Difference between revisions of "Biodiversity" - New World Encyclopedia

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===Hotspots of biodiversity===
 
===Hotspots of biodiversity===
One definition of a [[biodiversity hotspot]] is a region with many [[endemic (ecology)|endemic]] species.   These biodiversity hotspots were first identified by Dr. Norman Myers in two articles in the scientific journal ''The Environmentalist'' (1988 and 1990). Hotspots unfortunately tend to occur in areas of significant human impact, leading to threats to their many endemic species.  As a result of the pressures of the growing human population, human activity in many of these areas is increasing dramatically.  Most of these hotspots are located in the [[tropics]] and most of them are forests.
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One definition of a [[biodiversity hotspot]] is a region with many endemic species, or species exclusively native to a place or biota. As a result of the pressures of the growing human population, human activity in many of these areas is increasing dramatically, leading to threats to endemic species. These biodiversity hotspots were first identified by Dr. Norman Myers in two articles in the scientific journal ''The Environmentalist'' (1988 and 1990).  As a result of the pressures of the growing human population, human activity in many of these areas is increasing dramatically.  Most of these hotspots are located in the [[tropics]] and most of them are forests.
  
 
Some examples are the following:
 
Some examples are the following:
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During the last century, [[biodiversity erosion|erosion of biodiversity]] has been increasingly observed. Estimates of extinction rates are controversial, ranging from very low to upwards of 200 species a day{{Citation needed}}, but all scientists acknowledge that the rate of species loss is greater now than at any time in human history, with extinctions occurring at rates hundreds of times higher than [[background extinction]] rates.
 
During the last century, [[biodiversity erosion|erosion of biodiversity]] has been increasingly observed. Estimates of extinction rates are controversial, ranging from very low to upwards of 200 species a day{{Citation needed}}, but all scientists acknowledge that the rate of species loss is greater now than at any time in human history, with extinctions occurring at rates hundreds of times higher than [[background extinction]] rates.
  
Some studies show that about one of eight known plant species is threatened with [[extinction]]. Some estimates put the loss at thousands of species per year, though these are based on [[Species-area theory]] and are controversial<!--must find reference—>. This figure indicates [[sustainability|unsustainable]] ecological practices, because only a small number of species come into being each year. All agree that the losses are due to human activities, in particular destruction of plant and animal [[habitat (ecology)|habitats]].<!--must find reference—>
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Conservationists maintain that human growth and development is leading to an [[extinction]] rate similar to the end of the Permian and Cretaceous eras, where about 50% of the species in the fossil record died out (Raup and Sakowksi 1984). Some estimates put the loss at thousands of species per year, though these are based on [[Species-area theory]] and are controversial<!--must find reference—>. This figure indicates [[sustainability|unsustainable]] ecological practices, because only a small number of species come into being each year.  
  
 
An increasing number of studies indicate that elevated rates of extinction are being driven by human [[consumption]] of organic resources. While most of the species that are becoming extinct are not food species, their [[biomass]] is converted into human food when their habitat is transformed into [[pasture]], [[cropland]], and [[orchards]]. It is estimated that more than 40% of the Earth's biomass is tied up in only the few species that represent [[humans]], our [[livestock]] and [[agriculture|crops]].<!--must find reference—> Because an [[ecosystem]] decreases in stability as its species are made extinct, these studies warn that the global ecosystem is destined for collapse if it is further reduced in complexity.
 
An increasing number of studies indicate that elevated rates of extinction are being driven by human [[consumption]] of organic resources. While most of the species that are becoming extinct are not food species, their [[biomass]] is converted into human food when their habitat is transformed into [[pasture]], [[cropland]], and [[orchards]]. It is estimated that more than 40% of the Earth's biomass is tied up in only the few species that represent [[humans]], our [[livestock]] and [[agriculture|crops]].<!--must find reference—> Because an [[ecosystem]] decreases in stability as its species are made extinct, these studies warn that the global ecosystem is destined for collapse if it is further reduced in complexity.

Revision as of 17:37, 2 June 2006

Rainforests are the most biodiverse ecosystems on earth

Biodiversity or biological diversity is the diversity of life. There are a number of definitions and measures of biodiversity, ranging from community(a group of organisms that live in a given place) or ecosystem level to the global level.

