A biodiversity hotspot is a biogeographic region with significant levels of biodiversity that is threatened by human habitation.[1][2] Norman Myers wrote about the concept in two articles in The Environmentalist in 1988 [3] and 1990,[4] after which the concept was revised following thorough analysis by Myers and others into “Hotspots: Earth’s Biologically Richest and Most Endangered Terrestrial Ecoregions”[5] and a paper published in the journal Nature, both in 2000.[6]

To qualify as a biodiversity hotspot on Myers' 2000 edition of the hotspot map, a region must meet two strict criteria: it must contain at least 1,500 species of vascular plants (more than 0.5% of the world's total) as endemics, and it has to have lost at least 70% of its primary vegetation.[6] Globally, 36 zones qualify under this definition.[7] These sites support nearly 60% of the world's plant, bird, mammal, reptile, and amphibian species, with a high share of those species as endemics. Some of these hotspots support up to 15,000 endemic plant species, and some have lost up to 95% of their natural habitat.[7]

Biodiversity hotspots host their diverse ecosystems on just 2.4% of the planet's surface.[2] Ten hotspots were originally identified by Myer;[1] the current 36 used to cover more than 15.7% of all the land but have lost around 85% of their area.[8] This loss of habitat is why approximately 60% of the world's terrestrial life lives on only 2.4% of the land surface area. Caribbean Islands like Haiti and Jamaica are facing serious pressures on the populations of endemic plants and vertebrates as a result of rapid deforestation. Other areas include the Tropical Andes, Philippines, Mesoamerica, and Sundaland, which, under the current levels at which deforestation is occurring, will likely lose most of their plant and vertebrate species.[9]

Hotspot conservation initiatives

Only a small percentage of the total land area within biodiversity hotspots is now protected. Several international organizations are working to conserve biodiversity hotspots.

  • Critical Ecosystem Partnership Fund (CEPF) is a global program that provides funding and technical assistance to nongovernmental organizations in order to protect the Earth's richest regions of plant and animal diversity, including biodiversity hotspots, high-biodiversity wilderness areas and important marine regions.
  • The World Wide Fund for Nature has devised a system called the "Global 200 Ecoregions", the aim of which is to select priority ecoregions for conservation from fourteen terrestrial, three freshwater, and four marine habitat types. They are chosen for species richness, endemism, taxonomic uniqueness, unusual ecological or evolutionary phenomena, and global rarity. All biodiversity hotspots contain at least one Global 200 Ecoregion.
  • Birdlife International has identified 218 “Endemic Bird Areas” (EBAs) each of which holds two or more bird species found nowhere else. Birdlife International has identified more than 11,000 Important Bird Areas[10] all over the world.
  • Plant life International coordinates programs aiming to identify and manage Important Plant Areas.
  • Alliance for Zero Extinction is an initiative of scientific organizations and conservation groups who co-operate to focus on the most threatened endemic species of the world. They have identified 595 sites, including many Birdlife’s Important Bird Areas.
  • The National Geographic Society has prepared a world map[11] of the hotspots and ArcView shapefile and metadata for the Biodiversity Hotspots[12] including details of the individual endangered fauna in each hotspot, which is available from Conservation International.[13]
  • The Compensatory Afforestation Management and Planning Authority (CAMPA) seeks to control the destruction of forests in India.

Distribution by region

Biodiversity hotspots. Original proposal in green, and added regions in blue.[14]

A majority of biodiversity exists within the tropics; likewise, most biodiversity hotspots are within the tropics.[15] Of the 36 biodiversity hotspots, 15 are classified as old, climatically-buffered, infertile landscapes (OCBILs). [16] These areas have been historically isolated from interactions with other climate zones, but recent human interaction and encroachment have put these historically safe hotspots at risk. OCBILs have mainly been threatened by the relocation of indigenous groups and military actions as the infertile ground has previously dissuaded human populations.[17] The conservation of OCBILs within biodiversity hotspots has started to garner attention because current theories believe these sites provide not only high levels of biodiversity, but they have relatively stable lineages and the potential for high levels of speciation in the future. Because these sites are relatively stable, they can be classified as refugia.[18]

