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Journal articles on the topic 'Biodiversity hotspots'

Author: Grafiati

Published: 4 June 2021

Last updated: 25 July 2025

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1

Reid, Walter V. "Biodiversity hotspots." Trends in Ecology & Evolution 13, no. 7 (1998): 275–80. http://dx.doi.org/10.1016/s0169-5347(98)01363-9.

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2

Ceballos, Gerardo, and Paul R. Ehrlich. "Global mammal distributions, biodiversity hotspots, and conservation." Proceedings of the National Academy of Sciences 103, no. 51 (2006): 19374–79. https://doi.org/10.5281/zenodo.14820552.

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(Uploaded by Plazi for the Bat Literature Project) Hotspots, which have played a central role in the selection of sites for reserves, require careful rethinking. We carried out a global examination of distributions of all nonmarine mammals to determine patterns of species richness, endemism, and endangerment, and to evaluate the degree of congruence among hotspots of these three measures of diversity in mammals. We then compare congruence of hotspots in two animal groups (mammals and birds) to assess the generality of these patterns. We defined hotspots as the richest 2.5% of cells in a global

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3

Huang, Jihong, Canran Liu, Zhongjun Guo, et al. "Seed plant features, distribution patterns, diversity hotspots, and conservation gaps in Xinjiang, China." Nature Conservation 27 (June 7, 2018): 1–15. http://dx.doi.org/10.3897/natureconservation.27.23728.

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The flora in Xinjiang is unique. Decisions about biodiversity conservation and management based on seed plant diversity hotspots and conservation gaps in Xinjiang are essential to maintain this unique flora. Based on a species distribution dataset of seed plants, we measured seed plant diversity using species richness and phylogenetic diversity indices. Five percent of Xinjiang’s total land area with the highest biodiversity was used to identify hotspots for each index. In total, eight hotspots were identified. Most hotspots were located in mountainous areas, mainly in the Tianshan Mountains a

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4

Huang, Jihong, Canran Liu, Zhongjun Guo, et al. "Seed plant features, distribution patterns, diversity hotspots, and conservation gaps in Xinjiang, China." Nature Conservation 27 (June 7, 2018): 1–15. https://doi.org/10.3897/natureconservation.27.23728.

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The flora in Xinjiang is unique. Decisions about biodiversity conservation and management based on seed plant diversity hotspots and conservation gaps in Xinjiang are essential to maintain this unique flora. Based on a species distribution dataset of seed plants, we measured seed plant diversity using species richness and phylogenetic diversity indices. Five percent of Xinjiang's total land area with the highest biodiversity was used to identify hotspots for each index. In total, eight hotspots were identified. Most hotspots were located in mountainous areas, mainly in the Tianshan Mountains a

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5

NORMAN, MYERS. "Biodiversity Hotspots Revisited." BioScience 53, no. 10 (2003): 916. http://dx.doi.org/10.1641/0006-3568(2003)053[0916:bhr]2.0.co;2.

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6

Sundaram, Mekala, Michael J. Donoghue, Aljos Farjon, et al. "Accumulation over evolutionary time as a major cause of biodiversity hotspots in conifers." Proceedings of the Royal Society B: Biological Sciences 286, no. 1912 (2019): 20191887. http://dx.doi.org/10.1098/rspb.2019.1887.

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Biodiversity hotspots are important for understanding how areas of high species richness form, but disentangling the processes that produce them is difficult. We combine geographical ranges, phylogenetic relationships and trait data for 606 conifer species in order to explore the mechanisms underlying richness hotspot formation. We identify eight richness hotspots that overlap known centres of plant endemism and diversity, and find that conifer richness hotspots occur in mountainous areas within broader regions of long-term climate stability. Conifer hotspots are not unique in their species co

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7

Pipan, Tanja, Louis Deharveng, and David C. Culver. "Hotspots of Subterranean Biodiversity." Diversity 12, no. 5 (2020): 209. http://dx.doi.org/10.3390/d12050209.