Etymology

Biodiversity is a neologism and a portmanteau word, from biological and diversity. The term biological diversity was coined by Thomas Lovejoy, tropical and conservation biologist and chief biodiversity adviser to the president of the World Bank, senior adviser to the president of the United Nations Foundation, and president of the Heinz Center for Science, Economics, and the Environment. The word biodiversity itself was coined by W.G. Rosen in 1985 while planning the 1986 National Forum on Biological Diversity organized by the National Research Council (NRC). The term first appeared in a publication in 1988 when entomologist E. O. Wilson used it as the title of the proceedings [1] of that forum[2]. The word biodiversity was deemed more effective in terms of communication than biological diversity.

Since 1986 the terms and the concept have achieved widespread use among biologists, environmentalists, political leaders, and concerned citizens worldwide. This use has coincided with the expansion of concern over extinction observed in the last decades of the 20th century.

Definitions

Biological diversity has no single standard definition. One definition holds that biological diversity is a measure of the relative diversity among organisms present in different ecosystems(Gaston and Spi Diversity in this definition includes diversity within species and among species, and comparative diversity among ecosystems.

Another definition, simpler and clearer, but more challenging, is the totality of genes, species, and ecosystems of a region. An advantage of this definition is that it seems to describe most instances of its use, and one possibly unified view of the traditional three levels at which biodiversity has been identified:

Intraspecific diversity within Dog
  • genetic diversity - diversity of genes within a species. There is a genetic variability among the populations and the individuals of the same species
  • species diversity - diversity among species
  • ecosystem diversity - diversity at a higher level of organization, the ecosystem (richness in the different processes to which the genes ultimately contribute)

The lattermost definition, which conforms to the traditional five organization layers in biology, provides additional justification for multilevel approaches.

The 1992 United Nations Earth Summit in Rio de Janeiro defined biodiversity as "the variability among living organisms from all sources, including, inter alia, terrestrial, marine, and other aquatic ecosystems, and the ecological complexes of which they are part: this includes diversity within species, between species and of ecosystems".

This is, in fact, the closest thing to a single legally accepted definition of biodiversity, since it is the definition adopted by the United Nations Convention on Biological Diversity. The parties to this convention include all the countries on Earth, with the exception of Andorra, Brunei Darussalam, the Holy See, Iraq, Somalia, Timor-Leste, and the United States of America.

If the gene is the fundamental unit of natural selection, thus of evolution, some, like E. O. Wilson, say that the real biodiversity is the genetic diversity. However, the species diversity is the easiest one to study.

For geneticists, biodiversity is the diversity of genes and organisms. They study processes such as mutations, gene exchanges, and genome dynamics that occur at the DNA level and generate evolution.

For biologists, biodiversity is the diversity of populations of organisms and species, but also the way these organisms function. Organisms appear and disappear; sites are colonized by organisms of the same species or by another. Some species develop social organizations to improve their reproduction goals or use neighbor species that live in communities. Depending on their environment, organisms do not invariably use the same strategies of reproduction.

For ecologists, biodiversity is also the diversity of durable interactions among species. It not only applies to species, but also to their immediate environment (biotope) and the ecoregions the organisms live in. In each ecosystem, living organisms are part of a whole; they interact with one another, but also with the air, water, and soil that surround them.

Measurement of biodiversity

See also main article: diversity index.

No single objective measure of biodiversity is possible, only measures relating to particular purposes or applications.

For practical conservationists, this measure should quantify a value that is at the same time broadly shared among locally affected people.

For others, a broader and economically more defensible definition is that measures should allow the ensuring of continued possibilities for both adaptation and future use by people, assuring environmental sustainability. As a consequence, biologists argued that this measure is likely to be associated with the variety of genes. Since it cannot always be said which genes are more likely to prove beneficial, the best choice for conservation is to assure the persistence of as many genes as possible.

For ecologists, this approach is sometimes considered inadequate and too restricted.

There are three common metrics used to measure species-level biodiversity.

  • Species richness
  • Simpson index
  • Shannon-Wiener index

These are either biased towards species richness or species evenness.

Biodiversity is usually plotted as taxonomic richness of a geographic area over a temporal scale. Whittaker (1972) described three terms for measuring biodiversity over geographic scales:

  • Alpha diversity refers to diversity within a particular area,community or ecosystem, and is measured by counting the number of taxa within the ecosystem (usually species)
  • Beta diversity is species diversity between ecosystems; this involves comparing the number of taxa that are unique to each of the ecosystems.
  • Gamma diversity is a measure of the overall diversity for different ecosystems within a region.
(Whittaker, R.H. (1972). Evolution and measurement of species diversity. Taxon, 21, 213-251.)

