More than 99.9% of all species that ever lived on Earth, amounting to over five billion species, are estimated to be
extinct. Estimates on the number of Earth's current
species range from 10 million to 14 million, of which about 1.2 million have been documented and over 86% have not yet been described. The total amount of related
DNAbase pairs on Earth is estimated at 5.0 x 1037 and weighs 50 billion
tonnes. In comparison, the total
mass of the
biosphere has been estimated to be as much as four trillion tons of
carbon. In July 2016, scientists reported identifying a set of 355
genes from the
last universal common ancestor (LUCA) of all
organisms living on Earth.
1916 – The term biological diversity was used first by
J. Arthur Harris in "The Variable Desert," Scientific American: "The bare statement that the region contains a flora rich in genera and species and of diverse geographic origin or affinity is entirely inadequate as a description of its real biological diversity."
Raymond F. Dasmann used the term biological diversity in reference to the richness of living nature that conservationists should protect in his book A Different Kind of Country.
Thomas Lovejoy introduced the term biological diversity to the scientific community in a book. It rapidly became commonly used.
1985 – According to
Edward O. Wilson, the contracted form biodiversity was coined by W. G. Rosen: "The National Forum on BioDiversity ... was conceived by Walter G.Rosen ... Dr. Rosen represented the NRC/NAS throughout the planning stages of the project. Furthermore, he introduced the term biodiversity".
1985 – The term "biodiversity" appears in the article, "A New Plan to Conserve the Earth's Biota" by
1988 – The term biodiversity first appeared in publication.
"Biodiversity" is most commonly used to replace the more clearly-defined and long-established terms,
species diversity and
Biologists most often define biodiversity as the "totality of
ecosystems of a region". An advantage of this definition is that it presents a unified view of the traditional types of biological variety previously identified:
functional diversity (which is a measure of the number of functionally disparate species within a population (e.g. different feeding mechanism, different motility, predator vs prey, etc.)) This multilevel construct is consistent with Datman and Lovejoy.
Other definitions include (in chronological order):
An explicit definition consistent with this interpretation was first given in a paper by Bruce A. Wilcox commissioned by the
International Union for the Conservation of Nature and Natural Resources (IUCN) for the 1982 World National Parks Conference. Wilcox's definition was "Biological diversity is the variety of life forms...at all levels of biological systems (i.e., molecular, organismic, population, species and ecosystem)...".
A publication by Wilcox in 1984: Biodiversity can be defined genetically as the diversity of alleles, genes and
organisms. They study processes such as
gene transfer that drive evolution.
The 1992 United Nations Earth Summit defined "biological diversity" 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 definition is used in the United Nations Convention on Biological Diversity.
Gaston and Spicer's definition in their book "Biodiversity: an introduction" in 2004 is "variation of life at all levels of biological organization".
The Food and Agriculture Organization of the United Nations (FAO) defines biodiversity in 2019 as "the variability that exists among living organisms (both within and between species) and the ecosystems of which they are part."
According to Mora and colleagues' estimation, there are approximately 8.7 million terrestrial species and 2.2 million oceanic species. The authors note that these estimates are strongest for eukaryotic organisms and likely represent the lower bound of prokaryote diversity. Other estimates include:
fungi, estimates based on data from the tropics, long-term non-tropical sites and molecular studies that have revealed
cryptic speciation. Some 0.075 million species of fungi had been documented by 2001;
The number of
microbial species is not reliably known, but the
Global Ocean Sampling Expedition dramatically increased the estimates of genetic diversity by identifying an enormous number of new genes from near-surface
plankton samples at various marine locations, initially over the 2004–2006 period. The findings may eventually cause a significant change in the way science defines
species and other taxonomic categories.
Since the rate of extinction has increased, many extant species may become extinct before they are described. Not surprisingly, in the
animalia the most studied groups are
arthropods are the least studied
During the last century, decreases in biodiversity have been increasingly observed. It was estimated in 2007 that up to 30% of all species will be extinct by 2050. Of these, about one eighth of known plant species are threatened with
extinction. Estimates reach as high as 140,000 species per year (based on
Species-area theory). This figure indicates
unsustainable ecological practices, because few species emerge each year. 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. and expected to still grow in the upcoming years. As of 2012, some studies suggest that 25% of all mammal species could be extinct in 20 years.
In absolute terms, the planet has lost 58% of its biodiversity since 1970 according to a 2016 study by the World Wildlife Fund. The Living Planet Report 2014 claims that "the number of mammals, birds, reptiles, amphibians, and fish across the globe is, on average, about half the size it was 40 years ago". Of that number, 39% accounts for the terrestrial wildlife gone, 39% for the marine wildlife gone and 76% for the freshwater wildlife gone. Biodiversity took the biggest hit in
Latin America, plummeting 83 percent. High-income countries showed a 10% increase in biodiversity, which was canceled out by a loss in low-income countries. This is despite the fact that high-income countries use five times the ecological resources of low-income countries, which was explained as a result of a process whereby wealthy nations are outsourcing
resource depletion to poorer nations, which are suffering the greatest ecosystem losses.
A 2017 study published in PLOS One found that the biomass of insect life in Germany had declined by three-quarters in the last 25 years. Dave Goulson of
Sussex University stated that their study suggested that humans "appear to be making vast tracts of land inhospitable to most forms of life, and are currently on course for ecological Armageddon. If we lose the insects then everything is going to collapse."
In 2020 the
World Wildlife Foundation published a report saying that "biodiversity is being destroyed at a rate unprecedented in human history". The report claims that 68% of the population of the examined species were destroyed in the years 1970 – 2016.
Of 70,000 monitored species, around 48% are experiencing population declines from human activity (in 2023), whereas only 3% have increasing populations.
Loss of biodiversity results in the loss of
natural capital that supplies
ecosystem goods and services. Species today are being wiped out at a rate 100 to 1,000 times higher than baseline, and the rate of extinctions is increasing. This process destroys the resilience and adaptability of life on Earth.