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Worldwide, caves and groundwater habitats harbor thousands of species modified and limited to subterranean habitats in karst. Data are concentrated in Europe and USA, where a number of detailed analyses have been performed. Much less is known with respect to global patterns due to a lack of data. This special issue will focus on and discuss the global patterns of individual hotspot caves and groundwater habitats.

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8

HANSON, THOR, THOMAS M. BROOKS, GUSTAVO A. B. DA FONSECA, et al. "Warfare in Biodiversity Hotspots." Conservation Biology 23, no. 3 (2009): 578–87. http://dx.doi.org/10.1111/j.1523-1739.2009.01166.x.

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9

Kitching, Roger. "Biodiversity, hotspots and defiance." Trends in Ecology & Evolution 15, no. 12 (2000): 484–85. http://dx.doi.org/10.1016/s0169-5347(00)02001-2.

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10

Amori, Giovanni, Spartaco Gippoliti, and Luca Luiselli. "Do biodiversity hotspots match with rodent conservation hotspots?" Biodiversity and Conservation 20, no. 14 (2011): 3693–700. http://dx.doi.org/10.1007/s10531-011-0131-z.

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11

Mihaljević, Morana, Chelsea Korpanty, Willem Renema, Kevin Welsh, and John M. Pandolfi. "Identifying patterns and drivers of coral diversity in the Central Indo-Pacific marine biodiversity hotspot." Paleobiology 43, no. 3 (2017): 343–64. http://dx.doi.org/10.1017/pab.2017.1.

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AbstractBiodiversity hotspots are increasingly recognized as areas of high taxonomic and functional diversity. These hotspots are dynamic and shift geographically over time in response to environmental change. To identify drivers of the origin, evolution, and persistence of diversity hotspots, we investigated the diversity patterns of reef-building corals (Scleractinia) in the Central Indo-Pacific, a marine biodiversity hotspot for the last 25 Myr. We used the scleractinian fossil record (based on literature and a newly acquired fossil collection) to examine the taxonomic and functional divers

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12

Zhao, Linlin, Tingting Li, Bailin Cong, Bei Wang, Kaiyu Liu, and Shenghao Liu. "Marine Biodiversity Conservation Planning in the Indo-Pacific Convergence Zone Based on Ecological Spatial Analysis." Biology 14, no. 6 (2025): 700. https://doi.org/10.3390/biology14060700.

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Marine biodiversity is of critical importance to global ecosystems. The Indo-Pacific Convergence Zone (IPCZ), a global marine biodiversity hotspot, faces escalating threats from human activities and climate change. This underscores the pressing need to develop effective conservation strategies for marine biodiversity in the IPCZ. This study integrates spatial analysis of ecological sensitivity (coral reefs, mangroves, and seagrass) and anthropogenic pressures (shipping/fishing intensity) to identify biodiversity hotspots and conservation gaps. Using datasets from UNEP-WCMC, OBIS, and Global Fi

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13

Cunningham, Caitlin, and Karen Beazley. "Changes in Human Population Density and Protected Areas in Terrestrial Global Biodiversity Hotspots, 1995–2015." Land 7, no. 4 (2018): 136. http://dx.doi.org/10.3390/land7040136.

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Biodiversity hotspots are rich in endemic species and threatened by anthropogenic influences and, thus, considered priorities for conservation. In this study, conservation achievements in 36 global biodiversity hotspots (25 identified in 1988, 10 added in 2011, and one in 2016) were evaluated in relation to changes in human population density and protected area coverage between 1995 and 2015. Population densities were compared against 1995 global averages, and percentages of protected area coverage were compared against area-based targets outlined in Aichi target 11 of the Convention on Biolog

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14

Kong, Xuesong, Zhengzi Zhou, and Limin Jiao. "Hotspots of land-use change in global biodiversity hotspots." Resources, Conservation and Recycling 174 (November 2021): 105770. http://dx.doi.org/10.1016/j.resconrec.2021.105770.