Distribution of biodiversity

Biodiversity is not distributed evenly on earth. Biodiversity is generally highest in the tropics, lowest in the subtropical latitudes (desert regions) and the poles (tundra, high latitude deserts). Flora and fauna vary depending on climate, altitude, soils and the presence of other species. Biodiversity is also an important aspect of the study of ecoregions, a relatively large area of land or water that contains a geographically distinct assemblage of natural communities. The biodiversity of flora, fauna and ecosystems that characterise an ecoregion tend to be distinct from that of other ecoregions. World Wildlife Fund ecologists currently divide the land surface of the Earth into 8 major ecozones containing 867 smaller terrestrial ecoregions. Many consider this classification to be quite decisive, and some propose these as stable borders for bioregional democracy initiatives.

The ecozones are very well-defined, following major continental boundaries, while the ecoregions are subject to more change and controversy.

Hotspots of biodiversity

One definition of a biodiversity hotspot is a region with many endemic species, or species exclusively native to a place or biota. As a result of the pressures of the growing human population, human activity in many of these areas is increasing dramatically, leading to threats to endemic species. These biodiversity hotspots were first identified by Dr. Norman Myers in two articles in the scientific journal The Environmentalist (1988 and 1990). As a result of the pressures of the growing human population, human activity in many of these areas is increasing dramatically. Most of these hotspots are located in the tropics and most of them are forests.

Some examples are the following:

  • Brazil's Atlantic Forest contains roughly 20,000 plant species, 1,350 vertebrates, and millions of insects, just under half of which are thought to occur nowhere else in the world.

See also: biogeography, Amazonian forest, extinction, unified neutral theory of biodiversity.

Biodiversity and evolution

Apparent marine fossil diversity during the Phanerozoic

Biodiversity found on Earth today is the result of 4 billion years of evolution.

The original origin of life is not well known to science, though limited evidence suggests that life may already have been well-established only a few 100 million years after the formation of the Earth. Until approximately 600 million years ago, all life consisted of bacteria and similar single-celled organisms.

The history of biodiversity during the Phanerozoic (the last 540 million years), starts with rapid growth during the Cambrian explosion—a period during which nearly every phylum of multicellular organisms first appeared. Over the next 400 million years or so, global diversity showed little overall trend, but was marked by periodic, massive losses of diversity classified as mass extinction events.

The apparent biodiversity shown in the fossil record suggests that the last few million years include the period of greatest biodiversity in the Earth's history. However, not all scientists support this view, since there is considerable uncertainty as to how strongly the fossil record is biased by the greater availability and preservation of recent geologic sections. Some (e.g. Alroy et al. 2001) argue that corrected for sampling artifacts, modern biodiversity is not much different than biodiversity 300 million years ago. Estimates of the present global macroscopic species diversity vary from 2 million to 100 million species, with a best estimate of somewhere near 10 million.

Most biologists agree however that the period since the emergence of humans is part of a new mass extinction, the Holocene extinction event, caused primarily by the impact humans are having on the environment. At present, the number of species estimated to have gone extinct as a result of human action is still far smaller than are observed during the major mass extinctions of the geological past. However, it has been argued that the present rate of extinction is sufficient to create a major mass extinction in less than 100 years. Others dispute this and suggest that the present rate of extinctions could be sustained for many thousands of years before the loss of biodiversity matches the more than 20% losses seen in past global extinction events.

New species are regularly discovered (on average about three new species of birds each year) and many, though discovered, are not yet classified (an estimate states that about 40% of freshwater fish from South America are not yet classified). Most of the terrestrial diversity is found in tropical forests.

Benefits of biodiversity

Biodiversity has contributed in many ways to the development of human culture, and, in turn, human communities have played a major role in shaping the diversity of nature at the genetic, species, and ecological levels.

There are three main reasons commonly cited in the literature for the benefits of biodiversity.

Ecological role of biodiversity

All species provide some kind of function to an ecosystem. They can capture and store energy, produce organic material, decompose organic material, help to cycle water and nutrients throughout the ecosystem, control erosion or pests, fix atmospheric gases, or help regulate climate.