In 2006, many species were formally classified as
threatened; moreover, scientists have estimated that millions more species are at risk which have not been formally recognized. About 40 percent of the 40,177 species assessed using the
IUCN Red List criteria are now listed as threatened with
extinction—a total of 16,119. As of late 2022 9251 species were considered part of the IUCN's
According to the
IUCN the main direct threats to conservation (and thus causes for biodiversity loss) fall in eleven categories: Residential and commercial development; farming activities;
energy production and
mining; transportation and service corridors; biological resource usages; human intrusions and activities that
alter, destroy, disturb habitats and species from exhibiting natural behaviors; natural system modification; invasive and problematic species, pathogens and genes;
pollution; catastrophic geological events, climate change.
Some studies have however pointed out that habitat destruction for the expansion of agriculture and the overexploitation of wildlife are the more significant drivers of contemporary biodiversity loss, not
Terrestrial biodiversity is thought to be up to 25 times greater than ocean biodiversity. Forests harbour most of Earth's terrestrial biodiversity. The conservation of the world's biodiversity is thus utterly dependent on the way in which we interact with and use the world's forests. A new method used in 2011, put the total number of species on Earth at 8.7 million, of which 2.1 million were estimated to live in the ocean. However, this estimate seems to under-represent the diversity of microorganisms. Forests provide habitats for 80 percent of amphibian
species, 75 percent of bird species and 68 percent of mammal species. About 60 percent of all vascular plants are found in tropical forests. Mangroves provide breeding grounds and nurseries for numerous species of fish and shellfish and help trap sediments that might otherwise adversely affect seagrass beds and coral reefs, which are habitats for many more marine species. Forests span around 4 billion acres (nearly a third of the earth's land mass) and are home to approximately 80% of the world's biodiversity. About 1 billion hectares are covered by primary forests. Over 700 million hectares of the world's woods are officially protected.
The biodiversity of forests varies considerably according to factors such as forest type, geography, climate and soils – in addition to human use. Most forest habitats in temperate regions support relatively few animal and plant species and species that tend to have large geographical distributions, while the montane forests of Africa, South America and Southeast Asia and lowland forests of Australia, coastal Brazil, the Caribbean islands, Central America and insular Southeast Asia have many species with small geographical distributions. Areas with dense human populations and intense agricultural land use, such as
Europe, parts of Bangladesh, China, India and North America, are less intact in terms of their biodiversity. Northern Africa, southern Australia, coastal Brazil, Madagascar and South Africa, are also identified as areas with striking losses in biodiversity intactness. European forests in EU and non-EU nations comprise more than 30% of Europe's land mass (around 227 million hectares), representing an almost 10% growth since 1990.
Generally, there is an increase in biodiversity from the
poles to the
tropics. Thus localities at lower
latitudes have more species than localities at higher
latitudes. This is often referred to as the latitudinal gradient in species diversity. Several ecological factors may contribute to the gradient, but the ultimate factor behind many of them is the greater mean temperature at the equator compared to that of the poles.
Even though terrestrial biodiversity declines from the equator to the poles, some studies claim that this characteristic is unverified in
aquatic ecosystems, especially in
marine ecosystems. The latitudinal distribution of parasites does not appear to follow this rule. Also, in terrestrial ecosystems the soil bacterial diversity has been shown to be highest in temperate climatic zones, and has been attributed to carbon inputs and habitat connectivity.
In 2016, an alternative hypothesis ("the
fractal biodiversity") was proposed to explain the biodiversity latitudinal gradient. In this study, the
species pool size and the fractal nature of ecosystems were combined to clarify some general patterns of this gradient. This hypothesis considers
net primary production (NPP) as the main variables of an ecosystem niche and as the axis of the ecological
hypervolume. In this way, it is possible to build fractal hyper volumes, whose
fractal dimension rises to three moving towards the
Atlantic Forest is considered one such hotspot, containing roughly 20,000 plant species, 1,350 vertebrates and millions of insects, about half of which occur nowhere else. The island of
India are also particularly notable.
Colombia is characterized by high biodiversity, with the highest rate of species by area unit worldwide and it has the largest number of endemics (species that are not found naturally anywhere else) of any country. About 10% of the species of the Earth can be found in Colombia, including over 1,900 species of bird, more than in Europe and North America combined, Colombia has 10% of the world's mammals species, 14% of the amphibian species and 18% of the bird species of the world.Madagascar dry deciduous forests and lowland rainforests possess a high ratio of
endemism. Since the island separated from mainland
Africa 66 million years ago, many species and ecosystems have evolved independently.Indonesia's 17,000 islands cover 735,355 square miles (1,904,560 km2) and contain 10% of the world's
flowering plants, 12% of mammals and 17% of
birds—along with nearly 240 million people. Many regions of high biodiversity and/or endemism arise from specialized
habitats which require unusual adaptations, for example,
alpine environments in high
Northern European peat
Accurately measuring differences in biodiversity can be difficult.
Selection bias amongst researchers may contribute to biased empirical research for modern estimates of biodiversity. In 1768, Rev.
Gilbert White succinctly observed of his
Selborne, Hampshire"all nature is so full, that that district produces the most variety which is the most examined."
The biodivertisy of the past is called Paleobiodiversity. The
fossil record suggests that the last few million years featured the greatest biodiversity in
history. However, not all scientists support this view, since there is uncertainty as to how strongly the fossil record is biased by the greater availability and preservation of recent
geologic sections. Some scientists believe that corrected for sampling artifacts, modern biodiversity may not be much different from biodiversity 300 million years ago, whereas others consider the fossil record reasonably reflective of the diversification of life. Estimates of the present global macroscopic species diversity vary from 2 million to 100 million, with a best estimate of somewhere near 9 million, the vast majority
arthropods. Diversity appears to increase continually in the absence of natural selection.