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15

Deharveng, Louis, Tanja Pipan, Anne Bedos, and David C. Culver. "Hotspots of Subterranean Biodiversity Redux." Diversity 14, no. 10 (2022): 794. http://dx.doi.org/10.3390/d14100794.

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16

Jepson, Paul, and Susan Canney. "Biodiversity hotspots: hot for what?" Global Ecology and Biogeography 10, no. 3 (2001): 225–27. http://dx.doi.org/10.1046/j.1466-822x.2001.00255.x.

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17

Cyranoski, David. "Calls to conserve biodiversity hotspots." Nature 439, no. 7078 (2006): 774. http://dx.doi.org/10.1038/439774a.

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18

Vamosi, J. C., T. M. Knight, J. A. Steets, S. J. Mazer, M. Burd, and T. L. Ashman. "Pollination decays in biodiversity hotspots." Proceedings of the National Academy of Sciences 103, no. 4 (2006): 956–61. http://dx.doi.org/10.1073/pnas.0507165103.

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19

Hopper, Stephen D., Fernando A. O. Silveira, and Peggy L. Fiedler. "Biodiversity hotspots and Ocbil theory." Plant and Soil 403, no. 1-2 (2015): 167–216. http://dx.doi.org/10.1007/s11104-015-2764-2.

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20

Myers, Norman, Russell A. Mittermeier, Cristina G. Mittermeier, Gustavo A. B. da Fonseca, and Jennifer Kent. "Biodiversity hotspots for conservation priorities." Nature 403, no. 6772 (2000): 853–58. http://dx.doi.org/10.1038/35002501.

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21

Dalton, Rex. "Biodiversity cash aimed at hotspots." Nature 406, no. 6798 (2000): 818. http://dx.doi.org/10.1038/35022730.

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22

Weinzettel, Jan, David Vačkář, and Helena Medková. "Human footprint in biodiversity hotspots." Frontiers in Ecology and the Environment 16, no. 8 (2018): 447–52. http://dx.doi.org/10.1002/fee.1825.

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23

Myers, Norman, Russell A. Mittermeier, Cristina G. Mittermeier, Fonseca Gustavo A. B. Da, and Jennifer Kent. "Biodiversity hotspots for conservation priorities." Nature 403, no. 6772 (2000): 853–58. https://doi.org/10.5281/zenodo.13511321.

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24

Myers, Norman, Russell A. Mittermeier, Cristina G. Mittermeier, Fonseca Gustavo A. B. Da, and Jennifer Kent. "Biodiversity hotspots for conservation priorities." Nature 403, no. 6772 (2000): 853–58. https://doi.org/10.5281/zenodo.13511321.

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25

Myers, Norman, Russell A. Mittermeier, Cristina G. Mittermeier, Fonseca Gustavo A. B. Da, and Jennifer Kent. "Biodiversity hotspots for conservation priorities." Nature 403, no. 6772 (2000): 853–58. https://doi.org/10.5281/zenodo.13511321.

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26

Myers, Norman, Russell A. Mittermeier, Cristina G. Mittermeier, Fonseca Gustavo A. B. Da, and Jennifer Kent. "Biodiversity hotspots for conservation priorities." Nature 403, no. 6772 (2000): 853–58. https://doi.org/10.5281/zenodo.13511321.

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27

Xu, Si-Yuan, Tian-Ci Yi, Jian-Jun Guo, and Dao-Chao Jin. "Four New Species of Larval Charletonia and Leptus (Acari: Trombidiformes: Erythraeidae), with a Checklist of the Two Genera and Their Hosts from China." Insects 13, no. 12 (2022): 1154. http://dx.doi.org/10.3390/insects13121154.

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Four new species, Charletonia rectangia Xu and Jin sp. nov., Leptus (Leptus) bomiensis Xu and Jin sp. nov., Leptus (Leptus) longisolenidionus Xu and Jin sp. nov., and Leptus (Leptus) striatus Xu and Jin sp. nov. are described and illustrated based on larvae. All four new species are from biodiversity hotspots, L. (L.) bomiensissp. nov. from the Eastern Himalayas biodiversity hotspot, while the other three species from the Indo–Burma biodiversity hotspot.

