2018年9月30日星期日

Biosphere

The biosphere, also known as the ecosphere, is the worldwide sum of all ecosystems. It can also be termed the zone of life on Earth, a closed system (apart from solar and cosmic radiation and heat from the interior of the Earth), and largely self-regulating. By the most general biophysiological definition, the biosphere is the global ecological system integrating all living beings and their relationships, including their interaction with the elements of the lithosphere, geosphere, hydrosphere, and atmosphere. The biosphere is postulated to have evolved, beginning with a process of biopoiesis (life created naturally from non-living matter, such as simple organic compounds) or biogenesis (life created from living matter), at least some 3.5 billion years ago.

In a general sense, biospheres are any closed, self-regulating systems containing ecosystems. This includes artificial biospheres such as Biosphere 2 and BIOS-3, and potentially ones on other planets or moons.

Origin and use of the term
The term "biosphere" was coined by geologist Eduard Suess in 1875, which he defined as the place on Earth's surface where life dwells.

While the concept has a geological origin, it is an indication of the effect of both Charles Darwin and Matthew F. Maury on the Earth sciences. The biosphere's ecological context comes from the 1920s (see Vladimir I. Vernadsky), preceding the 1935 introduction of the term "ecosystem" by Sir Arthur Tansley (see ecology history). Vernadsky defined ecology as the science of the biosphere. It is an interdisciplinary concept for integrating astronomy, geophysics, meteorology, biogeography, evolution, geology, geochemistry, hydrology and, generally speaking, all life and Earth sciences.

Narrow definition
Geochemists define the biosphere as being the total sum of living organisms (the "biomass" or "biota" as referred to by biologists and ecologists). In this sense, the biosphere is but one of four separate components of the geochemical model, the other three being geosphere, hydrosphere, and atmosphere. When these four component spheres are combined into one system, it is known as the Ecosphere. This term was coined during the 1960s and encompasses both biological and physical components of the planet.

The Second International Conference on Closed Life Systems defined biospherics as the science and technology of analogs and models of Earth's biosphere; i.e., artificial Earth-like biospheres. Others may include the creation of artificial non-Earth biospheres—for example, human-centered biospheres or a native Martian biosphere—as part of the topic of biospherics.

Earth's biosphere

Age
The earliest evidence for life on Earth includes biogenic graphite found in 3.7 billion-year-old metasedimentary rocks from Western Greenland and microbial mat fossils found in 3.48 billion-year-old sandstone from Western Australia. More recently, in 2015, "remains of biotic life" were found in 4.1 billion-year-old rocks in Western Australia. In 2017, putative fossilized microorganisms (or microfossils) were announced to have been discovered in hydrothermal vent precipitates in the Nuvvuagittuq Belt of Quebec, Canada that were as old as 4.28 billion years, the oldest record of life on earth, suggesting "an almost instantaneous emergence of life" after ocean formation 4.4 billion years ago, and not long after the formation of the Earth 4.54 billion years ago. According to biologist Stephen Blair Hedges, "If life arose relatively quickly on Earth... then it could be common in the universe."

Extent
Every part of the planet, from the polar ice caps to the equator, features life of some kind. Recent advances in microbiology have demonstrated that microbes live deep beneath the Earth's terrestrial surface, and that the total mass of microbial life in so-called "uninhabitable zones" may, in biomass, exceed all animal and plant life on the surface. The actual thickness of the biosphere on earth is difficult to measure. Birds typically fly at altitudes as high as 1,800 m (5,900 ft; 1.1 mi) and fish live as much as 8,372 m (27,467 ft; 5.202 mi) underwater in the Puerto Rico Trench.

There are more extreme examples for life on the planet: Rüppell's vulture has been found at altitudes of 11,300 m (37,100 ft; 7.0 mi); bar-headed geese migrate at altitudes of at least 8,300 m (27,200 ft; 5.2 mi); yaks live at elevations as high as 5,400 m (17,700 ft; 3.4 mi) above sea level; mountain goats live up to 3,050 m (10,010 ft; 1.90 mi). Herbivorous animals at these elevations depend on lichens, grasses, and herbs.

Life forms live in every part of the Earth's biosphere, including soil, hot springs, inside rocks at least 19 km (12 mi) deep underground, the deepest parts of the ocean, and at least 64 km (40 mi) high in the atmosphere. Microorganisms, under certain test conditions, have been observed to survive the vacuum of outer space. The total amount of soil and subsurface bacterial carbon is estimated as 5 × 1017 g, or the "weight of the United Kingdom". The mass of prokaryote microorganisms—which includes bacteria and archaea, but not the nucleated eukaryote microorganisms—may be as much as 0.8 trillion tons of carbon (of the total biosphere mass, estimated at between 1 and 4 trillion tons). Barophilic marine microbes have been found at more than a depth of 10,000 m (33,000 ft; 6.2 mi) in the Mariana Trench, the deepest spot in the Earth's oceans. In fact, single-celled life forms have been found in the deepest part of the Mariana Trench, by the Challenger Deep, at depths of 11,034 m (36,201 ft; 6.856 mi). Other researchers reported related studies that microorganisms thrive inside rocks up to 580 m (1,900 ft; 0.36 mi) below the sea floor under 2,590 m (8,500 ft; 1.61 mi) of ocean off the coast of the northwestern United States, as well as 2,400 m (7,900 ft; 1.5 mi) beneath the seabed off Japan. Culturable thermophilic microbes have been extracted from cores drilled more than 5,000 m (16,000 ft; 3.1 mi) into the Earth's crust in Sweden, from rocks between 65–75 °C (149–167 °F). Temperature increases with increasing depth into the Earth's crust. The rate at which the temperature increases depends on many factors, including type of crust (continental vs. oceanic), rock type, geographic location, etc. The greatest known temperature at which microbial life can exist is 122 °C (252 °F) (Methanopyrus kandleri Strain 116), and it is likely that the limit of life in the "deep biosphere" is defined by temperature rather than absolute depth. On 20 August 2014, scientists confirmed the existence of microorganisms living 800 m (2,600 ft; 0.50 mi) below the ice of Antarctica. According to one researcher, "You can find microbes everywhere — they're extremely adaptable to conditions, and survive wherever they are."

Our biosphere is divided into a number of biomes, inhabited by fairly similar flora and fauna. On land, biomes are separated primarily by latitude. Terrestrial biomes lying within the Arctic and Antarctic Circles are relatively barren of plant and animal life, while most of the more populous biomes lie near the equator.

Distribution of life
It constitutes a thin layer of irregular dimensions, just as the density of biomass, diversity and primary production is irregular. It spans the surface and the bottom of the oceans and seas, where it first developed, by the surface of the continents, and on the surface levels of the earth's crust, where life thrives, with low density, between pores and interstices of the rocks.