The existence of a global carrying capacity, limiting the amount of life that can live at once, is debated, as is the question of whether such a limit would also cap the number of species. While records of life in the sea show a
logistic pattern of growth, life on land (insects, plants and tetrapods) shows an
exponential rise in diversity. As one author states, "Tetrapods have not yet invaded 64 percent of potentially habitable modes and it could be that without human influence the ecological and
taxonomic diversity of tetrapods would continue to increase exponentially until most or all of the available eco-space is filled."
It also appears that the diversity continues to increase over time, especially after mass extinctions.
On the other hand, changes through the
Phanerozoic correlate much better with the
hyperbolic model (widely used in
macrosociology, as well as
fossil biodiversity) than with exponential and logistic models. The latter models imply that changes in diversity are guided by a first-order
positive feedback (more ancestors, more descendants) and/or a
negative feedback arising from resource limitation. Hyperbolic model implies a second-order positive feedback. Differences in the strength of the second-order feedback due to different intensities of interspecific competition might explain the faster rediversification of
ammonoids in comparison to
bivalves after the
end-Permian extinction. The hyperbolic pattern of the
world population growth arises from a second-order positive feedback between the population size and the rate of technological growth. The hyperbolic character of biodiversity growth can be similarly accounted for by a feedback between diversity and community structure complexity. The similarity between the curves of biodiversity and human population probably comes from the fact that both are derived from the interference of the hyperbolic trend with cyclical and
Most biologists agree however that the period since human emergence is part of a new mass extinction, named the
Holocene extinction event, caused primarily by the impact humans are having on the environment. It has been argued that the present rate of extinction is sufficient to eliminate most species on the planet Earth within 100 years.
New species are regularly discovered (on average between 5–10,000 new species each year, most of them
insects) and many, though discovered, are not yet classified (estimates are that nearly 90% of all
arthropods are not yet classified). Most of the terrestrial diversity is found in
tropical forests and in general, the land has more species than the ocean; some 8.7 million species may exist on Earth, of which some 2.1 million live in the ocean.
From the perspective of the method known as
Natural Economy the economic value of 17 ecosystem services for Earth's
biosphere (calculated in 1997) has an estimated value of US$33 trillion (3.3x1013) per year.
"Ecosystem services are the suite of benefits that ecosystems provide to humanity." The natural species, or biota, are the caretakers of all ecosystems. It is as if the natural world is an enormous bank account of capital assets capable of paying life sustaining dividends indefinitely, but only if the capital is maintained.
These services come in three flavors:
Provisioning services which involve the production of renewable resources (e.g.: food, wood, fresh water)
Regulating services which are those that lessen environmental change (e.g.: climate regulation, pest/disease control)
Cultural services represent human value and enjoyment (e.g.: landscape aesthetics, cultural heritage, outdoor recreation and spiritual significance)
There have been many claims about biodiversity's effect on these ecosystem services, especially provisioning and regulating services. After an exhaustive survey through peer-reviewed literature to evaluate 36 different claims about biodiversity's effect on ecosystem services, 14 of those claims have been validated, 6 demonstrate mixed support or are unsupported, 3 are incorrect and 13 lack enough evidence to draw definitive conclusions.
Greater species diversity
of plants increases fodder yield (synthesis of 271 experimental studies).
of plants (i.e. diversity within a single species) increases overall
crop yield (synthesis of 575 experimental studies). Although another review of 100 experimental studies reports mixed evidence.
of trees increases overall
wood production (Synthesis of 53 experimental studies). However, there is not enough data to draw a conclusion about the effect of tree trait diversity on wood production.
Greater species diversity
of fish increases the stability of
fisheries yield (Synthesis of 8 observational studies)
of natural pest enemies decreases herbivorous pest populations (Data from two separate reviews; Synthesis of 266 experimental and observational studies; Synthesis of 18 observational studies. Although another review of 38 experimental studies found mixed support for this claim, suggesting that in cases where mutual intraguild predation occurs, a single predatory species is often more effective
of plants decreases disease prevalence on plants (Synthesis of 107 experimental studies)
of plants increases resistance to
plant invasion (Data from two separate reviews; Synthesis of 105 experimental studies; Synthesis of 15 experimental studies)
of plants increases
carbon sequestration, but note that this finding only relates to actual uptake of carbon dioxide and not long-term storage, see below; Synthesis of 479 experimental studies)
of plants increases soil organic matter (Synthesis of 85 experimental studies)
Services with mixed evidence
None to date
Greater species diversity of plants may or may not decrease herbivorous pest populations. Data from two separate reviews suggest that greater diversity decreases pest populations (Synthesis of 40 observational studies; Synthesis of 100 experimental studies). One review found mixed evidence (Synthesis of 287 experimental studies), while another found contrary evidence (Synthesis of 100 experimental studies)
Greater species diversity of animals may or may not decrease disease prevalence on those animals (Synthesis of 45 experimental and observational studies), although a 2013 study offers more support showing that biodiversity may in fact enhance disease resistance within animal communities, at least in amphibian frog ponds. Many more studies must be published in support of diversity to sway the balance of evidence will be such that we can draw a general rule on this service.
Greater species and trait diversity of plants may or may not increase long term carbon storage (Synthesis of 33 observational studies)
Greater pollinator diversity may or may not increase pollination (Synthesis of 7 observational studies), but a publication from March 2013 suggests that increased native pollinator diversity enhances pollen deposition (although not necessarily fruit set as the authors would have you believe, for details explore their lengthy supplementary material).