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28

Vincent, Holly, David Hole, and Nigel Maxted. "Congruence between global crop wild relative hotspots and biodiversity hotspots." Biological Conservation 265 (January 2022): 109432. http://dx.doi.org/10.1016/j.biocon.2021.109432.

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29

Kougioumoutzis, Konstantinos, Ioannis P. Kokkoris, Panayiotis Trigas, Arne Strid, and Panayotis Dimopoulos. "Projected Impacts of Climate and Land Use Change on Endemic Plant Distributions in a Mediterranean Island Hotspot: The Case of Evvia (Aegean, Greece)." Climate 13, no. 5 (2025): 100. https://doi.org/10.3390/cli13050100.

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Anthropogenic climate and land use change pose major threats to island floras worldwide, yet few studies have integrated these drivers in a single vulnerability assessment. Here, we examine the endemic flora of Evvia, the second-largest Aegean island in Greece and an important biodiversity hotspot, as a model system to address how these disturbances may reshape species distributions, community composition, and phylogenetic diversity patterns. We used species distribution models under the Ensemble of Small Models and the ENphylo framework, specifically designed to overcome parameter uncertainty

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30

Gavish, Yoni. "Questioning Israel's Great Biodiversity—Relative to Whom? A Comment on Roll et al., 2009." Israel Journal of Ecology and Evolution 57, no. 3 (2011): 183–92. http://dx.doi.org/10.1560/ijee.57.3.183.

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Each evolutionary-independent province has its own mainland species area relationship (SPAR). When using the power law SPAR (S = cAz), separate mainland SPARs are parallel in a log-log space (similar z value), yet they differ in species density per unit area (c value). This implies that there are two main SPAR-based strategies to identify biodiversity hotspots. The first treats all mainland SPARs of all provinces as if they form one global SPAR. This is the strategy employed by Roll et al. (2009) when questioning Israel's high biodiversity. They concluded that Israel is not a global biodiversi

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31

Rizun, V., A. Novikov, K. Hushtan, et al. "Rare component of biota in the Data Centre "Biodiversity of Ukraine" and its possible use to identify hotspot areas and evaluation of biodiversity." Biosystems Diversity 32, no. 3 (2024): 334–44. http://dx.doi.org/10.15421/012436.

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The problem of assessing the diversity of biotic complexes is extremely important and relevant and has been covered in numerous publications, mostly for certain taxonomic groups. The use of information retrieval systems with large databases opens up new opportunities and approaches to automated biodiversity assessment. All the data used in this article are taken from the web resource of the Data Centre “Biodiversity of Ukraine” and include data from museum collections, literature and human observation. To evaluate species diversity included in the Red Data Book of Ukraine, we developed a scori

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32

Culver, David C., Louis Deharveng, Tanja Pipan, and Anne Bedos. "An Overview of Subterranean Biodiversity Hotspots." Diversity 13, no. 10 (2021): 487. http://dx.doi.org/10.3390/d13100487.

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33

Harcourt, A. H. "Coincidence and mismatch of biodiversity hotspots." Biological Conservation 93, no. 2 (2000): 163–75. http://dx.doi.org/10.1016/s0006-3207(99)00145-7.

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34

Willis, Katherine J., Lindsey Gillson, and Sandra Knapp. "Biodiversity hotspots through time: an introduction." Philosophical Transactions of the Royal Society B: Biological Sciences 362, no. 1478 (2006): 169–74. http://dx.doi.org/10.1098/rstb.2006.1976.

