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Journal articles on the topic 'Key biodiversity areas'

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1

Bennun, Leon, Mohamed Bakarr, Güven Eken, and Gustavo A. B. Da Fonseca. "Clarifying the Key Biodiversity Areas Approach." BioScience 57, no. 8 (2007): 645. http://dx.doi.org/10.1641/b570816.

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2

EKEN, GÜVEN, LEON BENNUN, THOMAS M. BROOKS, et al. "Key Biodiversity Areas as Site Conservation Targets." BioScience 54, no. 12 (2004): 1110. http://dx.doi.org/10.1641/0006-3568(2004)054[1110:kbaasc]2.0.co;2.

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3

Natori, Yoji, Mari Kohri, Seiji Hayama, and Naamal De Silva. "Key Biodiversity Areas identification in Japan Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2797–805. http://dx.doi.org/10.11609/jott.o2999.2797-805.

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4

Natori, Yoji, Mari Kohri, Seiji Hayama, and Silva Naamal De. "Key Biodiversity Areas identification in Japan Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2797–805. https://doi.org/10.5281/zenodo.13441952.

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(Uploaded by Plazi for the Bat Literature Project) Priority sites within Japan Hotspot were identified using Key Biodiversity Area (KBA) criteria, based on vulnerability and irreplaceability. The identification process considered 217 trigger species from mammals, birds, reptiles, amphibians, freshwater and brackish water fishes and odonates, and focused on identifying gaps in Japan's protected-area system. We identified 228 sites as KBAs and 50 rivers as candidate KBAs. Collectively, KBAs occupy 18% of the land, about half is not protected. Sites selected include natural and semi-natural envir
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5

Natori, Yoji, Mari Kohri, Seiji Hayama, and Silva Naamal De. "Key Biodiversity Areas identification in Japan Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2797–805. https://doi.org/10.5281/zenodo.13441952.

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(Uploaded by Plazi for the Bat Literature Project) Priority sites within Japan Hotspot were identified using Key Biodiversity Area (KBA) criteria, based on vulnerability and irreplaceability. The identification process considered 217 trigger species from mammals, birds, reptiles, amphibians, freshwater and brackish water fishes and odonates, and focused on identifying gaps in Japan's protected-area system. We identified 228 sites as KBAs and 50 rivers as candidate KBAs. Collectively, KBAs occupy 18% of the land, about half is not protected. Sites selected include natural and semi-natural envir
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6

Natori, Yoji, Mari Kohri, Seiji Hayama, and Silva Naamal De. "Key Biodiversity Areas identification in Japan Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2797–805. https://doi.org/10.5281/zenodo.13441952.

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(Uploaded by Plazi for the Bat Literature Project) Priority sites within Japan Hotspot were identified using Key Biodiversity Area (KBA) criteria, based on vulnerability and irreplaceability. The identification process considered 217 trigger species from mammals, birds, reptiles, amphibians, freshwater and brackish water fishes and odonates, and focused on identifying gaps in Japan's protected-area system. We identified 228 sites as KBAs and 50 rivers as candidate KBAs. Collectively, KBAs occupy 18% of the land, about half is not protected. Sites selected include natural and semi-natural envir
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7

Natori, Yoji, Mari Kohri, Seiji Hayama, and Silva Naamal De. "Key Biodiversity Areas identification in Japan Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2797–805. https://doi.org/10.5281/zenodo.13441952.

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(Uploaded by Plazi for the Bat Literature Project) Priority sites within Japan Hotspot were identified using Key Biodiversity Area (KBA) criteria, based on vulnerability and irreplaceability. The identification process considered 217 trigger species from mammals, birds, reptiles, amphibians, freshwater and brackish water fishes and odonates, and focused on identifying gaps in Japan's protected-area system. We identified 228 sites as KBAs and 50 rivers as candidate KBAs. Collectively, KBAs occupy 18% of the land, about half is not protected. Sites selected include natural and semi-natural envir
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8

Natori, Yoji, Mari Kohri, Seiji Hayama, and Silva Naamal De. "Key Biodiversity Areas identification in Japan Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2797–805. https://doi.org/10.5281/zenodo.13441952.