Greater species diversity of plants reduces primary production (Synthesis of 7 experimental studies)
greater genetic and species diversity of a number of organisms reduces freshwater purification (Synthesis of 8 experimental studies, although an attempt by the authors to investigate the effect of detritivore diversity on freshwater purification was unsuccessful due to a lack of available evidence (only 1
observational study was found
Effect of species diversity of plants on biofuel yield (In a survey of the literature, the investigators only found 3 studies)
Effect of species diversity of fish on fishery yield (In a survey of the literature, the investigators only found 4 experimental studies and 1 observational study)
Effect of species diversity on the stability of
biofuel yield (In a survey of the literature, the investigators did not find any studies)
Effect of species diversity of plants on the stability of fodder yield (In a survey of the literature, the investigators only found 2 studies)
Effect of species diversity of plants on the stability of crop yield (In a survey of the literature, the investigators only found 1 study)
genetic diversity of plants on the stability of crop yield (In a survey of the literature, the investigators only found 2 studies)
Effect of diversity on the stability of wood production (In a survey of the literature, the investigators could not find any studies)
Effect of species diversity of multiple taxa on
erosion control (In a survey of the literature, the investigators could not find any studies – they did, however, find studies on the effect of species diversity and root biomass)
Effect of diversity on
flood regulation (In a survey of the literature, the investigators could not find any studies)
Effect of species and trait diversity of plants on
soil moisture (In a survey of the literature, the investigators only found 2 studies)
Other sources have reported somewhat conflicting results and in 1997 Robert Costanza and his colleagues reported the estimated global value of ecosystem services (not captured in traditional markets) at an average of $33 trillion annually.
Stone Age, species loss has accelerated above the average basal rate, driven by human activity. Estimates of species losses are at a rate 100–10,000 times as fast as is typical in the fossil record. Biodiversity also affords many non-material benefits including spiritual and aesthetic values, knowledge systems and education.
Agricultural diversity can be divided into two categories:
intraspecific diversity, which includes the genetic variation within a single species, like the potato (Solanum tuberosum) that is composed of many different forms and types (e.g. in the U.S. they might compare russet potatoes with new potatoes or purple potatoes, all different, but all part of the same species, S. tuberosum).
The other category of agricultural diversity is called
interspecific diversity and refers to the number and types of different species. Thinking about this diversity we might note that many small vegetable farmers grow many different crops like potatoes and also carrots, peppers, lettuce, etc.
Agricultural diversity can also be divided by whether it is 'planned' diversity or 'associated' diversity. This is a functional classification that we impose and not an intrinsic feature of life or diversity. Planned diversity includes the crops which a farmer has encouraged, planted or raised (e.g. crops, covers, symbionts, and livestock, among others), which can be contrasted with the associated diversity that arrives among the crops, uninvited (e.g. herbivores, weed species and pathogens, among others).
Associated biodiversity can be damaging or beneficial. The beneficial associated biodiversity include for instance wild pollinators such as wild bees and
syrphid flies that pollinate crops and natural enemies and antagonists to pests and pathogens. Beneficial associated biodiversity occurs abundantly in crop fields and provide multiple
ecosystem services such as pest control, nutrient cycling and pollination that support crop production.
The control of damaging associated biodiversity is one of the great agricultural challenges that farmers face. On
monoculture farms, the approach is generally to suppress damaging associated diversity using a suite of biologically destructive
pesticides, mechanized tools and
transgenic engineering techniques, then to
rotate crops. Although some
polyculture farmers use the same techniques, they also employ
integrated pest management strategies as well as more labor-intensive strategies, but generally less dependent on capital, biotechnology, and energy.
Interspecific crop diversity is, in part, responsible for offering variety in what we eat. Intraspecific diversity, the variety of alleles within a single species, also offers us a choice in our diets. If a crop fails in a monoculture, we rely on agricultural diversity to replant the land with something new. If a wheat crop is destroyed by a pest we may plant a hardier variety of wheat the next year, relying on intraspecific diversity. We may forgo wheat production in that area and plant a different species altogether, relying on interspecific diversity. Even an agricultural society that primarily grows monocultures relies on biodiversity at some point.
Irish potato blight of 1846 was a major factor in the deaths of one million people and the emigration of about two million. It was the result of planting only two potato varieties, both vulnerable to the blight, Phytophthora infestans, which arrived in 1845
rice grassy stunt virus struck rice fields from Indonesia to India in the 1970s, 6,273 varieties were tested for resistance. Only one was resistant, an Indian variety and known to science only since 1966. This variety formed a hybrid with other varieties and is now widely grown.
Coffee rust attacked coffee plantations in
Brazil and Central America in 1970. A resistant variety was found in Ethiopia. The diseases are themselves a form of biodiversity.
Although about 80 percent of humans' food supply comes from just 20 kinds of plants, humans use at least 40,000 species. Earth's surviving biodiversity provides resources for increasing the range of food and other products suitable for human use, although the present extinction rate shrinks that potential.
Biodiversity's relevance to human health is becoming an international political issue, as scientific evidence builds on the global health implications of biodiversity loss. This issue is closely linked with the issue of
climate change, as many of the anticipated
health risks of climate change are associated with changes in biodiversity (e.g. changes in populations and distribution of disease vectors, scarcity of fresh water, impacts on agricultural biodiversity and food resources etc.). This is because the species most likely to disappear are those that buffer against infectious disease transmission, while surviving species tend to be the ones that increase disease transmission, such as that of West Nile Virus,
Lyme disease and Hantavirus, according to a study done co-authored by Felicia Keesing, an ecologist at Bard College and Drew Harvell, associate director for Environment of the
Atkinson Center for a Sustainable Future (ACSF) at
The growing demand and lack of drinkable water on the planet presents an additional challenge to the future of human health. Partly, the problem lies in the success of water suppliers to increase supplies and failure of groups promoting the preservation of water resources. While the distribution of clean water increases, in some parts of the world it remains unequal. According to the World Health Organisation (2018), only 71% of the global population used a safely managed drinking-water service.
Some of the health issues influenced by biodiversity include dietary health and nutrition security, infectious disease, medical science and medicinal resources, social and psychological health. Biodiversity is also known to have an important role in reducing disaster risk and in post-disaster relief and recovery efforts.
