User:Ldonahue3254/Biodiversity hotspot
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[edit]A biodiversity hotspot is a biogeographic region with significant levels of biodiversity that is threatened by human habitation. Norman Myers wrote about the concept in two articles in The Environmentalist in 1988 and 1990, after which the concept was revised following thorough analysis by Myers and others into “Hotspots: Earth’s Biologically Richest and Most Endangered Terrestrial Ecoregions” and a paper published in the journal Nature, both in 2000.
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. Globally, 36 zones qualify under this definition. 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.
Biodiversity hotspots host their diverse ecosystems on just 2.4% of the planet's surface. Ten hotspots were originally identified by Myer; the current 36 used to cover more than 15.7% of all the land but have lost around 85% of their area. 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.
A majority of biodiversity exists within the tropics; likewise, most biodiversity hotspots are within the tropics.[1] Of the 36 biodiversity hotspots, 15 are classified as old, climatically-buffered, infertile landscapes (OCBILs). [2] 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.[3] 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. [4]
Distribution by region
[edit]Biodiversity hotspots. Original proposal in green, and added regions in blue.
North and Central America
- California Floristic Province (8)
- Madrean pine–oak woodlands (26)
- Mesoamerica (2)
- North American Coastal Plain (36)
The Caribbean
- Atlantic Forest (4)
- Cerrado (6)
- Chilean Winter Rainfall-Valdivian Forests (7)
- Tumbes–Chocó–Magdalena (5)
- Tropical Andes (1)
- Mediterranean Basin (14)
- Cape Floristic Region (12)
- Coastal Forests of Eastern Africa (10)
- Eastern Afromontane (28)
- Guinean Forests of West Africa (11)
- Horn of Africa (29)
- Madagascar and the Indian Ocean Islands (9)
- Maputaland-Pondoland-Albany (27)
- Succulent Karoo (13)
- Eastern Himalaya (32)
- Indo-Burma, Bangladesh, India and Myanmar (19)
- Western Ghats and Sri Lanka (21)
Southeast Asia and Asia-Pacific
- East Melanesian Islands (34)
- New Caledonia (23)
- New Zealand (24)
- Philippines (18)
- Polynesia-Micronesia (25)
- Eastern Australian temperate forests (35)
- Southwest Australia (22)
- Sundaland, Indonesia and Nicobar islands of India (16)
- Wallacea of Indonesia (17)
- Japan (33)
- Mountains of Southwest China (20)
- Caucasus (15)
- Irano-Anatolian (30)
Critiques of "Hotspots"
[edit]The high profile of the biodiversity hotspots approach has resulted in some criticism. Papers such as Kareiva & Marvier (2003) 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.
A recent series of papers has pointed out that biodiversity hotspots (and many other priority region sets) do not address the concept of cost. 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.
References
[edit]- ^ 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. doi:10.1126/science.aaz6970. ISSN 0036-8075.
- ^ academic.oup.com https://academic.oup.com/crawlprevention/governor?content=%2fbiolinnean%2farticle%2f133%2f2%2f266%2f6118895. Retrieved 2023-03-23.
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(help) - ^ 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. doi:10.1007/s11104-015-2764-2. ISSN 1573-5036.
- ^ 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. doi:10.1007/s11104-009-0068-0. ISSN 1573-5036.