North and Central America

The Caribbean

South America

Europe

Africa

Central Asia

South Asia

Southeast Asia and Asia-Pacific

East Asia

West Asia

Critiques of "Hotspots"

The high profile of the biodiversity hotspots approach has resulted in some criticism. Papers such as Kareiva & Marvier (2003)[21] have argued that the biodiversity hotspots:

  • Do not adequately represent other forms of species richness (e.g. total species richness or threatened species richness).
  • Do not adequately represent taxa other than vascular plants (e.g. vertebrates and fungi).
  • Do not protect smaller scale richness hotspots.
  • Do not make allowances for changing land use patterns. Hotspots represent regions that have experienced considerable habitat loss, but this does not mean they are experiencing ongoing habitat loss. On the other hand, regions that are relatively intact (e.g. the Amazon basin) have experienced relatively little land loss, but are currently losing habitat at tremendous rates.
  • Do not protect ecosystem services.
  • Do not consider phylogenetic diversity.[22]

A recent series of papers has pointed out that biodiversity hotspots (and many other priority region sets) do not address the concept of cost.[23] The purpose of biodiversity hotspots is not simply to identify regions that are of high biodiversity value, but to prioritize conservation spending. The regions identified include some in the developed world (e.g. the California Floristic Province), alongside others in the developing world (e.g. Madagascar). The cost of land is likely to vary between these regions by an order of magnitude or more, but the biodiversity hotspot designations do not consider the conservation importance of this difference. However, the available resources for conservation also tend to vary in this way.