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(Uploaded by Plazi for the Bat Literature Project) Priority sites within Japan Hotspot were identified using Key Biodiversity Area (KBA) criteria, based on vulnerability and irreplaceability. The identification process considered 217 trigger species from mammals, birds, reptiles, amphibians, freshwater and brackish water fishes and odonates, and focused on identifying gaps in Japan's protected-area system. We identified 228 sites as KBAs and 50 rivers as candidate KBAs. Collectively, KBAs occupy 18% of the land, about half is not protected. Sites selected include natural and semi-natural envir
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9

Kouame, O. M. L., N. Jengre, M. Kobele, et al. "Key Biodiversity Areas identification in the Upper Guinea forest biodiversity hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2745–52. http://dx.doi.org/10.11609/jott.o2717.2745-52.

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10

Kouame, O.M.L., N. Jengre, M. Kobele, et al. "Key Biodiversity Areas identification in the Upper Guinea forest biodiversity hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2745–52. https://doi.org/10.5281/zenodo.13450108.

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(Uploaded by Plazi for the Bat Literature Project) Priority-setting approaches and tools are commons ways to support the rapid extinction of species and their habitats and the effective allocation of resources for their conservation. The Key Biodiversity Area (KBA) approach is a method for the identification of fine-scale priority areas for conservation. This process led bottom-up has been used in the Upper Guinea Forest Ecosystem of West Africa where humaninduced changes have increased the extinction risk of several endemic and threatened species. The irreplaceability and vulnerability criter
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11

Kouame, O.M.L., N. Jengre, M. Kobele, et al. "Key Biodiversity Areas identification in the Upper Guinea forest biodiversity hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2745–52. https://doi.org/10.5281/zenodo.13450108.

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(Uploaded by Plazi for the Bat Literature Project) Priority-setting approaches and tools are commons ways to support the rapid extinction of species and their habitats and the effective allocation of resources for their conservation. The Key Biodiversity Area (KBA) approach is a method for the identification of fine-scale priority areas for conservation. This process led bottom-up has been used in the Upper Guinea Forest Ecosystem of West Africa where humaninduced changes have increased the extinction risk of several endemic and threatened species. The irreplaceability and vulnerability criter
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12

Kouame, O.M.L., N. Jengre, M. Kobele, et al. "Key Biodiversity Areas identification in the Upper Guinea forest biodiversity hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2745–52. https://doi.org/10.5281/zenodo.13450108.

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(Uploaded by Plazi for the Bat Literature Project) Priority-setting approaches and tools are commons ways to support the rapid extinction of species and their habitats and the effective allocation of resources for their conservation. The Key Biodiversity Area (KBA) approach is a method for the identification of fine-scale priority areas for conservation. This process led bottom-up has been used in the Upper Guinea Forest Ecosystem of West Africa where humaninduced changes have increased the extinction risk of several endemic and threatened species. The irreplaceability and vulnerability criter
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13

Kouame, O.M.L., N. Jengre, M. Kobele, et al. "Key Biodiversity Areas identification in the Upper Guinea forest biodiversity hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2745–52. https://doi.org/10.5281/zenodo.13450108.

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(Uploaded by Plazi for the Bat Literature Project) Priority-setting approaches and tools are commons ways to support the rapid extinction of species and their habitats and the effective allocation of resources for their conservation. The Key Biodiversity Area (KBA) approach is a method for the identification of fine-scale priority areas for conservation. This process led bottom-up has been used in the Upper Guinea Forest Ecosystem of West Africa where humaninduced changes have increased the extinction risk of several endemic and threatened species. The irreplaceability and vulnerability criter
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14

Kouame, O.M.L., N. Jengre, M. Kobele, et al. "Key Biodiversity Areas identification in the Upper Guinea forest biodiversity hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2745–52. https://doi.org/10.5281/zenodo.13450108.

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(Uploaded by Plazi for the Bat Literature Project) Priority-setting approaches and tools are commons ways to support the rapid extinction of species and their habitats and the effective allocation of resources for their conservation. The Key Biodiversity Area (KBA) approach is a method for the identification of fine-scale priority areas for conservation. This process led bottom-up has been used in the Upper Guinea Forest Ecosystem of West Africa where humaninduced changes have increased the extinction risk of several endemic and threatened species. The irreplaceability and vulnerability criter
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15

Garrett, J. K., P. F. Donald, and K. J. Gaston. "Skyglow extends into the world's Key Biodiversity Areas." Animal Conservation 23, no. 2 (2020): 153–59. http://dx.doi.org/10.1111/acv.12480.