Oceans
In the oceans the life is concentrated in the surface layer, photic zone, into which the light. The trophic chain starts here with photosynthesizers that are mostly cyanobacteria and protists, usually unicellular and planktonic. The limiting factors for the development of life are here some essential nutrients, such as iron, which are scarce, and maximum productivitywe find it in the cold seas and in certain tropical regions, contiguous to the continents, in which the currents bring out nutrients from the bottom of the sea. Outside those places, the pelagic (offshore) regions of the warm latitudes are biological deserts, with low density of life. The richest and most complex marine ecosystems are, however, tropical, and they are those that develop at a very shallow depth, only a few meters, rich in benthic life, near the shore; The clearest example is the coral reefs.

In addition to the photic zone, there is a thriving marine life in each of the dark and extensive ocean bottoms, which depends, for its nutrition, on the organic matter that falls from above, in the form of waste and corpses. In some places where the geotectonic processes bring out hot waters laden with salts, the primary, autotrophic producers, who obtain the energy of chemical reactions based on inorganic substrates, are important; the type of matabolism that we call chemosynthesis.

Against certain prejudices, the average density of life is greater in the continents than in the oceans in the current biosphere; although as the ocean is much more extensive, corresponds approximately 50% of the total primary production of the planet.

Continents
In the continents the trophic chain starts from the terrestrial plants, photosynthesizers that obtain mineral nutrients from the soil thanks to the same structures with which they are anchored, the roots, making water circulate towards the foliage, where they evaporate it. For this reason the main limiting factor in the continents is the availability of water in the soil, at the same time as the temperature, which is more variable than in the seas, where the high specific heat of the water ensures a very homogeneous thermal environment and stable in time.

For the indicated reason, biomass, gross productivity and ecological diversity, is distributed:

Following a gradient, with a maximum towards the equator and a minimum in the polar regions, in correlation with the available energy.
Concentrated in three latitudinally extended bands. The first one is the equatorial one, where the rains produced by the intertropical front, which are of the zenith type, occur all year round or alternate with a dry season. The other two, more or less symmetrical, cover the middle or temperate latitudes, where there is a greater or lesser abundance of cyclonal rains, which accompany the storms.

Among these humid areas and dense life, there are two symmetrical bands of tropical desert or semi-desert regions, where although biomass is low, biodiversity is high. In the high latitudes of both hemispheres we have, finally, the polar regions, where the poverty of life is explained by the shortage of liquid water as well as the lack of energy.

Deep biosphere
Until recently the level was set as limit for life, a few meters deep, to where the roots of the plants extend. Now we have verified that not only in the oceanic bottoms there are ecosystems dependent on chemoautotrophic organisms, but that life of this type extends to deep levels of the crust. It consists of bacteria and extremophile archaea, which extract energy from inorganic chemical processes (chemosynthesis). They thrive no doubt better in places where certain unstable mineral mixtures appear, which offer a potential for chemical energy; but the Earth is geologically a still alive planet, where the internal processes still generate constantly situations of that type.

Extension
The sheath-like biosphere begins about 60 km above the Earth's surface and ends about 5 km below the Earth's surface. It begins in the lower hemisphere of the mesosphere, pervades the remaining layers of the Earth's atmosphere and the upper parts of the hydrosphere, penetrates the pedosphere and ends in the upper part of the lithosphere, after a few kilometers in the Earth's crust. At least when attention is paid to microorganisms, the biosphere extends over the entire surface of the earth, the oceans and seabeds.

Vertical extension
According to current knowledge, the upper limit of the terrestrial biosphere is slightly above the stratopause, in the lowest mesosphere at 60 km altitude. There are still certain microorganisms in permanent stages before.  At these atmospheric altitudes they defy the low temperatures ranging from about -50 ° C (lower stratosphere) to about 0 ° C (lower mesosphere), as well as the almost complete lack of water and the strong ultraviolet radiation, At present, it is assumed that the microorganisms found do not go through their entire life cycle so far from the earth's surface. Instead, they should only be swirled up the Earth's surface in various ways and then remain in the stratosphere and lowest mesosphere for some time.

Below the stratosphere is the troposphere, the densest and lowest Earth's atmosphere layer. Here the air has higher air temperatures thanks to the natural greenhouse effect and is relatively low in radiation due to the stratospheric ozone layer above. For these reasons, there are the habitats of terrestrial creatures in the troposphere, temperature-induced mostly even just below the nival altitudinal zone.

Below the troposphere, on the one hand, the bottoms of the pedosphere and, on the other hand, the waters of the hydrosphere follow. The soils are inhabited by a variety of soil organisms. Their habitat is limited to the bottom by the supply of soil water and soil air, with microorganisms penetrate the deepest. Intact, but frozen microorganisms find themselves still deep in the permafrost.  In the waters life forms exist to the bottom and once more many meters into the muddy body of water. In fact, a larger proportion of theEarth's total biomass in the form of archaea and bacteria in ocean sediments. But the more prominent members of the aquatic life keep in the top and light-filled water layers of epipelagial on. Beyond that, species and individuals densities can become very small. This is especially true for the deep sea. However, their cold darkness is interrupted by volcanic islands and atolls, which rise above the water surface. Submarine, Guyots and Seamounts provide habitats to many organisms, some of these undersea mountains can rise to the epipelagial. Seen worldwide, seamounts occur very frequently and occupy an area the size of Europe. Collectively, they are likely to be one of the major major biomes. Depending on the depth of the water, volcanic islands, atolls, seamounts and guyots can find diverse communities that interrupt the desert life of the deep sea in this way.

Below the soils and muddy watercourses, the rocks of the lithosphere join. Here caves were found to contain simple cave ecosystems consisting of microorganisms and some multicellular organisms.  All other communities of the lithosphere consist exclusively of microorganisms. Some live in oil deposits,   coal seams, gas hydrates, in deep aquifers, or in fine pores directly in the bedrock. Furthermore, at least certain microbial long-term stages also occur in salt domes. It can be assumed that the biosphere in the lithosphere pulls down to the depth from which the ambient temperature rises geothermally above 150 ° C. At this temperature, it should become too hot even for hyperthermophilic microbes.  As a rule of thumb, it is assumed that the ambient temperature increases by 3 ° C per 100 meters of depth. Thus, the biosphere would have to end in about 5 km lithosphere depth. However, there are strong regional deviations from this rule of thumb.

Microbial ecosystems can also be found in sub-glacial lakes, which are completely isolated from the environment by the overlapping glacial ice. Microorganisms are also found deep in the glacier ice itself. It remains unclear to what extent they only survive or show active life processes there.

Horizontal extension
The living things do not distribute themselves evenly over the biosphere. First, there are biomes with large species and individuals densities. These include, for example, the tropical rainforests and coral reefs. On the other hand, there are also areas with very sparse macroscopic and limited microscopic life. These include cold deserts and dry deserts in the countryside and seabeds in the oceans of the lightless and cold deep seas (Bathyal, Abyssal, Hadal). However, within the desert areas scattered inland areas of higher biodiversity: water oases in the dry deserts, post-volcanic phenomena (Thermal springs, solfatars, fumaroles, mofettes) in the cold deserts, as well as hydrothermal sources (Black Smokers, White Smokers),, and methane sources (Cold Seeps), on deep seabeds,

Construction
Only a thin shell of the earth is space with life. Measured by the total earth volume, the biosphere has only a tiny volume. For earthly organisms have certain claims to their abiotic environment. Most parts of the world can not meet the demands.