Ecosystems also provide various supports of production (soil fertility, pollinators of plants, predators, decomposition of wastes...) and services such as purification of the air and water, stabilisation and moderation of the climate, decrease of flooding, drought, and other environmental disasters.

These functions are important for ecosystem function and human survival.

Research suggests that a more diverse ecosystem is better able to withstand environmental stress and consequently is more productive. The loss of a species is thus likely to decrease the ability of the system to maintain itself or to recover from damage or disturbance. Just like a species with high genetic diversity, an ecosystem with high biodiversity may have a greater chance of adapting to environmental change. In other words, the more species comprising an ecosystem, the more stable the ecosystem is likely to be. The mechanisms underlying these effects are complex and hotly contested. In recent years, however, it has become clear that there are real ecological effects of biodiversity.

Unusual and wild strains of maize are collected to increase the crop diversity when selectively breeding domestic corn.

Economic role of biodiversity

For all humans, biodiversity is first a resource for daily life. One important part of biodiversity is 'crop diversity', which is also called agrobiodiversity.

Most people see biodiversity as a reservoir of resources to be drawn upon for the manufacture of food, pharmaceutical, and cosmetic products. This concept of biological resources management probably explains most fears of resources disappearance related to the erosion of the biodiversity. However, it is also the origin of new conflicts dealing with rules of division and appropriation of natural resources.

Some of the important economic commodities that biodiversity supplies to humankind are:

  • food : crops, livestock, forestry, and fish; (see also local food)
  • medication. Wild plant species have been used for medicinal purposes since before the beginning of recorded history. For example, quinine comes from the cinchona tree (used to treat malaria), digitalis from the foxglove plant (chronic heart trouble), and morphine from the poppy plant (pain relief). According to the National Cancer Institute, over 70 % of the promising anti-cancer drugs come from plants in the tropical rainforests. Animals may also play a role, in particular in research. It is estimated that of the 250,000 known plant species, only 5,000 have been researched for possible medical applications.
  • industry : for example, fibers for clothing, wood for shelter and warmth. Biodiversity may be a source of energy (such as biomass). Other industrial products are oils, lubricants, perfumes, fragrances, dyes, paper, waxes, rubber, latexes, resins, poisons, and cork, which can all be derived from various plant species. Supplies from animal origin include wool, silk, fur, leather, lubricants, and waxes. Animals may also be used as a mode of transport.
  • tourism and recreation : biodiversity is a source of economical wealth for many areas, such as many parks and forests, where wild nature and animals are a source of beauty and joy for many people. Ecotourism, in particular, is a growing outdoor recreational activity.

Ecologists and environmentalists were the first to insist on the economic aspect of biological diversity protection. Thus, E. O. Wilson wrote in 1992 that : The biodiversity is the one of the bigger wealths of the planet, and nevertheless the less recognized as such.

Estimation of the value of biodiversity is a necessary precondition to any discussion on the distribution of biodiversity richnesses. This value can be divided into use value (direct such as tourism or indirect such as pollination) and non-use or intrinsic value.

If biological resources represent an ecological interest for the community, their economic value is also increasing. New products are developed because of biotechnologies, and new markets created. For society, biodiversity also is a field of activity and profit. It requires a proper management setup to determine how these resources are to be used.

The majority of species have yet to be evaluated for their current or future economic importance.

Ethical role of biodiversity

Finally, biodiversity has an ethical role if humans consider that other species have an intrinsic right to exist. Ecophilosophies such as deep ecology assert that a recognition of this intrinsic right makes it morally wrong to voluntarily cause extinction. The level of biodiversity is a good indicator of the state of our relationships with other living species. Biodiversity is also part of many cultures' spiritual heritage (see indigenous people and cultural diversity).

Scientific role of biodiversity

This is a fourth benefit separate from the three main ones. Biodiversity is important because each species can give scientists some clue as to how life evolved and will continue to evolve on Earth. In addition, biodiversity helps scientists understand how life functions and the role of each species in sustaining ecosystems.

See also Environmental economics

Threats to biodiversity

During the last century, erosion of biodiversity has been increasingly observed. Estimates of extinction rates are controversial, ranging from very low to upwards of 200 species a day[citation needed], but all scientists acknowledge that the rate of species loss is greater now than at any time in human history, with extinctions occurring at rates hundreds of times higher than background extinction rates.