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16

Stuart, Simon N., Thomas M. Brooks, Stuart H. M. Butchart, et al. "Clarifying the key biodiversity areas partnership and programme." Biodiversity and Conservation 27, no. 3 (2017): 791–93. http://dx.doi.org/10.1007/s10531-017-1490-x.

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17

Yahi, N., E. Vela, S. Benhouhou, G. De Belair, and R. Gharzouli. "Identifying Important Plants Areas (Key Biodiversity Areas for Plants) in northern Algeria." Journal of Threatened Taxa 04, no. 08 (2012): 2753–65. http://dx.doi.org/10.11609/jott.o2998.2753-65.

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18

Ambal, R. G. R., M. V. Duya, M. A. Cruz, et al. "Key Biodiversity Areas in the Philippines: Priorities for Conservation." Journal of Threatened Taxa 04, no. 08 (2012): 2788–96. http://dx.doi.org/10.11609/jott.o2995.2788-96.

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19

Brooks, T. M., and P. Matiku. "The science-policy interface for safeguarding key biodiversity areas." Animal Conservation 14, no. 2 (2011): 111–13. http://dx.doi.org/10.1111/j.1469-1795.2011.00452.x.

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20

Ahmad Ruzman, N. H., M. A. Shahfiz, K. Munian, et al. "Key Biodiversity Areas (KBA): An Important Approach in Mainstreaming Biodiversity Conservation in Malaysia." IOP Conference Series: Earth and Environmental Science 842, no. 1 (2021): 012054. http://dx.doi.org/10.1088/1755-1315/842/1/012054.

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21

Ararat, Korsh. "Key Biodiversity Areas: Rapid assessment of birds in Kurdistan, northern Iraq." BioRisk 3 (December 28, 2009): 187–203. https://doi.org/10.3897/biorisk.3.21.

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Bird surveys to help identify and assess Key Biodiversity Areas (KBAs) were undertaken in Kurdistan in the winter and summer of 2008. The winter survey was from 19 January to 8 February and the summer survey from 7 May to 16 June, a total of 45 days. During these periods a total of 34 sites were surveyed in the North Iraq governorates of Sulaimani, Erbil, and Dohuk and 185 species of birds recorded. Of these, according to IUCN criteria, one species was globally endangered, three vulnerable and two near threat- ened. In addition, 32 species were considered to be of conservation concern in Iraq,
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22

Knight, Andrew T., Robert J. Smith, Richard M. Cowling, et al. "Improving the Key Biodiversity Areas Approach for Effective Conservation Planning." BioScience 57, no. 3 (2007): 256–61. http://dx.doi.org/10.1641/b570309.

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23

Eken, Güven, Süreyya Isfendiyaroğlu, Can Yeniyurt, Itri Levent Erkol, Ahmet Karataş, and Murat Ataol. "Identifying key biodiversity areas in Turkey: a multi-taxon approach." International Journal of Biodiversity Science, Ecosystem Services & Management 12, no. 3 (2016): 181–90. http://dx.doi.org/10.1080/21513732.2016.1182949.

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24

Crowe, Olivia, Alison E. Beresford, Graeme M. Buchanan, et al. "A global assessment of forest integrity within Key Biodiversity Areas." Biological Conservation 286 (October 2023): 110293. http://dx.doi.org/10.1016/j.biocon.2023.110293.

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25

Abed, Ibrahim, Clayton Rubec, and Brian Coad. "Key Biodiversity Areas: Rapid assessment of fish fauna in southern Iraq." BioRisk 3 (December 28, 2009): 161–71. https://doi.org/10.3897/biorisk.3.15.

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Surveys of fish in the southern marshes of Iraq are an integral component of the Key Biodiversity Areas (KBA) Project that was initiated in 2005 by Nature Iraq. This included sampling in the January to February and June periods of 2005, 2006 and 2007. Fish species occurrence, relative abundance, and weight and length were recorded. Species of importance for local consumption were noted. An initial project report included details and photographs of the species observed in 2005. Records based on interviews with local residents are noted. Sixteen "Species of Special Concern" are proposed, conside
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26

Anadón-Irizarry, Verónica, David C. Wege, Amy Upgren, et al. "Sites for priority biodiversity conservation in the Caribbean Islands Biodiversity Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2806–44. https://doi.org/10.5281/zenodo.13476713.