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International targets set for reducing the rate of biodiversity loss—the 2010 target—and ensuring environmental stability (Millennium Development Goals) have helped to focus the efforts of the scientific community on providing the data necessary for their implementation. The urgency of these goals, coupled with the increased rate of habitat alteration worldwide, has meant that actions have largely not taken into account the increasing body of data about the biodiversity change in the past. We know a lot about how our planet has been altered and recovered in the past, both in deep time and thro

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35

Cooper, M. "Biodiversity hotspots in the developing world." Trends in Ecology & Evolution 13, no. 10 (1998): 409. http://dx.doi.org/10.1016/s0169-5347(98)01469-4.

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36

Cincotta, Richard P., Jennifer Wisnewski, and Robert Engelman. "Human population in the biodiversity hotspots." Nature 404, no. 6781 (2000): 990–92. http://dx.doi.org/10.1038/35010105.

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37

Contreras-Medina, Raúl, Juan J. Morrone, and Isolda Luna Vega. "Biogeographic methods identify gymnosperm biodiversity hotspots." Naturwissenschaften 88, no. 10 (2001): 427–30. http://dx.doi.org/10.1007/s001140100252.

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38

Schmiing, M., H. Diogo, RS Santos, and P. Afonso. "Assessing hotspots within hotspots to conserve biodiversity and support fisheries management." Marine Ecology Progress Series 513 (October 22, 2014): 187–99. http://dx.doi.org/10.3354/meps10924.

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39

Bao, Wenhui, Xingyu Zeng, Chunyu Luo, Hongqiang Zhang, Yi Qu, and Nan Xu. "The Relationship between Hydrological Connectivity Changes Inside and Outside Biodiversity Hotspots and Its Implication for Sustainable Environmental Management." Sustainability 14, no. 11 (2022): 6654. http://dx.doi.org/10.3390/su14116654.

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The conservation management of biodiversity hotspots is of vital significance for biological conservation. For wetlands, which are a special type of ecosystems that are based on water as their main medium, a decline in external hydrological connectivity often leads to wetland degradation inside biodiversity hotspots. In this context, the relationship between hydrological connectivity changes inside and outside hotspots is worth exploring. Based on the wetland biodiversity hotspots identified using systematic conservation planning, this study selected eight representative biodiversity hotspots

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40

Santos, Sara M., J. Tiago Marques, André Lourenço, et al. "Sampling effects on the identification of roadkill hotspots: Implications for survey design." Journal of Environmental Management 162 (June 12, 2015): 87–95. https://doi.org/10.5281/zenodo.13431164.

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(Uploaded by Plazi for the Bat Literature Project) Although locating wildlife roadkill hotspots is essential to mitigate road impacts, the influence of study design on hotspot identification remains uncertain. We evaluated how sampling frequency affects the accuracy of hotspot identification, using a dataset of vertebrate roadkills (n ¼ 4427) recorded over a year of daily surveys along 37 km of roads. "True" hotspots were identified using this baseline dataset, as the 500-m segments where the number of road-killed vertebrates exceeded the upper 95% confidence limit of the mean, assuming a Pois

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41

Santos, Sara M., J. Tiago Marques, André Lourenço, et al. "Sampling effects on the identification of roadkill hotspots: Implications for survey design." Journal of Environmental Management 162 (June 7, 2015): 87–95. https://doi.org/10.5281/zenodo.13431164.

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(Uploaded by Plazi for the Bat Literature Project) Although locating wildlife roadkill hotspots is essential to mitigate road impacts, the influence of study design on hotspot identification remains uncertain. We evaluated how sampling frequency affects the accuracy of hotspot identification, using a dataset of vertebrate roadkills (n ¼ 4427) recorded over a year of daily surveys along 37 km of roads. "True" hotspots were identified using this baseline dataset, as the 500-m segments where the number of road-killed vertebrates exceeded the upper 95% confidence limit of the mean, assuming a Pois

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42

Santos, Sara M., J. Tiago Marques, André Lourenço, et al. "Sampling effects on the identification of roadkill hotspots: Implications for survey design." Journal of Environmental Management 162 (July 3, 2015): 87–95. https://doi.org/10.5281/zenodo.13431164.

