instances, particularly affecting plant outcomes via resource competition and animal populations through direct predation.[128] Globally, invasive alien species contribute to native extinctions and drive losses exceeding $423 billion annually to economies via agricultural damage, health costs, and reduced ecosystem services.[129] Notable examples include the brown tree snake in Guam, which eradicated 10-12 native bird species after introduction in the 1940s by preying on eggs, juveniles, and adults lacking evolved defenses, leading to silent forests and broader trophic disruptions.[130] In aquatic systems, zebra mussels filter vast water volumes, outcompeting natives and altering nutrient cycles, with invasions linked to declines in unionid mussel diversity by over 90% in affected North American lakes.[131] Eradication efforts, such as removing rats, cats, and goats from islands, achieve success rates around 88%, yielding biodiversity recoveries like seabird population rebounds and vegetation restoration, with benefit-cost ratios often exceeding 4:1 in preserved habitats.[132] These interventions underscore causal links between invasive removal and native resilience, though challenges persist in continental settings due to reinvasion risks.[133]Climate Variability and Pollution
Climate variability, including alterations in temperature regimes, precipitation patterns, and the frequency of extreme weather events, exerts selective pressures on biodiversity by disrupting physiological tolerances, reproductive timings, and interspecies interactions. Empirical analyses of species responses reveal shifts in morphology, behavior, and phenology, alongside geographic redistributions, as primary adaptations to these changes. For example, a survey of researchers documented that 87% observed northward or upward species movements and 78% noted earlier seasonal events, such as breeding or migration, attributable to warming trends. However, systematic reviews of range-shift data indicate that only 46.6% of observations align with predicted poleward, upslope, or deeper-water migrations, with barriers like dispersal limitations and habitat constraints impeding many species from tracking optimal climates. In avian communities across the United States, climate effects manifest heterogeneously, with some regions experiencing biodiversity declines while others see compositional reshuffling due to differential sensitivities among species. Ecosystem-level responses to variability further complicate conservation dynamics. Regions with greater plant diversity demonstrate reduced sensitivity to temperature fluctuations, as diverse assemblages buffer against temporal instability in productivity and resource availability. Nonetheless, projected climate scenarios for 2081–2100 under IPCC models forecast heightened extinction risks for vulnerable taxa, particularly in montane and polar habitats where elevational or latitudinal options are constrained. Coral reef systems exemplify acute vulnerabilities, with recurrent bleaching events tied to marine heatwaves correlating to biomass losses exceeding 30% in affected areas during episodes like the 2014–2017 global event. These patterns underscore causal links between variability and demographic declines, though adaptive capacities vary, with generalist species often faring better than specialists reliant on narrow thermal niches. Pollution, encompassing chemical effluents, particulates, plastics, and acoustic disturbances, imposes direct toxicological and ecological burdens on species and habitats, often amplifying synergies with habitat degradation. Air pollutants, including nitrogen oxides and ozone, impair pollinator function and plant reproduction, with meta-analyses confirming negative effects on visitation rates and seed set in contaminated landscapes. Global syntheses attribute local species richness reductions of approximately 20% to human pressures, including pollution, across terrestrial, freshwater, and marine realms, with vertebrates and invertebrates showing pronounced compositional shifts away from pre-industrial baselines. Microplastic ingestion disrupts endocrine systems and gut microbiomes in wildlife, leading to reduced fecundity and survival; laboratory and field studies report bioaccumulation factors exceeding 10^3 in top predators like seabirds and marine mammals. Aquatic ecosystems face compounded threats from nutrient runoff and heavy metals, fostering eutrophication and hypoxic zones that have eliminated billions of fish annually in events like the Gulf of Mexico dead zone, spanning over 15,000 km² in peak years. Noise pollution from anthropogenic sources alters behavioral ecology, with systematic maps evidencing disrupted foraging and communication in over 100 species, correlating to population declines in noise-exposed habitats. Forested areas under chronic air pollution exhibit suppressed photosynthetic efficiency and heightened susceptibility to pests, as evidenced by elevated mortality in ozone-impacted stands. Conservation responses must prioritize pollution mitigation to avert cascading extinctions, given its role as a modifiable driver orthogonal to climatic forcings.Strategies and Interventions