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(Uploaded by Plazi for the Bat Literature Project) The Caribbean Islands Biodiversity Hotspot is exceptionally important for global biodiversity conservation due to high levels of species endemism and threat. A total of 755 Caribbean plant and vertebrate species are considered globally threatened, making it one of the top Biodiversity Hotspots in terms of threat levels. In 2009, Key Biodiversity Areas (KBAs) were identified for the Caribbean Islands through a regionallevel analysis of accessible data and literature, followed by extensive national-level stakeholder consultation. By applying the
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27

Anadón-Irizarry, Verónica, David C. Wege, Amy Upgren, et al. "Sites for priority biodiversity conservation in the Caribbean Islands Biodiversity Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2806–44. https://doi.org/10.5281/zenodo.13476713.

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(Uploaded by Plazi for the Bat Literature Project) The Caribbean Islands Biodiversity Hotspot is exceptionally important for global biodiversity conservation due to high levels of species endemism and threat. A total of 755 Caribbean plant and vertebrate species are considered globally threatened, making it one of the top Biodiversity Hotspots in terms of threat levels. In 2009, Key Biodiversity Areas (KBAs) were identified for the Caribbean Islands through a regionallevel analysis of accessible data and literature, followed by extensive national-level stakeholder consultation. By applying the
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28

Anadón-Irizarry, Verónica, David C. Wege, Amy Upgren, et al. "Sites for priority biodiversity conservation in the Caribbean Islands Biodiversity Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2806–44. https://doi.org/10.5281/zenodo.13476713.

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(Uploaded by Plazi for the Bat Literature Project) The Caribbean Islands Biodiversity Hotspot is exceptionally important for global biodiversity conservation due to high levels of species endemism and threat. A total of 755 Caribbean plant and vertebrate species are considered globally threatened, making it one of the top Biodiversity Hotspots in terms of threat levels. In 2009, Key Biodiversity Areas (KBAs) were identified for the Caribbean Islands through a regionallevel analysis of accessible data and literature, followed by extensive national-level stakeholder consultation. By applying the
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29

Anadón-Irizarry, Verónica, David C. Wege, Amy Upgren, et al. "Sites for priority biodiversity conservation in the Caribbean Islands Biodiversity Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2806–44. https://doi.org/10.5281/zenodo.13476713.

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(Uploaded by Plazi for the Bat Literature Project) The Caribbean Islands Biodiversity Hotspot is exceptionally important for global biodiversity conservation due to high levels of species endemism and threat. A total of 755 Caribbean plant and vertebrate species are considered globally threatened, making it one of the top Biodiversity Hotspots in terms of threat levels. In 2009, Key Biodiversity Areas (KBAs) were identified for the Caribbean Islands through a regionallevel analysis of accessible data and literature, followed by extensive national-level stakeholder consultation. By applying the
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30

Anadón-Irizarry, Verónica, David C. Wege, Amy Upgren, et al. "Sites for priority biodiversity conservation in the Caribbean Islands Biodiversity Hotspot." Journal of Threatened Taxa 04, no. 08 (2012): 2806–44. https://doi.org/10.5281/zenodo.13476713.

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(Uploaded by Plazi for the Bat Literature Project) The Caribbean Islands Biodiversity Hotspot is exceptionally important for global biodiversity conservation due to high levels of species endemism and threat. A total of 755 Caribbean plant and vertebrate species are considered globally threatened, making it one of the top Biodiversity Hotspots in terms of threat levels. In 2009, Key Biodiversity Areas (KBAs) were identified for the Caribbean Islands through a regionallevel analysis of accessible data and literature, followed by extensive national-level stakeholder consultation. By applying the
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31

Abed, Ibrahim, Clayton Rubec, and Brian Coad. "Key Biodiversity Areas: Rapid assessment of fish fauna in southern Iraq." BioRisk 3 (December 28, 2009): 161–71. http://dx.doi.org/10.3897/biorisk.3.15.

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32

Ararat, Korsh. "Key Biodiversity Areas: Rapid assessment of birds in Kurdistan, northern Iraq." BioRisk 3 (December 28, 2009): 187–203. http://dx.doi.org/10.3897/biorisk.3.21.