According to the
United Nations Environment Programme a
pathogen, like a
virus, have more chances to meet resistance in a diverse population.Therefore, in a population genetically similar it expands more easily. For example, the
COVID-19 pandemic had less chances to occur in a world with higher biodiversity. A broad literature review published in 2010 by
Nature (journal), Impacts of biodiversity on the emergence and transmission of infectious disease, found this to be broadly true within real environments. Although some small population exceptions were found to exist, on average a collapse in biodiversity significantly increased the spread & spillover of infectious diseases.
Biodiversity provides critical support for drug discovery and the availability of medicinal resources. A significant proportion of drugs are derived, directly or indirectly, from biological sources: at least 50% of the pharmaceutical compounds on the US market are derived from plants, animals and
microorganisms, while about 80% of the world population depends on medicines from nature (used in either modern or traditional medical practice) for primary healthcare. Only a tiny fraction of wild species has been investigated for medical potential. Biodiversity has been critical to advances throughout the field of
bionics. Evidence from market analysis and biodiversity science indicates that the decline in output from the pharmaceutical sector since the mid-1980s can be attributed to a move away from natural product exploration ("bioprospecting") in favour of genomics and synthetic chemistry, indeed claims about the value of undiscovered pharmaceuticals may not provide enough incentive for companies in free markets to search for them because of the high cost of development; meanwhile, natural products have a long history of supporting significant economic and health innovation. Marine ecosystems are particularly important, although inappropriate
bioprospecting can increase biodiversity loss, as well as violating the laws of the communities and states from which the resources are taken.
Business and industry
Many industrial materials derive directly from biological sources. These include building materials, fibers, dyes, rubber, and oil. Biodiversity is also important to the security of resources such as water, timber, paper, fiber, and food. As a result, biodiversity loss is a significant risk factor in business development and a threat to long-term economic sustainability.
Leisure, cultural and aesthetic value
Biodiversity enriches leisure activities such as
birdwatching or natural history study.
Popular activities such as
fishkeeping strongly depend on biodiversity. The number of species involved in such pursuits is in the tens of thousands, though the majority do not enter commerce.[clarification needed]
The relationships between the original natural areas of these often exotic animals and plants and commercial collectors, suppliers, breeders, propagators and those who promote their understanding and enjoyment are complex and poorly understood. The general public responds well to exposure to rare and unusual organisms, reflecting their inherent value.
Philosophically it could be argued that biodiversity has intrinsic aesthetic and spiritual value to
mankindin and of itself. This idea can be used as a counterweight to the notion that
tropical forests and other ecological realms are only worthy of conservation because of the services they provide.
"There is now unequivocal evidence that biodiversity loss reduces the efficiency by which ecological communities capture biologically essential resources, produce biomass, decompose and recycle biologically essential nutrients... There is mounting evidence that biodiversity increases the stability of ecosystem functions through time... Diverse communities are more productive because they contain key species that have a large influence on productivity and differences in functional traits among organisms increase total resource capture... The impacts of diversity loss on ecological processes might be sufficiently large to rival the impacts of many other global drivers of environmental change... Maintaining multiple ecosystem processes at multiple places and times requires higher levels of biodiversity than does a single process at a single place and time."
It plays a part in regulating the chemistry of our
water supply. Biodiversity is directly involved in
water purification, recycling
nutrients and providing fertile soils. Experiments with controlled environments have shown that humans cannot easily build ecosystems to support human needs; for example
insect pollination cannot be mimicked, though there have been attempts to create artificial pollinators using
unmanned aerial vehicles. The economic activity of pollination alone represented between $2.1–14.6 billion in 2003.
A variety of objective means exist to empirically measure biodiversity. Each measure relates to a particular use of the data, and is likely to be associated with the variety of genes. Biodiversity is commonly measured in terms of taxonomic richness of a geographic area over a time interval. In order to calculate biodiversity, species evenness, species richness, and species diversity are to be obtained first. Species evenness is the relative number of individuals of each species in a given area. Species richness is the number of species present in a given area. Species diversity is the relationship between species evenness and species richness. There are many ways to measure biodiversity within a given ecosystem. However, the two most popular are Shannon-Weaver diversity index, commonly referred to as Shannon diversity index, and the other is Simpsons diversity index. Although many scientists prefer to use Shannon's diversity index simply because it takes into account species richness.
This section needs expansion. You can help by
adding to it. (November 2019)
Taxonomic and size relationships
Less than 1% of all species that have been described have been studied beyond noting their existence. The vast majority of Earth's species are microbial. Contemporary biodiversity physics is "firmly fixated on the visible [macroscopic] world". For example, microbial life is
metabolically and environmentally more diverse than multicellular life (see e.g.,
extremophile). "On the tree of life, based on analyses of small-subunit
ribosomal RNA, visible life consists of barely noticeable twigs. The inverse relationship of size and population recurs higher on the evolutionary ladder—to a first approximation, all multicellular species on Earth are insects".Insect extinction rates are high—supporting the Holocene extinction hypothesis.
Barriers such as large
deserts encourage diversity by enabling independent evolution on either side of the barrier, via the process of
allopatric speciation. The term
invasive species is applied to species that breach the natural barriers that would normally keep them constrained. Without barriers, such species occupy new territory, often supplanting native species by occupying their niches, or by using resources that would normally sustain native species.
The number of species invasions has been on the rise at least since the beginning of the 1900s. Species are increasingly being moved by humans (on purpose and accidentally). In some cases the invaders are causing drastic changes and damage to their new habitats (e.g.: zebra mussels and the emerald ash borer in the Great Lakes region and the lion fish along the North American Atlantic coast). Some evidence suggests that invasive species are competitive in their new habitats because they are subject to less pathogen disturbance. Others report confounding evidence that occasionally suggest that species-rich communities harbor many native and exotic species simultaneously while some say that diverse ecosystems are more resilient and resist invasive plants and animals. An important question is, "do invasive species cause extinctions?" Many studies cite effects of invasive species on natives, but not extinctions. Invasive species seem to increase local (i.e.:
alpha diversity) diversity, which decreases turnover of diversity (i.e.:
beta diversity). Overall
gamma diversity may be lowered because species are going extinct because of other causes, but even some of the most insidious invaders (e.g.: Dutch elm disease, emerald ash borer, chestnut blight in North America) have not caused their host species to become extinct.
population decline and
homogenization of regional biodiversity are much more common. Human activities have frequently been the cause of invasive species circumventing their barriers, by introducing them for food and other purposes. Human activities therefore allow species to migrate to new areas (and thus become invasive) occurred on time scales much shorter than historically have been required for a species to extend its range.