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(Uploaded by Plazi for the Bat Literature Project) Although locating wildlife roadkill hotspots is essential to mitigate road impacts, the influence of study design on hotspot identification remains uncertain. We evaluated how sampling frequency affects the accuracy of hotspot identification, using a dataset of vertebrate roadkills (n ¼ 4427) recorded over a year of daily surveys along 37 km of roads. "True" hotspots were identified using this baseline dataset, as the 500-m segments where the number of road-killed vertebrates exceeded the upper 95% confidence limit of the mean, assuming a Pois

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43

Santos, Sara M., J. Tiago Marques, André Lourenço, et al. "Sampling effects on the identification of roadkill hotspots: Implications for survey design." Journal of Environmental Management 162 (July 10, 2015): 87–95. https://doi.org/10.5281/zenodo.13431164.

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(Uploaded by Plazi for the Bat Literature Project) Although locating wildlife roadkill hotspots is essential to mitigate road impacts, the influence of study design on hotspot identification remains uncertain. We evaluated how sampling frequency affects the accuracy of hotspot identification, using a dataset of vertebrate roadkills (n ¼ 4427) recorded over a year of daily surveys along 37 km of roads. "True" hotspots were identified using this baseline dataset, as the 500-m segments where the number of road-killed vertebrates exceeded the upper 95% confidence limit of the mean, assuming a Pois

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44

Santos, Sara M., J. Tiago Marques, André Lourenço, et al. "Sampling effects on the identification of roadkill hotspots: Implications for survey design." Journal of Environmental Management 162 (July 17, 2015): 87–95. https://doi.org/10.5281/zenodo.13431164.

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(Uploaded by Plazi for the Bat Literature Project) Although locating wildlife roadkill hotspots is essential to mitigate road impacts, the influence of study design on hotspot identification remains uncertain. We evaluated how sampling frequency affects the accuracy of hotspot identification, using a dataset of vertebrate roadkills (n ¼ 4427) recorded over a year of daily surveys along 37 km of roads. "True" hotspots were identified using this baseline dataset, as the 500-m segments where the number of road-killed vertebrates exceeded the upper 95% confidence limit of the mean, assuming a Pois

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45

Rahmani, Asad R. "Hotspots and Coldspots." Journal of the Bombay Natural History Society 102 (June 12, 2005): 1–2. https://doi.org/10.5281/zenodo.13468097.

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46

Rahmani, Asad R. "Hotspots and Coldspots." Journal of the Bombay Natural History Society 102 (June 7, 2005): 1–2. https://doi.org/10.5281/zenodo.13468097.

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47

Rahmani, Asad R. "Hotspots and Coldspots." Journal of the Bombay Natural History Society 102 (July 3, 2005): 1–2. https://doi.org/10.5281/zenodo.13468097.

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48

Rahmani, Asad R. "Hotspots and Coldspots." Journal of the Bombay Natural History Society 102 (July 10, 2005): 1–2. https://doi.org/10.5281/zenodo.13468097.

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49

Rahmani, Asad R. "Hotspots and Coldspots." Journal of the Bombay Natural History Society 102 (July 17, 2005): 1–2. https://doi.org/10.5281/zenodo.13468097.

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50

Moore, Margaret. "THE BIODIVERSITY CRISIS, BIODIVERSITY HOTSPOTS, AND OUR OBLIGATIONS WITH RESPECT TO THEM." Social Philosophy and Policy 40, no. 2 (2023): 482–502. http://dx.doi.org/10.1017/s0265052524000165.

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AbstractThis essay argues that we have a duty to protect biodiversity hotspots, rooted in an argument about the wrongful imposition of risk and intergenerational justice. State authority over territory and resources is not unlimited; the state has a duty to protect these areas. The essay argues that although biodiversity loss is a global problem, it can be tackled at the domestic level through clear rules. The argument thus challenges the usual view of state sovereignty, which holds that authority over territory, resources, and migration (all of which are connected to the protection of biodive

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