Conservationists maintain that human growth and development is leading to an extinction rate similar to the end of the Permian and Cretaceous eras, where about 50% of the species in the fossil record died out (Raup and Sakowksi 1984). Some estimates put the loss at thousands of species per year, though these are based on Species-area theory and are controversial. This figure indicates unsustainable ecological practices, because only a small number of species come into being each year.

An increasing number of studies indicate that elevated rates of extinction are being driven by human consumption of organic resources. While most of the species that are becoming extinct are not food species, their biomass is converted into human food when their habitat is transformed into pasture, cropland, and orchards. It is estimated that more than 40% of the Earth's biomass is tied up in only the few species that represent humans, our livestock and crops. Because an ecosystem decreases in stability as its species are made extinct, these studies warn that the global ecosystem is destined for collapse if it is further reduced in complexity.

Some justify this situation not so much by a species overuse or ecosystem degradation as by their conversion in very standardized ecosystems (e.g., monoculture following deforestation). Before 1992, others pointed out that no property rights or no access regulation of resources necessarily lead to their decrease (degrading costs having to be supported by the community).

There are also the issues of pollution by human activity and global warming or climate change, driven by human activity. These have not yet been proven to have caused reduction in biodiversity but the potential for them to do so is clear.

Dissenters (notably economist Bjørn Lomborg) argue that there is not enough data to support the view of mass extinction, and say abusive extrapolations are being made on the global destruction of rainforests, coral reefs, mangrove swamps, and other rich habitats.

There is also a growing awareness that the movement and the introduction of exotic species around the world by humans is a potent threat to biodiversity.

When exotic species are introduced to ecosystems by humans and establish self-sustaining populations, the endemic species in that ecosystem, that have not evolved to cope with the exotic species in question, cannot automatically be expected to survive. Indeed, in many situations some will not. The exotic organisms in questions may be predators and/or have features due to their evolutionary background and environment that makes them very competitive, and similarly makes endemic species very defenceless and/or uncompetitive against these exotic species.

The rich diversity of unique species across many parts of the world that humans treasure exist only because they are separated by barriers - particularly seas and oceans - from other species of other land masses, particularly the highly fecund, ultra-competitive, generalist "super-species". These are barriers that could never be crossed by natural processes, except for many millions of years in the future through continental drift. However human beings have invented ships and aeroplanes. Now human beings have the power to bring into contact species that would never have encountered each other in their evolutionary history, and to do it with ease in weeks, days or even just hours.

As a consequence of the above, if human beings continue to unleash species of the world against each other by introductions - species that otherwise would never have encountered each other in their evolutionary history - some fear that it is possible that many of the world's ecosystems will end up dominated by a very few, cosmopolitan "super-species".

Biodiversity management: conservation, preservation and protection

The conservation of biological diversity has become a global concern. Although not everybody agrees on extent and significance of current extinction, most consider biodiversity essential. There are basically two main types of conservation options, in-situ conservation and ex-situ conservation. In-situ is usually seen as the ultimate conservation strategy. However, its implementation is sometimes unfeasible. For example, destruction of rare or endangered species' habitats sometimes requires ex-situ conservation efforts. Furthermore, ex-situ conservation can provide a backup solution to in-situ conservation projects. Some believe both types of conservation are required to ensure proper preservation. An example of an in-situ conservation effort is the setting-up of protection areas. An example of an ex-situ conservation effort, by contrast, would be planting germplasts in seedbanks. Such efforts allow the preservation of large populations of plants with minimal genetic erosion.

The threat to biological diversity was among the hot topics discussed at the UN World Summit for Sustainable Development, in hope of seeing the foundation of a Global Conservation Trust to help maintain plant collections.

See also: Conservation ethic, Earth Day, Global 200, IUCN, Seedbank, World Ocean Day.

Juridical status of biological diversity

Biodiversity must be evaluated and its evolution analysed (through observations, inventories, conservation...) then it must be taken into account in political decisions. It is beginning to receive a juridical setting.

  • "Law and ecosystems" relationship is very ancient and has consequences for biodiversity. It is related to property rights, private and public. It can define protection for threatened ecosystems, but also some rights and duties (for example, fishing rights, hunting rights).
  • "Laws and species" is a more recent issue. It defines species that must be protected because threatened by extinction. Some people question application of these laws. The U.S. Endangered Species Act is an example of an attempt to address the "law and species" issue.
  • "Laws and genes" is only about a century old. While the genetic approach is not new (domestication, plant traditional selection methods), progress made in the genetic field in the past 20 years lead to the obligation to tighten laws. With the new technologies of genetic and genetic engineering, people are going through gene patenting, processes patenting, and a totally new concept of genetic resource. A very hot debate today seeks to define whether the resource is the gene, the organism, the DNA or the processes.