The claims of the living beings begin with the space requirement. They can only stay in places that provide enough space for their body sizes. If enough space is available, the place must also offer suitable possibilities of staying in the room. Which options are suitable differs from life form to life form. For example, trees need enough rooting space and tang attachment sites on the seabed, while phytoplankton already get along with the free body of water. The whereabouts claims can change seasonally and age-dependently.

Example: Adult King Albatrosses need some space for their three-meter-wide wings. They roam the low air layers over the open ocean. There they mainly catch octopuses, drink seawater, sleep in the air or float on the sea surface. Adult king algae broods do not need any solid settlement opportunity. However, that changes seasonally. Because they fly to the mainland every two years. There they brag, occupy a breeding ground, incubate her an egg for 79 days and protect the very defenseless young birds in the first five weeks of life. Afterwards, the parents fly out to the sea again. However, they return at irregular intervals to the breeding site to feed the young birds. The young birds must persevere on land,

Furthermore, the abiotic eco-factors (physio-system, location) must move into bandwidths that are tolerable on earthly life forms. This applies in an outstanding way to the offers of thermal energy and liquid water and downstream of the other abiotic eco-factors. In addition, the whereabouts must also ensure the nutrition of the living beings. Autotrophic organisms must have sufficient nutrients and heterotrophic organisms sufficient nutrients.

In the course of Earth's history, the life forms have evolved very different body sizes, settlement methods, Physiosystemansprüche and diets. Now, the same conditions do not prevail everywhere within the biosphere. Therefore no living thing occurs in all places of the biosphere. Life forms with similar or complementary adaptations are found together in the same location. Together they form ecoregions (Eu-biome) and ecozones (zonobioms).

The location of the ecological zones of the mainland depends on the climate.  The climate depends on the degree of latitude (→ lighting zones), the distance to the sea (→ oceanicity / continentality) and possibly of high mountains that prevent precipitation (→ climate glacier). Overall, the ecozones run approximately broad circle parallel.

The location of the ecozones of the oceans (realms) depends on the near-surface water temperature. It should also be borne in mind that, for many marine organisms, the continental shores or sheer vastness of the oceans are barriers that restrict their spread. A total of twelve marine eco-zones are distinguished worldwide. Within a marine ecology, desert-like ecoregions are next to ecoregions of great organismic abundance. This is because the same trophic conditions do not prevail everywhere in the oceans: phytoplankton can only thrive extensively in sections of the sea with a rich supply of building materials. The phytoplankton is at the base of the marine food webs, Consequently, there are also the other marine life forms especially numerous. Sea areas with high concentrations of building materials are areas of upwelling in which building-rich deep water rises to the surface of the water. Large amounts of runot can produce a similar effect (whale pump).

Organismic structure
The size of the biosphere is determined primarily by microorganisms. At the outer borders of the biosphere, only permanent stages of microbes are found, which are immune to inhospitable conditions. This applies to the mesosphere and stratosphere as well as to permafrost soils,  salt domes and deep glacial ice. But even within the biosphere boundaries many ecosystems can be found that consist exclusively of microorganisms. This applies to all communities within the lithosphere, ie for deposits of crude oil, coal and gas hydrate as well as for deep aquifers, deeper sediments of the ocean and for ecosystems in simple solid rock. In addition, the microorganisms occupy all rooms that are alsoinhabitedby multicellular organisms. They even live on and in these metabionts, on skin  and rhizosphere as well as on leaves and in digestive tracts.  The terrestrial biosphere proves to be a sphere of microorganisms everywhere, especially in its more extreme areas. In comparison, the habitat of metabionts appears very limited.

Trophic construction
Strictly speaking, the biosphere consists of many ecosystems that are more or less closely interlinked. In every ecosystem, living things fulfill one of three different trophic functions: Primary producers - also called autotrophs - build up biomass from low-energy building materials. This biomass is then consumed by consumers. During production and consumption, large quantities of waste material are collected. The inventory waste is from organisms of the third trophic function, the Destruenten, mined down to the low-energy building materials. The building materials can then be used again by the primary producers to build new biomass.

The existence of consumers and destructors depends on the presence of primary producers. Complete ecosystems can only be developed in places where primary producers find suitable living conditions. This ultimately applies to the entire biosphere. The extent and existence of the entire biosphere is spatiotemporal depending on the presence of primary producers.

The most striking and important primary producers of the terrestrial biosphere are the photoautotrophic organisms. They operate photosynthesis in order to produce their biomass from low-energy building materials with the help of light. Among the best known photoautotrophic organisms are land plants and algae (→ phototrophic organisms), where more than 99% of the total plant biomass is produced by land plants. The photoautotrophic primary production of the oceans is mainly done by non-calcifying haptophytes and cyanobacteria.

Photoautotrophic organisms are at the base of many terrestrial ecosystems. The biosphere shows its most species- and individual-rich ecosystems in locations where plants or other photoautotrophic life forms can exist. In the countryside in places where daylight comes in, but outside the cold deserts, outside the dry deserts and below the nivalen altitude level. In the water in the euphotic zone of the epipelagial.

Beyond the areas of daylight, long-term relationships can only be established if their phototrophic primary producers are satisfied with only scant volcanic activity - or if they become completely independent of photoautotrophically generated biomass. At the basis of such completely light-independent ecosystems are then chemoautotrophicPrimary producers. Chemoautotrophic organisms also grow their biomass from low-energy building materials. They gain the necessary energy not from light, but from certain chemical reactions. The ecosystems that rely on primary chemoautotrophic producers include hydrothermal (black smokers, white smokers), cold seeps, sub-glacial lakes, caves completely isolated from the outside world, and various microbial ecosystems deep in the bedrock (→ Endolites).

However, the biosphere also includes spaces that are not directly associated with the photoautotrophic or chemoautotrophic ecosystems. Instead, they lie between and outside of them. Due to unfavorable living conditions, the rooms can not be colonized by primary producers. However, these inhospitable areas can be temporarily taken over by consumers, who then return to autotrophically maintained ecosystems.

Example: Many migratory birds pass through their habitats with extremely sparse autotrophic life on their annual migrations. So white storks fly through the dry desert Sahara. Striped geese cross the vegetation-free main ridge of the Himalayas. However, both bird species choose their winter and breeding areas again in habitats inhabited by plants. So they only stay temporarily outside photoautotrophically maintained ecosystems.

The vertical migration is similar to annual bird migration: depending on the time of day, many aquatic organisms migrate back and forth between the epipelagial and the low-lying layers of water below. Some members of the phytoplankton migrate down at night to acquire building materials in the deeper water layers. At daybreak, they return to the water surface.  At the same time there is an opposite movement of zooplankton and some larger animals. They swim in the shelter of darkness to the surface of the water to make prey, and return at dawn to the depth to be safe even from larger predators.