Not all introduced species are invasive, nor all invasive species deliberately introduced. In cases such as the
invasion of US waterways was unintentional. In other cases, such as
Hawaii, the introduction is deliberate but ineffective (
nocturnalrats were not vulnerable to the
diurnal mongoose). In other cases, such as
oil palms in Indonesia and Malaysia, the introduction produces substantial economic benefits, but the benefits are accompanied by costly
Finally, an introduced species may unintentionally injure a species that depends on the species it replaces. In
Belgium, Prunus spinosa from Eastern Europe leafs much sooner than its West European counterparts, disrupting the feeding habits of the Thecla betulae butterfly (which feeds on the leaves). Introducing new species often leaves endemic and other local species unable to compete with the exotic species and unable to survive. The exotic organisms may be
parasites, or may outcompete indigenous species for nutrients, water and light.
At present, several countries have already imported so many exotic species, particularly agricultural and ornamental plants, that their indigenous fauna/flora may be outnumbered. For example, the introduction of
kudzu from Southeast Asia to Canada and the United States has threatened biodiversity in certain areas. Nature offers effective ways to help mitigate climate change. Another example may be ignored is the pines, most pines origin in the north hemisphere and the pines were introduced into South hemisphere as the landscape plants.
Hybridization and introgression are side-effects of introduction and invasion. These phenomena can be especially detrimental to
rare species that come into contact with more abundant ones. The abundant species can interbreed with the rare species, swamping its
gene pool. This problem is not always apparent from
morphological (outward appearance) observations alone. Some degree of
gene flow is normal adaptation and not all
genotype constellations can be preserved. However, hybridization with or without introgression may, nevertheless, threaten a rare species' existence.
animal husbandry, the
Green Revolution popularized the use of conventional
hybridization to increase yield. Often hybridized breeds originated in developed countries and were further hybridized with local varieties in the developing world to create high yield strains resistant to local climate and diseases. Local governments and industry have been pushing hybridization. Formerly huge gene pools of various wild and indigenous breeds have collapsed causing widespread
genetic erosion and genetic pollution. This has resulted in the loss of genetic diversity and biodiversity as a whole.
Genetic erosion and genetic pollution have the potential to destroy unique
genotypes, threatening future access to
food security. A decrease in genetic diversity weakens the ability of crops and livestock to be hybridized to resist disease and survive changes in climate.
Conservation biology is reforming around strategic plans to protect biodiversity. Preserving global biodiversity is a priority in strategic conservation plans that are designed to engage public policy and concerns affecting local, regional and global scales of communities, ecosystems and cultures. Action plans identify
ways of sustaining human well-being, employing
market capital and
Removal of exotic species will allow the species that they have negatively impacted to recover their ecological niches. Exotic species that have become pests can be identified taxonomically (e.g., with
Digital Automated Identification SYstem (DAISY), using the
barcode of life). Removal is practical only given large groups of individuals due to the economic cost.
Gene banks are collections of specimens and genetic material. Some banks intend to reintroduce banked species to the ecosystem (e.g., via tree nurseries).
Reduction and better targeting of pesticides allows more species to survive in agricultural and urbanized areas.
Location-specific approaches may be less useful for protecting migratory species. One approach is to create
wildlife corridors that correspond to the animals' movements. National and other boundaries can complicate corridor creation.
Priorities for resource allocation
Focusing on limited areas of higher potential biodiversity promises greater immediate return on investment than spreading resources evenly or focusing on areas of little diversity but greater interest in biodiversity.
A second strategy focuses on areas that retain most of their original diversity, which typically require little or no restoration. These are typically non-urbanized, non-agricultural areas. Tropical areas often fit both criteria, given their natively high diversity and relative lack of development.
Protected areas, including forest reserves and biosphere reserves, serve many functions including for affording protection to wild animals and their habitat. Protected areas have been set up all over the world with the specific aim of protecting and conserving plants and animals. Some scientists have called on the global community to designate as protected areas of 30 percent of the planet by 2030, and 50 percent by 2050, in order to mitigate biodiversity loss from anthropogenic causes. The target of protecting 30% of the area of the planet by the year 2030 (
30 by 30) was adopted by almost 200 countries in the
2022 United Nations Biodiversity Conference. At the moment of adoption (December 2022) 17% of land territory and 10% of ocean territory were protected. In a study published 4 September 2020 in
Science Advances researchers mapped out regions that can help meet critical conservation and climate goals.
Protected areas safeguard nature and cultural resources and contribute to livelihoods, particularly at local level. There are over 238 563 designated protected areas worldwide, equivalent to 14.9 percent of the earth's land surface, varying in their extension, level of protection, and type of management (IUCN, 2018).
Forest protected areas are a subset of all protected areas in which a significant portion of the area is forest. This may be the whole or only a part of the protected area. Globally, 18 percent of the world's forest area, or more than 700 million hectares, fall within legally established protected areas such as national parks, conservation areas and game reserves.
The benefits of protected areas extend beyond their immediate environment and time. In addition to conserving nature, protected areas are crucial for securing the long-term delivery of ecosystem services. They provide numerous benefits including the conservation of
genetic resources for food and agriculture, the provision of medicine and health benefits, the provision of water, recreation and tourism, and for acting as a buffer against disaster. Increasingly, there is acknowledgement of the wider socioeconomic values of these natural ecosystems and of the ecosystem services they can provide.