See also

References

  1. 1 2 "Biodiversity Hotspots in India". www.bsienvis.nic.in.
  2. 1 2 "Why Hotspots Matter". Conservation International.
  3. ↑ Myers, N. (1988). "Threatened biotas: "Hot spots" in tropical forests". Environmentalist. 8 (3): 187–208. Bibcode:1988ThEnv...8..187M. doi:10.1007/BF02240252. PMID 12322582. S2CID 2370659.
  4. ↑ Myers, N. The Environmentalist 10 243-256 (1990)
  5. ↑ Russell A. Mittermeier, Norman Myers and Cristina Goettsch Mittermeier, Hotspots: Earth's Biologically Richest and Most Endangered Terrestrial Ecoregions, Conservation International, 2000 ISBN 978-968-6397-58-1
  6. 1 2 Myers, Norman; Mittermeier, Russell A.; Mittermeier, Cristina G.; da Fonseca, Gustavo A. B.; Kent, Jennifer (2000). "Biodiversity hotspots for conservation priorities" (PDF). Nature. 403 (6772): 853–858. Bibcode:2000Natur.403..853M. doi:10.1038/35002501. ISSN 0028-0836. PMID 10706275. S2CID 4414279.
  7. 1 2 "Biodiversity hotspots defined". Critical Ecosystem Partnership Fund. Conservation International. Retrieved 10 August 2020.
  8. ↑ "Biodiversity Hotspots". www.e-education.psu.edu.
  9. ↑ Brooks, Thomas M.; Mittermeier, Russell A.; Mittermeier, Cristina G.; da Fonseca, Gustavo A. B.; Rylands, Anthony B.; Konstant, William R.; Flick, Penny; Pilgrim, John; Oldfield, Sara; Magin, Georgina; Hilton-Taylor, Craig (August 2002). "Habitat Loss and Extinction in the Hotspots of Biodiversity". Conservation Biology. 16 (4): 909–923. Bibcode:2002ConBi..16..909B. doi:10.1046/j.1523-1739.2002.00530.x. ISSN 0888-8892. S2CID 44009934.
  10. ↑ Archived August 8, 2007, at the Wayback Machine
  11. ↑ "Conservation International" (PDF). The Biodiversity Hotspots. 2010-10-07. Archived from the original (PDF) on 2012-03-27. Retrieved 2012-06-22.
  12. ↑ "Conservation International". The Biodiversity Hotspots. 2010-10-07. Archived from the original on 2012-03-20. Retrieved 2012-06-22.
  13. ↑ "Resources". Biodiversityhotspots.org. 2010-10-07. Archived from the original on 2012-03-24. Retrieved 2012-06-22.
  14. ↑ "Biodiversity Hotspots". GEOG 30N: Environment and Society in a Changing World. John A. Dutton e-Education Institute, College of Earth and Mineral Sciences, Pennsylvania State University. Retrieved 3 August 2022.
  15. ↑ Harvey, Michael G.; Bravo, Gustavo A.; Claramunt, Santiago; Cuervo, Andrés M.; Derryberry, Graham E.; Battilana, Jaqueline; Seeholzer, Glenn F.; McKay, Jessica Shearer; O’Meara, Brian C.; Faircloth, Brant C.; Edwards, Scott V.; Pérez-Emán, Jorge; Moyle, Robert G.; Sheldon, Frederick H.; Aleixo, Alexandre (2020-12-11). "The evolution of a tropical biodiversity hotspot". Science. 370 (6522): 1343–1348. Bibcode:2020Sci...370.1343H. doi:10.1126/science.aaz6970. hdl:10138/329703. ISSN 0036-8075. PMID 33303617. S2CID 228084618.
  16. ↑ https://academic.oup.com/biolinnean/article/133/2/266/6118895. Retrieved 2023-03-23. {{cite web}}: Missing or empty |title= (help)
  17. ↑ Hopper, Stephen D.; Silveira, Fernando A. O.; Fiedler, Peggy L. (2016-06-01). "Biodiversity hotspots and Ocbil theory". Plant and Soil. 403 (1): 167–216. Bibcode:2016PlSoi.403..167H. doi:10.1007/s11104-015-2764-2. ISSN 1573-5036. S2CID 254948226.
  18. ↑ Hopper, Stephen D. (2009-09-01). "OCBIL theory: towards an integrated understanding of the evolution, ecology and conservation of biodiversity on old, climatically buffered, infertile landscapes". Plant and Soil. 322 (1): 49–86. Bibcode:2009PlSoi.322...49H. doi:10.1007/s11104-009-0068-0. ISSN 1573-5036. S2CID 28155038.
  19. ↑ "North American Coastal Plain". Critical Ecosystem Partnership Fund. Retrieved 7 February 2019.
  20. ↑ Noss, Reed F.; Platt, William J.; Sorrie, Bruce A.; Weakley, Alan S.; Means, D. Bruce; Costanza, Jennifer; Peet, Robert K. (2015). "How global biodiversity hotspots may go unrecognized: lessons from the North American Coastal Plain" (PDF). Diversity and Distributions. 21 (2): 236–244. Bibcode:2015DivDi..21..236N. doi:10.1111/ddi.12278.
  21. ↑ Kareiva, Peter; Marvier, Michelle (2003). "Conserving Biodiversity Coldspots: Recent calls to direct conservation funding to the world's biodiversity hotspots may be bad investment advice". American Scientist. 91 (4): 344–351. doi:10.1511/2003.4.344. ISSN 0003-0996. JSTOR 27858246. Retrieved 10 May 2022.
  22. ↑ Daru, Barnabas H.; van der Bank, Michelle; Davies, T. Jonathan (2014). "Spatial incongruence among hotspots and complementary areas of tree diversity in southern Africa". Diversity and Distributions. 21 (7): 769–780. doi:10.1111/ddi.12290. S2CID 18417574.
  23. ↑ Possingham, Hugh P.; Wilson, Kerrie A. (August 2005). "Turning up the heat on hotspots". Nature. 436 (7053): 919–920. doi:10.1038/436919a. ISSN 1476-4687. PMID 16107821. S2CID 4398455.

Further reading

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