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33

Portocarrero-Aya, Marcela, and Ian G. Cowx. "Conservation of freshwater biodiversity in key areas of the Colombian Amazon." Aquatic Conservation: Marine and Freshwater Ecosystems 26, no. 2 (2015): 350–63. http://dx.doi.org/10.1002/aqc.2582.

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34

Yang, Runjia, Xinyu Dong, Suchen Xu, et al. "Fragmentation of Key Biodiversity Areas highlights attention to human disturbance patterns." Biological Conservation 290 (February 2024): 110428. http://dx.doi.org/10.1016/j.biocon.2023.110428.

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35

Rubec, Clayton, Azzam Alwash, and Anna Bachmann. "The Key Biodiversity Areas Project in Iraq: Objectives and scope 2004–-2008." BioRisk 3 (December 28, 2009): 39–53. https://doi.org/10.3897/biorisk.3.12.

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Nature Iraq conducted biological surveys throughout Iraq during the 2004 to 2008 period under the Key Biodiversity Areas (KBA) Project. This continuing initiative comprises the largest and most comprehensive biological surveys to take place in Iraq in well over 25 years. Under the KBA Project in Iraq, Nature Iraq in cooperation with the Iraqi Ministry of Environment, has visited over one hundred sites in southern Iraq and in Kurdistan in northern Iraq to survey plants, fish, reptile, bird and mammal species. In addition, water quality physical parameters, sediment, plankton and benthic inverte
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36

Melovski, Ljupcho, Metodija Velevski, Vlado Matevski, Vasko Avukatov, and Aleksandar Sarov. "Using important plant areas and important bird areas to identify Key Biodiversity Areas in the Republic of Macedonia." Journal of Threatened Taxa 04, no. 08 (2012): 2766–78. http://dx.doi.org/10.11609/jott.o2997.2766-78.

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37

Harvey, Michael S., Gina M. Ralph, Beth A. Polidoro, Sara M. Maxwell, and Kent E. Carpenter. "Identifying key biodiversity areas as marine conservation priorities in the greater Caribbean." Biodiversity and Conservation 30, no. 13 (2021): 4039–59. http://dx.doi.org/10.1007/s10531-021-02291-8.

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38

Bachmann, Anna, Clayton Rubec, and Azzam Alwash. "The Key Biodiversity Areas Project in Iraq: Objectives and scope 2004–-2008." BioRisk 3 (December 28, 2009): 39–53. http://dx.doi.org/10.3897/biorisk.3.12.

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39

Gerlach, Justin. "Setting Conservation Priorities - A Key Biodiversity Areas Analysis for the Seychelles Islands." Open Conservation Biology Journal 2, no. 1 (2008): 44–53. http://dx.doi.org/10.2174/1874839200802010044.

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40

Bass, D., P. Anderson, and N. De Silva. "Applying thresholds to identify key biodiversity areas for marine turtles in Melanesia." Animal Conservation 14, no. 1 (2010): 1–11. http://dx.doi.org/10.1111/j.1469-1795.2010.00385.x.

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41

Edgar, G. J., and T. M. Brooks. "Testing absolute and percentage thresholds in the identification of key biodiversity areas." Animal Conservation 14, no. 1 (2011): 12–13. http://dx.doi.org/10.1111/j.1469-1795.2011.00438.x.

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42

Dong, Xuede, Jirui Gong, Weiyuan Zhang, et al. "Importance of including Key Biodiversity Areas in China's conservation area-based network." Biological Conservation 296 (August 2024): 110676. http://dx.doi.org/10.1016/j.biocon.2024.110676.

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43

Brooks, T. M., A. Cuttelod, D. P. Faith, J. Garcia-Moreno, P. Langhammer, and S. Pérez-Espona. "Why and how might genetic and phylogenetic diversity be reflected in the identification of key biodiversity areas?" Philosophical Transactions of the Royal Society B: Biological Sciences 370, no. 1662 (2015): 20140019. http://dx.doi.org/10.1098/rstb.2014.0019.