In addition, waste from the autotrophically maintained ecosystems is constantly flowing away. The waste can be recycled by destructors beyond the actual limits of those ecosystems. In this way, ecosystems can emerge - and thus expand the biosphere - which are not based directly on present primary producers, but on waste waste. Typical examples of such ecosystems are the soils, which are subject to a constant diversity of terrestrial living stock. But also water bodies and deeper water layers below the euphotic zone belong to it, to which inventory waste trickles down from the Epipelagial and from the banks. Particularly worth mentioning are the whale falls: Dead whales sink to the bottom of the sea and deliver large amounts of usable waste for deep-sea dwellers.  The walkadavers also serve as intermediate stations for deep-sea organisms on their migrations between the chemoautotroph-based ecosystems of the widely spread hydrothermal (smokers) and methane sources (cold seeps). The reduction of marine waste in the sea occurs at lower rates even in the oxygen-depleted zones (oxygen minimum zone s) by appropriately adapted organisms. In addition to soils and far-off water bodies, many caves are among the waste-based ecosystems, as far as they are not completely isolated from the outside world. In the caves inventory waste is entered in many ways, a prominent example is bat guano.

Artificial biospheres
Experimental biospheres, also called closed ecological systems, have been created to study ecosystems and the potential for supporting life outside the earth. These include spacecraft and the following terrestrial laboratories:

Biosphere 2 in Arizona, United States, 3.15 acres (13,000 m2).
BIOS-1, BIOS-2 and BIOS-3 at the Institute of Biophysics in Krasnoyarsk, Siberia, in what was then the Soviet Union.
Biosphere J (CEEF, Closed Ecology Experiment Facilities), an experiment in Japan.
Micro-Ecological Life Support System Alternative (MELiSSA) at Universitat Autònoma de Barcelona

Extraterrestrial biospheres
No biospheres have been detected beyond the Earth; therefore, the existence of extraterrestrial biospheres remains hypothetical. The rare Earth hypothesis suggests they should be very rare, save ones composed of microbial life only. On the other hand, Earth analogs may be quite numerous, at least in the Milky Way galaxy, given the large number of planets. Three of the planets discovered orbiting TRAPPIST-1 could possibly contain biospheres. Given limited understanding of abiogenesis, it is currently unknown what percentage of these planets actually develop biospheres.

Based on observations by the Kepler Space Telescope team, it has been calculated that provided the probability of abiogenesis is higher than 1 to 1000, the closest alien biosphere should be within 100 light-years from the Earth.

It is also possible that artificial biospheres will be created during the future, for example on Mars. The process of creating an uncontained system that mimics the function of Earth's biosphere is called terraforming.

Source from Wikipedia

Biosecurity

Biosecurity has multiple meanings and is defined differently according to various disciplines. The original definition of biosecurity started out as a set of preventive measures designed to reduce the risk of transmission of infectious diseases in crops and livestock, quarantined pests, invasive alien species, and living modified organisms (Koblentz, 2010). The emerging nature of biosecurity threats means that small scale risks blow up rapidly, thus an effective policy becomes a challenge for there are limitations on time and resources available for analysing threats and estimating the likelihood of their occurrence.

The term was first used by the agricultural and environmental communities. Starting from the late 1990s in response to the threat of biological terrorism, biosecurity encompasses the prevention of the intentional removal (theft) of biological materials from research laboratories. These preventative measures are a combination of systems and practices put into its place at bioscience laboratories to prevent the use of dangerous pathogens and toxins for malicious use, as well as by customs agents and agricultural and natural resource managers to prevent the spread of these biological agents.

Advances in technology have meant that many civilian research projects in medicine have the potential to be used in military applications (dual-use research) and biosecurity protocols are used to prevent dangerous biological materials from falling into the hands of malevolent parties. The National Academy of Sciences define biosecurity as "security against the inadvertent, inappropriate, or intentional malicious or malevolent use of potentially dangerous biological agents or biotechnology, including the development, production, stockpiling, or use of biological weapons as well as outbreaks of newly emergent and epidemic disease". Biosecurity requires the cooperation of scientists, technicians, policy makers, security engineers, and law enforcement officials.

As international security issue
Controversial experiments in synthetic biology, including the synthesis of poliovirus from its genetic sequence, and the modification of H5N1 for airborne transmission in mammals, have led to calls for tighter controls on the materials and information used to perform similar feats. Ideas include better enforcement by national governments and private entities concerning shipments and downloads of such materials, and registration or background check requirements for anyone handling such materials.

Initially, health security or biosecurity issues have not been considered as an international security issue especially in the traditional view of international relations. However, some changes in trend have contributed to inclusion of biosecurity (health security) in discussions of security (Koblentz, 2010).

As time progressed, there was a movement towards securitization. Non-traditional security issues such as climate change, organized crime, terrorism, and landmines came to be included in the definition of international security (Koblentz, 2010). There was a general realization that the actors in the international system not only involved nation-states but also included international organizations, institutions, and individuals (Koblentz, 2010). Therefore, ensuring the security of various actors within each nation became an important agenda. Biosecurity is one of the issues to be securitized under this trend. In fact, on January 10, 2000, the UN Security Council convened to discuss HIV/AIDS as a security issue in Africa and designated it a threat in the following month. The UNDP Millennium Development Goals also recognize health issues as international security issue (Koblentz, 2010). Several instances of epidemics that followed such as SARS increased awareness of health security (biosecurity). Recently several factors have rendered biosecurity issues more severe. There is a continuing advancement of biotechnology which increases the possibility for malevolent use, evolution of infectious diseases, and globalizing force which is making the world more interdependent and more susceptible to spread of epidemics (Koblentz, 2010).

Some uncertainties about the policy implementation for biosecurity remain for future. In order to carefully plan out preventative policies, policy makers need to be able to somewhat predict the probability and assess the risks; however, as the uncertain nature of the biosecurity issue goes it is largely difficult to predict and also involves a complex process as it requires a multidisciplinary approach(Koblentz, 2010). The policy choices they make to address an immediate threat could pose another threat in the future, facing an unintended trade-off. Policy makers are also constantly looking for a more effective way to coordinate international actors- governmental organizations and NGOs- and actors from different nations so that they could tackle the problem of resource overlap (Koblentz, 2010).

Laboratory program
Components of a laboratory biosecurity program include:

Physical security
Personnel security
Material control & accountability
Transport security
Information security
Program management

Animal
Animal biosecurity is the product of all actions undertaken by an entity to prevent introduction of disease agents into a specific area. Animal biosecurity differs from biosecurity which are measures taken to reduce the risk of infectious agent theft and dispersal by means of bioterrorism. Animal biosecurity is a comprehensive approach, encompassing different means of prevention and containment. A critical element in animal biosecurity, biocontainment, is the control of disease agents already present in a particular area, and works to prevent novel transmissions. Animal biosecurity may protect organisms from infectious agents or noninfectious agents such as toxins or pollutants, and can be executed in areas as large as a nation or as small as a local farm.

Animal biosecurity takes into account the epidemiological triad for disease occurrence: the individual host, the disease, and the environment in contributing to disease susceptibility. It aims to improve nonspecific immunity of the host to resist the introduction of an agent, or limit the risk that an agent will be sustained in an environment at adequate levels. Biocontainment, an element of animal biosecurity, works to improve specific immunity towards already present pathogens.