The 1972 UNESCO convention established that biological resources, such as plants, were the common heritage of mankind. These rules probably inspired the creation of great public banks of genetic resources, located outside the source-countries.

New global agreements (e.g.Convention on Biological Diversity), now give sovereign national rights over biological resources (not property). The idea of static conservation of biodiversity is disappearing and being replaced by the idea of dynamic conservation, through the notion of resource and innovation.

The new agreements commit countries to conserve biodiversity, develop resources for sustainability and share the benefits resulting from their use. Under these new rules, it is expected that bioprospecting or collection of natural products has to be allowed by the biodiversity-rich country, in exchange for a share of the benefits.

Sovereignty principles can rely upon what is better known as Access and Benefit Sharing Agreements (ABAs). The Convention on Biodiversity spirit implies a prior informed consent between the source country and the collector, to establish which resource will be used and for what, and to settle on a fair agreement on benefit sharing. Bioprospecting can become a type of biopiracy when those principles are not respected.

Uniform approval for use of biodiversity as a legal standard has not been achieved, however. At least one legal commentator has argued that biodiversity should not be used as a legal standard, arguing that the multiple layers of scientific uncertainty inherent in the concept of biodiversity will cause administrative waste and increase litigation without promoting preservation goals. See Fred Bosselman, A Dozen Biodiversity Puzzles, 12 N.Y.U. Environmental Law Journal 364 (2004)

Criticisms of the biodiversity paradigm

The 'founder effect'

The field of biodiversity research has often been criticised for being overly defined by the personal interests of the founders (ie. terrestrial mammals) giving a narrow focus, rather than extending to other areas where it could be useful. This is termed the 'founder effect' by Norse and Irish, (1996). France and Rigg reviewed biodiversity research literature in 1998 and found that a there was a significant lack of papers studying marine ecosystems, leading them to dub marine biodiversity research the 'sleeping hydra'.

References:

  • Irish, K.E. and Norse, E.A. (1996) Scant emphasis on marine biodiversity Conserv. Biol. 10 680
  • France, R., and Rigg, C. (1998) Examination of the 'founder effect' in biodiversity research: patterns and imbalances in the published literature Diversity and Distributions 4 77-86

Size bias

Biodiversity researcher Sean Nee, writing in the 24 June 2004 edition of Nature, points out that the vast majority of Earth's biodiversity is microbial, and that contemporary biodiversity science is "firmly fixated on the visible world" (Nee uses "visible" as a synonym for macroscopic). For example, microbial life is very much more metabolically and environmentally diverse than multicellular life (see extremophile).

Quotes from Sean Nee

  • "the contribution of visible life to biodiversity is very small indeed".
  • "On the tree of life, based on analyses of small-subunit ribosomal RNA, visible life consists of barely noticeable twigs. This should not be surprising — invisible life had at least three billion years to diversify and explore evolutionary space before the 'visibles' arrived".

Conferences

COP8 (Eight Meeting of the Conference of the Parties to the Convention on Biological Diversity) 20 - 31 March / Curitiba - Brazil

Notes

  1. Edward O.Wilson, editor, Frances M.Peter, associate editor, Biodiversity, National Academy Press, march 1988 ISBN 0-309037832 ; ISBN 0-309037395 (pbk.), online edition
  2. Global Biodiversity Assessment. UNEP, 1995, Annex 6, Glossary. ISBN 0-521564816, used as source by "Biodiversity", Glossary of terms related to the CBD, Belgian Clearing-House Mechanism, retrieved April 26, 2006.

See also

  • Adaptation
  • Biocomplexity
  • Bioinformatics
  • Ecology
  • Global 200
  • Intermediate Disturbance Hypothesis
  • International Treaty on Plant Genetic Resources for Food and Agriculture
  • Like-Minded Megadiverse Countries (LMMC), a group of 17 megadiverse countries, formed in February 2002
  • List of biodiversity topics
  • List of environment topics
  • Megadiverse countries
  • Millennium Ecosystem Assessment
  • Monoculture
  • Mutation
  • Seed bank
  • United States environmental law
  • Wildlife preserve
  • World Conservation Monitoring Centre

External links

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