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‘Key biodiversity areas' are defined as sites contributing significantly to the global persistence of biodiversity. The identification of these sites builds from existing approaches based on measures of species and ecosystem diversity and process. Here, we therefore build from the work of Sgró et al. (2011 Evol. Appl. 4 , 326–337. ( doi:10.1111/j.1752-4571.2010.00157.x )) to extend a framework for how components of genetic diversity might be considered in the identification of key biodiversity areas. We make three recommendations to inform the ongoing process of consolidating a key biodiversit
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44

Miu, Iulia V., Laurentiu Rozylowicz, Viorel D. Popescu, and Paulina Anastasiu. "Identification of areas of very high biodiversity value to achieve the EU Biodiversity Strategy for 2030 key commitments." PeerJ 8 (September 30, 2020): e10067. http://dx.doi.org/10.7717/peerj.10067.

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Background The European Union strives to increase protected areas of the EU terrestrial surface to 30% by year 2030, of which one third should be strictly protected. Designation of the Natura 2000 network, the backbone of nature protection in the EU, was mostly an expert-opinion process with little systematic conservation planning. The designation of the Natura 2000 network in Romania followed the same non-systematic approach, resulting in a suboptimal representation of invertebrates and plants. To help identify areas with very high biodiversity without repeating past planning missteps, we pre
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45

Timis-Gansac, Voichita, Lucian Dinca, Cristinel Constandache, Gabriel Murariu, Gabriel Cheregi, and Claudia Simona Cleopatra Timofte. "Conservation Biodiversity in Arid Areas: A Review." Sustainability 17, no. 6 (2025): 2422. https://doi.org/10.3390/su17062422.

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Drylands cover a vast area, and biodiversity conservation in these regions represents a major challenge. A bibliometric study of published research highlighted several key aspects, including publication types, research fields, years of publication, contributing countries, institutions, languages, journals, publishers, authors, and frequently used keywords. The analysis also included plants related to biodiversity conservation in arid areas, animals related to biodiversity conservation in arid areas, and causes of biodiversity decline in arid regions, effects of biodiversity loss in these regio
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46

Xu, Weihua, Yi Xiao, Jingjing Zhang, et al. "Strengthening protected areas for biodiversity and ecosystem services in China." Proceedings of the National Academy of Sciences 114, no. 7 (2017): 1601–6. http://dx.doi.org/10.1073/pnas.1620503114.

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Recent expansion of the scale of human activities poses severe threats to Earth’s life-support systems. Increasingly, protected areas (PAs) are expected to serve dual goals: protect biodiversity and secure ecosystem services. We report a nationwide assessment for China, quantifying the provision of threatened species habitat and four key regulating services—water retention, soil retention, sandstorm prevention, and carbon sequestration—in nature reserves (the primary category of PAs in China). We find that China’s nature reserves serve moderately well for mammals and birds, but not for other m
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47

Corrigan, Colleen M., Jeff A. Ardron, Mia T. Comeros-Raynal, Erich Hoyt, Giuseppe Notarbartolo Di Sciara, and Kent E. Carpenter. "Developing important marine mammal area criteria: learning from ecologically or biologically significant areas and key biodiversity areas." Aquatic Conservation: Marine and Freshwater Ecosystems 24, S2 (2014): 166–83. http://dx.doi.org/10.1002/aqc.2513.

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48

Kohring, Margaret. "Key Biodiversity Areas of Iraq: Priority Sites for Conservation and Protection Nature Iraq." Natural Areas Journal 39, no. 2 (2019): 275. http://dx.doi.org/10.3375/043.039.0214.

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49

Tordoff, A. W., M. C. Baltzer, J. R. Fellowes, J. D. Pilgrim, and P. F. Langhammer. "Key Biodiversity Areas in the Indo-Burma Hotspot: Process, Progress and Future Directions." Journal of Threatened Taxa 04, no. 08 (2012): 2779–87. http://dx.doi.org/10.11609/jott.o3000.2779-87.

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50

Zhong, Zhengle. "Balance Nature and Culture: Key to Ease Tensions Between Indigenous Peoples and Protected Areas." Communications in Humanities Research 64, no. 1 (2024): 11–16. https://doi.org/10.54254/2753-7064/2024.18491.

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Abstract:
Indigenous peoples have long-standing connections to their lands, however, the establishment of protected areas has often led to their exclusion and marginalization. This review examines the complicated relationship between Indigenous peoples and protected areas, highlighting the thresholds during historical conflicts that intensified tensions. As the number of protected areas has increased globally, wildlife biodiversity remains at risk. The article argues that participatory efforts involving Indigenous peoples often play a crucial role in maintaining biodiversity. It explores the challenges
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