Biosecurity means the prevention of the illicit use of pathogenic bioorganisms by laboratory staff or others. Biosafety means the protection of laboratory staff from being infected by pathogenic bioorganisms.

Medical countermeasures
Medical countermeasures ("MCMs") are products such as biologics and pharmaceutical drugs that can protect from or treat the effects of a chemical, biological, radiological, or nuclear ("CBRN") attack. MCMs can also be used for prevention and diagnosis of symptoms associated with CBRN attacks or threats.

The FDA runs a program called the FDA Medical Countermeasures Initiative ("MCMi"). The program helps support "partner" agencies and organizations prepare for public health emergencies that could require MCMs.

The federal government provides funding for MCM-related programs. In June 2016, a Senate Appropriations subcommittee approved a bill that would continue funding four specific medical countermeasure programs:

$512 million for the Biomedical Advanced Research and Development Authority (BARDA)
$510 million for BioShield Special Reserve Fund (SRF)
$575 million for the Strategic National Stockpile (SNS)
$72 million for pandemic influenza

Challenges
The destruction of the World Trade Center in Manhattan on September 11, 2001 by terrorists and subsequent wave of anthrax attacks on U.S. media and government outlets (both real and hoax) led to increased attention on the risk of bioterrorism attacks in the United States. Proposals for serious structural reforms, national and/or regional border controls, and a single co-ordinated system of biohazard response abounded.

One of the major challenges of biosecurity is that harmful technology is becoming more available and accessible. Biomedical advances and the globalization of scientific and technical expertise have made it possible to greatly improve public health. However, there is also the risk that these advances can make it easier for terrorists to produce biological weapons.

The proliferation of high biosafety level laboratories around the world has many experts worried about availability of targets for those that might be interested in stealing dangerous pathogens. Emerging and re-emerging disease is also a serious biosecurity concern. The recent growth in containment laboratories is often in response to emerging diseases, many new containment labs' main focus is to find ways to control these diseases. By strengthening national disease surveillance, prevention, control and response systems, these labs are raising international public health to new heights.

Research into biosecurity & biosafety conducted by the United Nations University Institute for the Advanced Study of Sustainability (UNU-IAS) emphasizes "long-term consequences of the development and use of biotechnology" and need for "an honest broker to create avenues and forums to unlock the impasses."

In the October 2011 Bio-Response Report Card, the WMD Center stated that the major challenges to biosecurity are:

attribution
communication
detection and diagnosis
environmental cleanup
medical countermeasure availability
medical countermeasure development and approval process
medical countermeasure dispensing
medical management
Communication between the citizen and law enforcement officials is imperative. Indicators of agro-terrorism at a food processing plant may include persons taking notes or photos of a business,theft of employee uniforms,employees changing working hours,or persons attempting to gain information about security measures and personnel. Unusual activity should be reported to law enforcement personnel promptly.

Communication between policymakers and life sciences scientists is also important.

The MENA region, with its socio-political unrest, diverse cultures and societies, and recent biological weapons programs, faces particular challenges.

Incidents
DateIncidentOrganismDetails
1984Rajneeshee religious cult attacks, The Dalles, OregonSalmonella typhimuriumContaminated restaurant salad bars, hoping to incapacitate the population so their candidates would win the county elections
751 illnesses, Early investigation by CDC suggested the event was a naturally occurring outbreak. Cult member arrested on unrelated charge confessed involvement with the event
1990sAum Shinrikyo attempts in Tokyo, Japan
Tokyo subway sarin attack, Matsumoto incident
Bacillus anthracisClostridium botulinumDissemination: Aerosolization in Tokyo
Shoko Asahara was convicted of criminal activity Aum Shinrikyo ordered C. botulinum from a pharmaceutical company and attempted to acquire from Zaire outbreak under guise of a "humanitarian mission" Resulted in around 20 deaths and more than 4000 injuries
2001"Amerithrax"Bacillus anthracisLetters containing anthrax spores were mailed to media offices and senators
Suspected perpetrator was a US DOD scientist
22 infected, 5 deaths
1995Larry Wayne Harris, a white supremacist, ordered 3 vials of Yersinia pestis from the ATCCYersinia pestis
2003Thomas C. Butler, United States professorYersinia pestis30 vials of Y. pestis missing from lab (never recovered); Butler served 19 months in jail
1966"Dr. X killings"CurareDr. Mario Jascalevich was accused of poisoning 5 patients
1977-1980Arnfinn Nesset, former nurse in NorwaysuccinylcholineConfessed to killing 27 patients, may have killed as many as 138
1987-1990David J. Acer, Florida dentistHIVInfected 6 patients after he was diagnosed with HIV
1995Debora Green, a Kansas physicianricinConvicted of trying to murder her estranged husband with ricin, later killed her family in a house fire
1998Richard J. Schmidt, a gastroenterologist in LouisianaHIVConvicted of attempted second degree murder for infecting nurse Janice Allen with HIV by injecting her with blood from an AIDS patient
1999Brian T. Stewart, a phlebotomistHIVSentenced to life in prison for deliberately infecting his 11-month-old baby with HIV-infected blood to avoid child support payments
1964-1966Dr. Mitsuru Suzuki, physician with training, JapanShigella dysenteriaeand Salmonella typhiObjective: Revenge due to deep antagonism to what he perceived as a prevailing seniority system
Dissemination: Sponge cake, other food sources Official investigation started after anonymous tip to Ministry of Health and Welfare. He was charged, but was not convicted of any deaths; later implicated in 200 – 400 illnesses and 4 deaths
1996Diane Thompson, clinical laboratory technician, Dallas, TXShigella dysenteriae Type 2Removed Shigella dysenteriae Type 2 from hospital's collection and infected co-workers with contaminated pastries in the office breakroom
Infected 12 of her coworkers, she was arrested, convicted, & sentenced to 20 years in prison

Role of education
The advance of the life sciences and biotechnology has the potential to bring great benefits to humankind through responding to societal challenges. However, it is also possible that such advances could be exploited for hostile purposes, something evidenced in a small number of incidents of bioterrorism, but more particularly by the series of large-scale offensive biological warfare programmes carried out by major states in the last century. Dealing with this challenge, which has been labelled the 'dual-use' dilemma requires a number of different activities such as those identified above as being require for biosecurity. However, one of the essential ingredients in ensuring that the life sciences continue to generate great benefits and do not become subject to misuse for hostile purposes is a process of engagement between scientists and the security community and the development of strong ethical and normative frameworks to compliment legal and regulatory measures that are being developed by states.