Protected Areas and Landscape Management
Protected areas encompass designated terrestrial, marine, and freshwater zones managed primarily for biodiversity conservation, ecosystem services, and cultural values, often through legal frameworks like national parks, reserves, and wildlife sanctuaries. Globally, as of October 2024, 17.6% of land and inland waters and 8.4% of oceans and coastal areas fall within protected or conserved areas, according to the IUCN's Protected Planet Report.[134] These designations aim to halt habitat loss, but effectiveness varies; a 2023 study across tropical regions found protected areas reduced deforestation by 39% and forest degradation by 25% compared to unprotected lands.[135] However, many sites suffer from inadequate funding and enforcement, leading to "paper parks" where illegal logging persists despite formal status.[136] Management of protected areas involves zoning, patrolling, and restoration to maintain ecological integrity, with IUCN categories ranging from strict no-take zones (Ia) to sustainably managed landscapes (VI). Peer-reviewed analyses indicate that well-enforced areas preserve species richness and habitat connectivity better than adjacent unmanaged lands, though outcomes depend on governance; for instance, collaborative indigenous-state partnerships have decreased tree cover loss by 55% annually in some forests.[137] Challenges include encroachment from agriculture and mining, exacerbated in biodiversity hotspots where only 81% of key biodiversity areas receive full protection.[138] Despite progress toward the 30x30 target of conserving 30% of Earth's surface by 2030, current coverage inadequately safeguards migratory species or fragmented habitats, necessitating integration with broader landscape approaches.[134] Landscape management extends conservation beyond isolated protected areas by addressing habitat fragmentation through connectivity enhancements, such as wildlife corridors that facilitate animal movement and gene flow. These strategies mitigate isolation effects, where small, disconnected reserves risk local extinctions; modeling shows corridors can boost population viability for wide-ranging species like large mammals.[139] Examples include the Florida Wildlife Corridor, spanning 18 million acres to link habitats for panthers and bears, and Nepal's Barandabhar Corridor supporting rhino dispersal.[140] Effective implementation involves prioritizing linkages via tools like Omniscape for spatially explicit planning, balancing restoration with land-use pressures from agriculture.[141] Key principles for landscape-scale conservation emphasize multifunctional land use, integrating biodiversity goals with human activities to avoid conflicts; a 2013 framework outlines ten such principles, including adaptive management and stakeholder coordination to reconcile agriculture with habitat retention.[142] Empirical assessments reveal that connectivity-focused strategies, like reducing road barriers with wildlife crossings, enhance ecosystem resilience more than expanding static reserves alone, particularly under climate-induced shifts.[143] Yet, success hinges on addressing threats like invasive infrastructure; in fragmented regions, unprotected matrix lands often determine overall biodiversity persistence, underscoring the need for permeable agricultural and urban designs.[144]Market Incentives and Private Initiatives
Market incentives in conservation biology leverage economic tools to align private interests with biodiversity goals, primarily through payments for ecosystem services (PES) and tradable permit systems. PES schemes compensate landowners for providing quantifiable environmental benefits, such as watershed protection or carbon storage, often verified via monitoring. A review of 38 PES programs worldwide indicated modest success in reducing deforestation rates, with most achieving stabilization or slight increases in forest cover rather than reversal of losses, though outcomes varied by program design and enforcement.[145] In Mexico's PROREDD program, redesigned contracts with full enrollment reduced deforestation by 41% compared to traditional partial-payment models, demonstrating that conditional incentives tied to verifiable actions enhance cost-effectiveness.[146] Biodiversity offsets and conservation banking represent another key mechanism, enabling developers to mitigate habitat impacts by funding equivalent or superior conservation elsewhere. Under the U.S. Endangered Species Act, conservation banks—privately managed reserves generating tradable credits—have operated since the 1980s, with over 200 banks established by 2020 conserving habitats for species like the gopher tortoise and California gnatcatcher across millions of acres. Empirical assessments show these banks often yield higher ecological value than project-specific offsets, as consolidated reserves support larger populations and natural processes, though additionality (preventing harm that would otherwise occur) remains debated in some cases.