Forest protected areas in particular play many important roles including as a provider of habitat, shelter, food and genetic materials, and as a buffer against disaster. They deliver stable supplies of many goods and environmental services. The role of protected areas, especially forest protected areas, in mitigating and adapting to climate change has increasingly been recognized over the last few years. Protected areas not only store and sequester carbon (i.e. the global network of protected areas stores at least 15 percent of terrestrial carbon), but also enable species to adapt to changing climate patterns by providing refuges and migration corridors. Protected areas also protect people from sudden climate events and reduce their vulnerability to weather-induced problems such as floods and droughts (UNEP–WCMC, 2016).
National park is a large natural or near natural areas set aside to protect large-scale ecological processes, which also provide a foundation for environmentally and culturally compatible, spiritual, scientific, educational, recreational and visitor opportunities. These areas are selected by governments or private organizations to protect natural biodiversity along with its underlying ecological structure and supporting environmental processes, and to promote education and recreation. The
International Union for Conservation of Nature (IUCN), and its World Commission on Protected Areas (WCPA), has defined "National Park" as its Category II type of protected areas.
National parks are usually owned and managed by national or state governments. In some cases, a limit is placed on the number of visitors permitted to enter certain fragile areas. Designated trails or roads are created. The visitors are allowed to enter only for study, cultural and recreation purposes. Forestry operations, grazing of animals and hunting of animals are regulated and the exploitation of habitat or wildlife is banned.
There is an estimated 726 million ha of forest in protected areas worldwide. Of the six major world regions, South America has the highest share of forests in protected areas, 31 percent.
forests play a vital role in harboring more than 45,000 floral and 81,000 faunal species of which 5150 floral and 1837 faunal species are
endemic. In addition, there are 60,065 different tree species in the world. Plant and animal species confined to a specific geographical area are called endemic species. In forest reserves, rights to activities like hunting and grazing are sometimes given to communities living on the fringes of the forest, who sustain their livelihood partially or wholly from forest resources or products. The unclassed forests cover 6.4 percent of the total forest area and they are marked by the following characteristics:
They are large inaccessible forests.
Many of these are unoccupied.
They are ecologically and economically less important.
Approximately 50 million hectares (or 24%) of European forest land is protected for biodiversity and landscape protection. Forests allocated for soil, water, and other ecosystem services encompass around 72 million hectares (32% of European forest area).
zoological parks or zoos, live animals are kept for public
recreation, education and conservation purposes. Modern zoos offer veterinary facilities, provide opportunities for threatened species to
breed in captivity and usually build environments that simulate the native habitats of the animals in their care. Zoos play a major role in creating
awareness about the need to conserve nature.
botanical gardens, plants are grown and displayed primarily for scientific and educational purposes. They consist of a collection of living plants, grown outdoors or under glass in
greenhouses and conservatories. Also, a botanical garden may include a collection of dried plants or
herbarium and such facilities as lecture rooms, laboratories, libraries, museums and experimental or research plantings.
Citizen science, also known as public participation in scientific research, has been widely used in environmental sciences and is particularly popular in a biodiversity-related context. It has been used to enable scientists to involve the general public in biodiversity research, thereby enabling the scientists to collect data that they would otherwise not have been able to obtain. An online survey of 1,160 CS participants across 63 biodiversity citizen science projects in Europe, Australia and New Zealand reported positive changes in (a) content, process and nature of science knowledge, (b) skills of science inquiry, (c) self-efficacy for science and the environment, (d) interest in science and the environment, (e) motivation for science and the environment and (f) behaviour towards the environment.
Volunteer observers have made significant contributions to on-the-ground knowledge about biodiversity, and recent improvements in technology have helped increase the flow and quality of occurrences from citizen sources. A 2016 study published in Biological Conservation registers the massive contributions that citizen scientists already make to data mediated by the
Global Biodiversity Information Facility (GBIF). Despite some limitations of the dataset-level analysis, it is clear that nearly half of all occurrence records shared through the GBIF network come from datasets with significant volunteer contributions. Recording and sharing observations are enabled by several global-scale platforms, including
Global agreements such as the
Convention on Biological Diversity, give "sovereign national rights over biological resources" (not property). The agreements commit countries to "conserve biodiversity", "develop resources for sustainability" and "share the benefits" resulting from their use. Biodiverse countries that allow
bioprospecting or collection of natural products, expect a share of the benefits rather than allowing the individual or institution that discovers/exploits the resource to capture them privately. Bioprospecting can become a type of
biopiracy when such principles are not respected.
In May 2020, the European Union published its Biodiversity Strategy for 2030. The biodiversity strategy is an essential part of the
climate change mitigation strategy of the European Union. From the 25% of the European budget that will go to fight climate change, large part will go to restore biodiversity and
nature based solutions.
Give €20 billion per year to the issue and make it part of the business practice.
Approximately half of the global
GDP depend on nature. In Europe many parts of the economy that generate trillions of euros per year depend on nature. The benefits of
Natura 2000 alone in Europe are €200 – €300 billion per year.
National level laws
Biodiversity is taken into account in some political and judicial decisions:
The relationship between law and ecosystems is very ancient and has consequences for biodiversity. It is related to private and public property rights. It can define protection for threatened ecosystems, but also some rights and duties (for example,
fishing and hunting rights).
Law regarding species is more recent. It defines species that must be protected because they may be threatened by extinction. The U.S.
Endangered Species Act is an example of an attempt to address the "law and species" issue.
Laws regarding gene pools are only about a century old. Domestication and plant breeding methods are not new, but advances in genetic engineering have led to tighter laws covering distribution of
genetically modified organisms, gene
patents and process patents. Governments struggle to decide whether to focus on for example, genes, genomes, or organisms and species.
Uniform approval for use of biodiversity as a legal standard has not been achieved, however. Bosselman argues that biodiversity should not be used as a legal standard, claiming that the remaining areas of scientific uncertainty cause unacceptable administrative waste and increase litigation without promoting preservation goals.