Regulations
US Select Agent Regulations
Facility registration if it possesses one of 81 Select Agents
Facility must designate a Responsible Official
Background checks for individuals with access to Select Agents
Access controls for areas and containers that contain Select Agents
Detailed inventory requirements for Select Agents
Security, safety, and emergency response plans
Safety and security training
Regulation of transfers of Select Agents
Extensive documentation and recordkeeping
Safety and security inspections

Biological Weapons Convention addresses three relevant issues:
National Implementing Legislation
National Pathogen Security (biosecurity)
International Cooperation
States Parties agree to pursue national implementation of laboratory and transportation biosecurity (2003)

UN 1540
urges States to take preventative measures to mitigate the threat of WMD proliferation by non-state actors
"Take and enforce effective measures to establish domestic controls to prevent the proliferation of ... biological weapons ...; including by establishing appropriate controls over related materials"

European Commission Green Paper on Bio-Preparedness (November 2007)
recommends developing European standards on laboratory biosecurity including Physical protection, access controls, accountability of pathogens, and registration of researchers

Organization for Economic Cooperation and Development
published "Best Practice Guidelines for Biological Resource Centers" including a section on biosecurity in February 2007

Kampala Compact (October 2005) and the Nairobi Announcement (July 2007)
stress importance of implementing laboratory biosafety and biosecurity in Africa

Source from Wikipedia

Biodiversity Crisis

Biodiversity is most commonly used to replace the more clearly defined and long established terms, species diversity and species richness. Biologists most often define biodiversity as the "totality of genes, species and ecosystems of a region". An advantage of this definition is that it seems to describe most circumstances and presents a unified view of the traditional types of biological variety previously identified:

taxonomic diversity (usually measured at the species diversity level)
ecological diversity (often viewed from the perspective of ecosystem diversity)
morphological diversity (which stems from genetic diversity and molecular diversity)
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. 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)...". 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.

One textbook's definition is "variation of life at all levels of biological organization".

Biodiversity can be defined genetically as the diversity of alleles, genes and organisms. They study processes such as mutation and gene transfer that drive evolution.

Measuring diversity at one level in a group of organisms may not precisely correspond to diversity at other levels. However, tetrapod (terrestrial vertebrates) taxonomic and ecological diversity shows a very close correlation.

Number of species
According to Mora and colleagues, the total number of terrestrial species is estimated to be around 8.7 million while the number of oceanic species is much lower, estimated at 2.2 million. The authors note that these estimates are strongest for eukaryotic organisms and likely represent the lower bound of prokaryote diversity. Other estimates include:

220,000 vascular plants, estimated using the species-area relation method
0.7-1 million marine species
10–30 million insects; (of some 0.9 million we know today)
5–10 million bacteria;
1.5-3 million 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)
1 million mites
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 birds and mammals, whereas fishes and arthropods are the least studied animals groups.

Measuring biodiversity
Conservation biologists have designed a variety of objective means to measure biodiversity empirically. Each measure of biodiversity relates to a particular use of the data. For practical conservationists, measurements should include a quantification of values that are commonly shared among locally affected organisms, including humans[clarification needed]. For others, a more economically defensible definition should allow the ensuring of continued possibilities for both adaptation and future use by humans, assuring environmental sustainability.

As a consequence, biologists argue 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 latter approach is sometimes considered too restrictive, as it prohibits ecological succession.

Species loss rates
No longer do we have to justify the existence of humid tropical forests on the feeble grounds that they might carry plants with drugs that cure human disease. Gaia theory forces us to see that they offer much more than this. Through their capacity to evapotranspirate vast volumes of water vapor, they serve to keep the planet cool by wearing a sunshade of white reflecting cloud. Their replacement by cropland could precipitate a disaster that is global in scale.

During the last century, decreases in biodiversity have been increasingly observed. In 2007, German Federal Environment Minister Sigmar Gabriel cited estimates 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. Almost 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. 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 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."

Threats
In 2006 many species were formally classified as rare or endangered or 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.

Jared Diamond describes an "Evil Quartet" of habitat destruction, overkill, introduced species and secondary extinctions. Edward O. Wilson prefers the acronym HIPPO, standing for Habitat destruction, Invasive species, Pollution, human over-Population and Over-harvesting. The most authoritative classification in use today is IUCN's Classification of Direct Threats which has been adopted by major international conservation organizations such as the US Nature Conservancy, the World Wildlife Fund, Conservation International and BirdLife International.

Habitat destruction
Habitat destruction has played a key role in extinctions, especially in relation to tropical forest destruction. Factors contributing to habitat loss include: overconsumption, overpopulation, land use change, deforestation, pollution (air pollution, water pollution, soil contamination) and global warming or climate change.

Habitat size and numbers of species are systematically related. Physically larger species and those living at lower latitudes or in forests or oceans are more sensitive to reduction in habitat area. Conversion to "trivial" standardized ecosystems (e.g., monoculture following deforestation) effectively destroys habitat for the more diverse species that preceded the conversion. Even the simplest forms of agriculture affect diversity - through clearing/draining land, discouraging weeds and "pests", and encouraging just a limited set of domesticated plant and animal species. In some countries lack of property rights or lax law/regulatory enforcement necessarily leads to biodiversity loss (degradation costs having to be supported by the community).

A 2007 study conducted by the National Science Foundation found that biodiversity and genetic diversity are codependent—that diversity among species requires diversity within a species and vice versa. "If any one type is removed from the system, the cycle can break down and the community becomes dominated by a single species." At present, the most threatened ecosystems occur in fresh water, according to the Millennium Ecosystem Assessment 2005, which was confirmed by the "Freshwater Animal Diversity Assessment" organised by the biodiversity platform and the French Institut de recherche pour le développement (MNHNP).

Co-extinctions are a form of habitat destruction. Co-extinction occurs when the extinction or decline in one species accompanies similar processes in another, such as in plants and beetles.

Introduced and invasive species
Barriers such as large rivers, seas, oceans, mountains and 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. Extirpation, 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 zebra mussel, invasion of US waterways was unintentional. In other cases, such as mongooses in Hawaii, the introduction is deliberate but ineffective (nocturnal rats 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 unintended consequences.

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 predators, parasites, or may simply 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 own 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.

Genetic pollution
Endemic species can be threatened with extinction through the process of genetic pollution, i.e. uncontrolled hybridization, introgression and genetic swamping. Genetic pollution leads to homogenization or replacement of local genomes as a result of either a numerical and/or fitness advantage of an introduced species. 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 gene and genotype constellations can be preserved. However, hybridization with or without introgression may, nevertheless, threaten a rare species' existence.

Overexploitation
Overexploitation occurs when a resource is consumed at an unsustainable rate. This occurs on land in the form of overhunting, excessive logging, poor soil conservation in agriculture and the illegal wildlife trade.

About 25% of world fisheries are now overfished to the point where their current biomass is less than the level that maximizes their sustainable yield.

The overkill hypothesis, a pattern of large animal extinctions connected with human migration patterns, can be used explain why megafaunal extinctions can occur within a relatively short time period.

Hybridization, genetic pollution/erosion and food security
In agriculture and 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 loss of genetic diversity and biodiversity as a whole.

Genetically modified organisms contain genetic material that is altered through genetic engineering. Genetically modified crops have become a common source for genetic pollution in not only wild varieties, but also in domesticated varieties derived from classical hybridization.

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.

Climate change
Global warming is also considered to be a major potential threat to global biodiversity in the future. For example, coral reefs - which are biodiversity hotspots - will be lost within the century if global warming continues at the current trend.