[147][148] Internationally, offset policies in Australia and the EU have scaled similar models, but success hinges on strict no-net-loss standards and independent verification to avoid greenwashing.[149] Private initiatives, driven by landowners, philanthropists, and corporations without direct government mandates, have preserved significant lands through voluntary easements and stewardship. In the U.S., organizations like the New England Forestry Foundation facilitated the conservation of 1,196 acres across four states in a single 25-day campaign in 2017 via private partnerships, emphasizing sustainable forestry that maintains biodiversity.[150] Market-oriented private efforts, such as eco-labeling for sustainable products and corporate habitat restoration, have also proliferated; for instance, voluntary rewilding on private ranches in the American West has restored bison populations on over 1 million acres, leveraging property rights to generate revenue from ecotourism and grazing leases.[151] These approaches often outperform regulatory mandates in flexibility and innovation, as evidenced by higher participation rates in incentive-based programs, though they require robust property rights to prevent free-rider problems.[152] Overall, while market incentives demonstrate causal links to conserved outcomes in controlled studies, long-term efficacy depends on adaptive design amid economic pressures.[153]Species Recovery and Population Interventions
Captive breeding programs serve as a cornerstone of species recovery for taxa facing acute population declines, enabling the propagation of individuals in controlled environments to mitigate inbreeding depression and bolster genetic diversity prior to reintroduction. These efforts often integrate veterinary care, genetic monitoring, and behavioral conditioning to enhance post-release survival, though success hinges on addressing underlying threats like habitat loss. For instance, the black-footed ferret (Mustela nigripes) program, initiated after the capture of the last 18 wild individuals in 1981, has produced over 9,600 offspring through ex situ breeding at accredited facilities, facilitating reintroductions across 24 sites in North America with approximately 400-500 ferrets persisting in the wild as of 2024.[154][155] Recent genetic interventions, including the birth of cloned kits in 2024 from a female derived from 1980s genetic material, aim to counteract the species' reliance on just seven founding ancestors, which limits adaptive potential.[156] Reintroduction and translocation interventions relocate individuals to former or suitable habitats to restore population viability, often complemented by habitat enhancement and predator control. The peregrine falcon (Falco peregrinus) recovery illustrates this approach: following a mid-20th-century population crash from 324 territorial pairs in 1970 to near extirpation in the contiguous U.S. due to DDT bioaccumulation, regulatory bans in 1972 and hacking techniques—releasing fledglings from artificial nests—yielded a rebound to over 2,000 pairs by 1999, enabling federal delisting.[157][158] Similarly, under the U.S. Endangered Species Act (ESA), integrated population interventions have contributed to the delisting of over 100 species based on recovery since 1973, including bald eagles and American peregrine falcons, with the ESA averting extinction in 99% of listed taxa.[159] Translocations, such as those for island endemics, further exemplify targeted interventions; a 2022 study on an elephant population (Loxodonta africana) in South Africa showed that culling and translocation reduced density-dependent declines but required concurrent drought mitigation to sustain growth.[160] ![Wapiti from Wagon Trails showing historical populations relevant to reintroduction efforts][float-right]Population augmentation, including supplementary feeding and vaccination, addresses demographic bottlenecks in fragmented habitats. Empirical analyses indicate that species with implemented interventions—particularly those previously at high extinction risk—exhibit improved trends, with a 2024 IUCN study finding conservation actions halved population declines in 47% of assessed cases. However, post-release survival remains variable, with captive-bred carnivores experiencing 20-30% lower first-year persistence than wild-caught counterparts due to impaired foraging and predator avoidance skills, underscoring the need for pre-release training.[161] Overall, while reintroduction success rates average 26-53% across meta-analyses, practitioner surveys report up to 60% when threats are controlled, emphasizing causal linkages between intervention scale and outcomes.[162]