India passed the
Biological Diversity Act in 2002 for the conservation of biological diversity in India. The Act also provides mechanisms for equitable sharing of benefits from the use of traditional biological resources and knowledge.
Wilcox, Bruce A. 1984. In situ conservation of genetic resources: determinants of minimum area requirements. In National Parks, Conservation and Development, Proceedings of the World Congress on National Parks, J.A. McNeely and K.R. Miller, Smithsonian Institution Press, pp. 18–30.
^Proceedings of the National Academy of Sciences, Census of Marine Life (CoML)
^Hawksworth, D. L. (24 July 2012). "Global species numbers of fungi: are tropical studies and molecular approaches contributing to a more robust estimate?". Biodiversity and Conservation. 21 (9): 2425–2433.
^Finn, Catherine; Grattarola, Florencia; Pincheira-Donoso, Daniel (2023). "More losers than winners: investigating Anthropocene defaunation through the diversity of population trends". Biological Reviews. 98 (5): 1732–1748.
^Stokstad, Erik (6 May 2019).
"Landmark analysis documents the alarming global decline of nature". Science.
doi:10.1126/science.aax9287. For the first time at a global scale, the report has ranked the causes of damage. Topping the list, changes in land use—principally agriculture—that have destroyed habitat. Second, hunting and other kinds of exploitation. These are followed by climate change, pollution, and invasive species, which are being spread by trade and other activities. Climate change will likely overtake the other threats in the next decades, the authors note. Driving these threats are the growing human population, which has doubled since 1970 to 7.6 billion, and consumption. (Per capita of use of materials is up 15% over the past 5 decades.)
^Pimm SL, Jenkins CN, Abell R, Brooks TM, Gittleman JL, Joppa LN, et al. (May 2014). "The biodiversity of species and their rates of extinction, distribution, and protection". Science. 344 (6187): 1246752.
S2CID206552746. The overarching driver of species extinction is human population growth and increasing per capita consumption.
^Hughes, Alice C.; Tougeron, Kévin; Martin, Dominic A.; Menga, Filippo; Rosado, Bruno H. P.; Villasante, Sebastian; Madgulkar, Shweta; Gonçalves, Fernando; Geneletti, Davide; Diele-Viegas, Luisa Maria; Berger, Sebastian; Colla, Sheila R.; de Andrade Kamimura, Vitor; Caggiano, Holly; Melo, Felipe (1 January 2023).
"Smaller human populations are neither a necessary nor sufficient condition for biodiversity conservation". Biological Conservation. 277: 109841.
ISSN0006-3207. Through examining the drivers of biodiversity loss in highly biodiverse countries, we show that it is not population driving the loss of habitats, but rather the growth of commodities for export, particularly soybean and oil-palm, primarily for livestock feed or biofuel consumption in higher income economies.
^Schopf, J. William; Kudryavtsev, Anatoliy B.; Czaja, Andrew D.; Tripathi, Abhishek B. (5 October 2007). "Evidence of Archean life: Stromatolites and microfossils". Precambrian Research. Earliest Evidence of Life on Earth. 158 (3–4): 141–155.
abHautmann, Michael; Bagherpour, Borhan; Brosse, Morgane; Frisk, Åsa; Hofmann, Richard; Baud, Aymon; Nützel, Alexander; Goudemand, Nicolas; Bucher, Hugo; Brayard, Arnaud (2015). "Competition in slow motion: the unusual case of benthic marine communities in the wake of the end-Permian mass extinction". Palaeontology. 58 (5): 871–901.
^Kiaer, Lars P.; Skovgaard, M.; Østergård, Hanne (1 December 2009). "Grain yield increase in cereal variety mixtures: A meta-analysis of field trials". Field Crops Research. 114 (3): 361–373.
^Philpott, Stacy M.; Soong, Oliver; Lowenstein, Jacob H.; Pulido, Astrid Luz; Lopez, Diego Tobar (1 October 2009). Flynn, Dan F. B.; DeClerck, Fabrice. "Functional richness and ecosystem services: bird predation on arthropods in tropical agroecosystems". Ecological Applications. 19 (7): 1858–1867.
^Vance-Chalcraft, Heather D.; et al. (1 November 2007). "The Influence of Intraguild Predation on Prey Suppression and Prey Release: A Meta-analysis". Ecology. 88 (11): 2689–2696.
^Hawkins E.S., Reich; Reich, MR (1992). "Japanese-originated pharmaceutical products in the United States from 1960 to 1989: an assessment of innovation". Clin Pharmacol Ther. 51 (1): 1–11.
^Sax, Dov F.; Gaines, Steven D.; Brown, James H. (1 December 2002). "Species Invasions Exceed Extinctions on Islands Worldwide: A Comparative Study of Plants and Birds". The American Naturalist. 160 (6): 766–783.
^Jude, David (1995). Munawar, M. (ed.). The lake Huron ecosystem: ecology, fisheries and management. Amsterdam: S.P.B. Academic Publishing.
^Beech, E.; Rivers, M.; Oldfield, S.; Smith, P. P. (4 July 2017). "GlobalTreeSearch: The first complete global database of tree species and country distributions". Journal of Sustainable Forestry. 36 (5): 454–489.
^Shiva, Vandana (January 2007). "Bioprospecting as Sophisticated Biopiracy". Signs: Journal of Women in Culture and Society. 32 (2): 307–313.
^Einhorn, Catrin (19 December 2022).
"Nearly Every Country Signs On to a Sweeping Deal to Protect Nature". The New York Times. Retrieved 27 December 2022. The United States is just one of two countries in the world that are not party to the Convention on Biological Diversity, largely because Republicans, who are typically opposed to joining treaties, have blocked United States membership. That means the American delegation was required to participate from the sidelines. (The only other country that has not joined the treaty is the Holy See.)