Climate change has seen many claims about potential to affect biodiversity but evidence supporting the statement is tenuous. Increasing atmospheric carbon dioxide certainly affects plant morphology and is acidifying oceans, and temperature affects species ranges, phenology, and weather, but the major impacts that have been predicted are still just potential impacts. We have not documented major extinctions yet, even as climate change drastically alters the biology of many species.

In 2004, an international collaborative study on four continents estimated that 10 percent of species would become extinct by 2050 because of global warming. "We need to limit climate change or we wind up with a lot of species in trouble, possibly extinct," said Dr. Lee Hannah, a co-author of the paper and chief climate change biologist at the Center for Applied Biodiversity Science at Conservation International.

A recent study predicts that up to 35% of the world terrestrial carnivores and ungulates will be at higher risk of extinction by 2050 because of the joint effects of predicted climate and land-use change under business-as-usual human development scenarios.

Human overpopulation
The world’s population numbered nearly 7.6 billion as of mid-2017 (which is approximately one billion more inhabitants compared to 2005) and is forecast to reach 11.1 billion in 2100. Sir David King, former chief scientific adviser to the UK government, told a parliamentary inquiry: "It is self-evident that the massive growth in the human population through the 20th century has had more impact on biodiversity than any other single factor." At least until the middle of the 21st century, worldwide losses of pristine biodiverse land will probably depend much on the worldwide human birth rate. Biologists such as Paul R. Ehrlich and Stuart Pimm have noted that human population growth and overconsumption are the main drivers of species extinction.

According to a 2014 study by the World Wildlife Fund, the global human population already exceeds planet's biocapacity - it would take the equivalent of 1.5 Earths of biocapacity to meet our current demands. The report further points that if everyone on the planet had the Footprint of the average resident of Qatar, we would need 4.8 Earths and if we lived the lifestyle of a typical resident of the USA, we would need 3.9 Earths.

The Holocene extinction
Rates of decline in biodiversity in this sixth mass extinction match or exceed rates of loss in the five previous mass extinction events in the fossil record. Loss of biodiversity results in the loss of natural capital that supplies ecosystem goods and services. 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.

Conservation
Conservation biology matured in the mid-20th century as ecologists, naturalists and other scientists began to research and address issues pertaining to global biodiversity declines.

The conservation ethic advocates management of natural resources for the purpose of sustaining biodiversity in species, ecosystems, the evolutionary process and human culture and society.

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 natural capital, market capital and ecosystem services.

In the EU Directive 1999/22/EC zoos are described as having a role in the preservation of the biodiversity of wildlife animals by conducting research or participation in breeding programs.

Protection and restoration techniques
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.

As sustainable populations of the remaining native species in an area become assured, "missing" species that are candidates for reintroduction can be identified using databases such as the Encyclopedia of Life and the Global Biodiversity Information Facility.

Biodiversity banking places a monetary value on biodiversity. One example is the Australian Native Vegetation Management Framework.
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.

Protected areas
Protected areas is meant for affording protection to wild animals and their habitat which also includes forest reserves and biosphere reserves. Protected areas have been set up all over the world with the specific aim of protecting and conserving plants and animals.

National parks
National park and nature reserve is the area selected by governments or private organizations for special protection against damage or degradation with the objective of biodiversity and landscape conservation. National parks are usually owned and managed by national or state governments. 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. Exploitation of habitat or wildlife is banned.

Wildlife sanctuary
Wildlife sanctuaries aim only at conservation of species and have the following features:

The boundaries of the sanctuaries are not limited by state legislation.
The killing, hunting or capturing of any species is prohibited except by or under the control of the highest authority in the department which is responsible for the management of the sanctuary.
Private ownership may be allowed.
Forestry and other usages can also be permitted.

Forest reserves
The forests play a vital role in harbouring more than 45,000 floral and 81,000 faunal species of which 5150 floral and 1837 faunal species are endemic. Plant and animal species confined to a specific geographical area are called endemic species. In reserved forests, 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 covers 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.

Steps to conserve the forest cover
An extensive reforestation/afforestation program should be followed.
Alternative environment-friendly sources of fuel energy such as biogas other than wood should be used.
Loss of biodiversity due to forest fire is a major problem, immediate steps to prevent forest fire need to be taken.
Overgrazing by cattle can damage a forest seriously. Therefore, certain steps should be taken to prevent overgrazing by cattle.
Hunting and poaching should be banned.

Zoological parks
In 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
In 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. In addition, 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.

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.

Legal status

International
United Nations Convention on Biological Diversity (1992) and Cartagena Protocol on Biosafety;
Convention on International Trade in Endangered Species (CITES);
Ramsar Convention (Wetlands);
Bonn Convention on Migratory Species;
World Heritage Convention (indirectly by protecting biodiversity habitats)
Regional Conventions such as the Apia Convention
Bilateral agreements such as the Japan-Australia Migratory Bird Agreement.

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.

Sovereignty principles can rely upon what is better known as Access and Benefit Sharing Agreements (ABAs). The Convention on Biodiversity implies 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.

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.

Analytical limits

Taxonomic and size relationships
Less than 1% of all species that have been described have been studied beyond simply 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.

Diversity study (botany)
The number of morphological attributes that can be scored for diversity study is generally limited and prone to environmental influences; thereby reducing the fine resolution required to ascertain the phylogenetic relationships. DNA based markers- microsatellites otherwise known as simple sequence repeats (SSR) were therefore used for the diversity studies of certain species and their wild relatives.

In the case of cowpea, a study conducted to assess the level of genetic diversity in cowpea germplasm and related wide species, where the relatedness among various taxa were compared, primers useful for classification of taxa identified, and the origin and phylogeny of cultivated cowpea classified show that SSR markers are useful in validating with species classification and revealing the center of diversity.

Source from Wikipedia

Biodiversity

Biodiversity generally refers to the variety and variability of life on Earth. According to the United Nations Environment Programme (UNEP), biodiversity typically measures variation at the genetic,species,and ecosystem level. Terrestrial biodiversity tends to be greater near the equator, which seems to be the result of the warm climate and high primary productivity. Biodiversity is not distributed evenly on Earth, and is richest in the tropics. These tropical forest ecosystems cover less than 10 percent of earth's surface, and contain about 90 percent of the world's species. Marine biodiversity tends to be highest along coasts in the Western Pacific, where sea surface temperature is highest, and in the mid-latitudinal band in all oceans. There are latitudinal gradients in species diversity. Biodiversity generally tends to cluster in hotspots, and has been increasing through time, but will be likely to slow in the future.

Rapid environmental changes typically cause mass extinctions. More than 99.9 percent 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 percent have not yet been described. More recently, in May 2016, scientists reported that 1 trillion species are estimated to be on Earth currently with only one-thousandth of one percent described. The total amount of related DNA base 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 4 TtC (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.

The age of the Earth is about 4.54 billion years. The earliest undisputed evidence of life on Earth dates at least from 3.5 billion years ago, during the Eoarchean Era after a geological crust started to solidify following the earlier molten Hadean Eon. There are microbial mat fossils found in 3.48 billion-year-old sandstone discovered in Western Australia. Other early physical evidence of a biogenic substance is graphite in 3.7 billion-year-old meta-sedimentary rocks discovered in Western Greenland. More recently, in 2015, "remains of biotic life" were found in 4.1 billion-year-old rocks in Western Australia. According to one of the researchers, "If life arose relatively quickly on Earth .. then it could be common in the universe."

Since life began on Earth, five major mass extinctions and several minor events have led to large and sudden drops in biodiversity. The Phanerozoic eon (the last 540 million years) marked a rapid growth in biodiversity via the Cambrian explosion—a period during which the majority of multicellular phyla first appeared. The next 400 million years included repeated, massive biodiversity losses classified as mass extinction events. In the Carboniferous, rainforest collapse led to a great loss of plant and animal life. The Permian–Triassic extinction event, 251 million years ago, was the worst; vertebrate recovery took 30 million years. The most recent, the Cretaceous–Paleogene extinction event, occurred 65 million years ago and has often attracted more attention than others because it resulted in the extinction of the dinosaurs.

The period since the emergence of humans has displayed an ongoing biodiversity reduction and an accompanying loss of genetic diversity. Named the Holocene extinction, the reduction is caused primarily by human impacts, particularly habitat destruction. Conversely, biodiversity positively impacts human health in a number of ways, although a few negative effects are studied.

The United Nations designated 2011–2020 as the United Nations Decade on Biodiversity.

Etymology
The term biological diversity was used first by wildlife scientist and conservationist Raymond F. Dasmann in the year 1968 lay book A Different Kind of Country advocating conservation. The term was widely adopted only after more than a decade, when in the 1980s it came into common usage in science and environmental policy. Thomas Lovejoy, in the foreword to the book Conservation Biology, introduced the term to the scientific community. Until then the term "natural diversity" was common, introduced by The Science Division of The Nature Conservancy in an important 1975 study, "The Preservation of Natural Diversity." By the early 1980s TNC's Science program and its head, Robert E. Jenkins, Lovejoy and other leading conservation scientists at the time in America advocated the use of the term "biological diversity".

The term's contracted form biodiversity may have been coined by W.G. Rosen in 1985 while planning the 1986 National Forum on Biological Diversity organized by the National Research Council (NRC). It first appeared in a publication in 1988 when sociobiologist E. O. Wilson used it as the title of the proceedings of that forum.

Since this period the term has achieved widespread use among biologists, environmentalists, political leaders and concerned citizens.

A similar term in the United States is "natural heritage." It pre-dates the others and is more accepted by the wider audience interested in conservation. Broader than biodiversity, it includes geology and landforms.

Distribution
Biodiversity is not evenly distributed, rather it varies greatly across the globe as well as within regions. Among other factors, the diversity of all living things (biota) depends on temperature, precipitation, altitude, soils, geography and the presence of other species. The study of the spatial distribution of organisms, species and ecosystems, is the science of biogeography.

Diversity consistently measures higher in the tropics and in other localized regions such as the Cape Floristic Region and lower in polar regions generally. Rain forests that have had wet climates for a long time, such as Yasuní National Park in Ecuador, have particularly high biodiversity.

Terrestrial biodiversity is thought to be up to 25 times greater than ocean biodiversity. 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.

Latitudinal gradients
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 mechanisms 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.

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 temperature, moisture, and 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 hypervolumes, whose fractal dimension rises up to three moving towards the equator.

Hotspots
A biodiversity hotspot is a region with a high level of endemic species that have experienced great habitat loss. The term hotspot was introduced in 1988 by Norman Myers. While hotspots are spread all over the world, the majority are forest areas and most are located in the tropics.

Brazil's 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 Madagascar and 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 reptiles, amphibians and 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 mountains, or Northern European peat bogs.

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."

Evolution and history
Biodiversity is the result of 3.5 billion years of evolution. The origin of life has not been definitely established by science, however some evidence suggests that life may already have been well-established only a few hundred million years after the formation of the Earth. Until approximately 600 million years ago, all life consisted of microorganisms – archaea, bacteria, and single-celled protozoans and protists.

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, invertebrate diversity showed little overall trend and vertebrate diversity shows an overall exponential trend. This dramatic rise in diversity was marked by periodic, massive losses of diversity classified as mass extinction events. A significant loss occurred when rainforests collapsed in the carboniferous. The worst was the Permian-Triassic extinction event, 251 million years ago. Vertebrates took 30 million years to recover from this event.

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.

Evolutionary diversification
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 shows 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 per cent of potentially habitable modes and it could be that without human influence the ecological and taxonomic diversity of tetrapods would continue to increase in an exponential fashion until most or all of the available ecospace is filled."

It also appears that the diversity continue 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 population biology, demography and 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. 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 stochastic dynamics.

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.

In 2011, in his Biodiversity-related Niches Differentiation Theory, Roberto Cazzolla Gatti proposed that species themselves are the architects of biodiversity, by proportionally increasing the number of potentially available niches in a given ecosystem. This study led to the idea that biodiversity is autocatalytic. An ecosystem of interdependent species can be, therefore, considered as an emergent autocatalytic set (a self-sustaining network of mutually "catalytic" entities), where one (group of) species enables the existence of (i.e., creates niches for) other species. This view offers a possible answer to the fundamental question of why so many species can coexist in the same ecosystem.

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, land has more species than the ocean; some 8.7 million species may exists on Earth, of which some 2.1 million live in the ocean.

Ecosystem services

The balance of evidence
"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.

Services enhanced

Provisioning services

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.

Regulating services
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)
plants increases soil nutrient remineralization (Synthesis of 103 experimental studies)
of plants increases soil organic matter (Synthesis of 85 experimental studies)

Services with mixed evidence

Provisioning services
None to date

Regulating services
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).

Services hindered

Provisioning services
Greater species diversity of plants reduces primary production (Synthesis of 7 experimental studies)

Regulating services
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

Provisioning services
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)

Regulating services
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)
Effect of 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.

Since the 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.

Agriculture
Agricultural diversity can be divided into two categories: intraspecific diversity, which includes the genetic variety 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).

The control of associated biodiversity is one of the great agricultural challenges that farmers face. On monoculture farms, the approach is generally to eradicate 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 strategies that are more labor-intensive, 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 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 which primarily grows monocultures, relies on biodiversity at some point.

The 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
When 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 Sri Lanka, Brazil and Central America in 1970. A resistant variety was found in Ethiopia. The diseases are themselves a form of biodiversity.

Monoculture was a contributing factor to several agricultural disasters, including the European wine industry collapse in the late 19th century and the US southern corn leaf blight epidemic of 1970.

Although about 80 percent of humans' food supply comes from just 20 kinds of plants, humans use at least 40,000 species. Many people depend on these species for food, shelter and clothing. 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.

Human health
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 Cornell University.

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 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.

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 micro-organisms, 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 favor 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 hiking, birdwatching or natural history study. Biodiversity inspires musicians, painters, sculptors, writers and other artists. Many cultures view themselves as an integral part of the natural world which requires them to respect other living organisms.

Popular activities such as gardening, fishkeeping and specimen collecting 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.

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 mankind in 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.

Ecological services
Biodiversity supports many ecosystem services:

"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 atmosphere and 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 billions in 2003.

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