The oceans top 30% for biodiversity
The marine biodiversity research group at the University of Auckland has published a world map of where most biodiversity is in the ocean. This is the most representative map of biodiversity to date because it considers marine life from genes to ecosystems. Prioritizing the protection of this 30% of the oceans would protect about 70% of its biodiversity. The map also indicates where monitoring of trends in species abundance would be most effective in documenting change in biodiversity.
The International Union for Conservation of Nature (IUCN) World Conservation Congress called for the full protection of 30% of each marine habitat globally and at least 30% of all the ocean. This map shows where these priority areas would be best located.
The areas were mainly on continental coasts, island arcs, oceanic islands, the southwest Indian Ridge, the northern Mid-Atlantic Ridge, the Coral Triangle (around Indonesia and Philippines), Caribbean Sea, and the Arctic Archipelago.
The project was led by former Ph.D. student Qianshuo Zhao, who previously used 20 kinds of environmental data to produce the first complete world map of marine ecosystems. Another Ph.D. student, Dinusha Jayathilake, produced the new world maps of the seagrass and kelp biomes used in the project.
Although only 30% of the ocean, the mapped areas include 94% of coral reefs and mangrove forests, and 86% of kelp forests and seagrass meadows, and 68% of species. Thus, most biodiversity is protected in the least area.
The analysis found that less than 1 % of the area had been designated to be protected. Ocean protection has hardly begun. It is far off the 10% global target agreed under the Convention on Biological Diversity and in the United Nations Sustainable Development Goals.
Most (58%) of the 30% priority area is coastal and so countries can unilaterally protect it. The remaining 42% is on the High Seas where international agreement is needed. The countries that could contribute most are Canada, Australia, USA, Greenland, Indonesia, Russia, and New Zealand, as they have the largest prioritized areas within their EEZs.
All the maps and underlying data are publicly available. These data include
- Species richness based on modeled ranges of 25,000 species (including deep-sea etc.) nested within 30 realms of endemicity based on cluster analyses of 65,000 species;
- Modeled ranges of the four major marine biomes, seagrass, laminarian kelp, mangroves, and shallow corals;
- Seabed topography as an indicator of other major seabed habitats;
- Seven world shallow-water marine ecosystems based on cluster analyses of 20 environmental layers (including seabed slope and depth, current and wind velocity, wave height, distance from land, sea surface temperature, salinity, pH, oxygen, chlorophyll concentration and primary production, nutrients, ice cover).
The optimal area was selected using decision-support software to identify the areas that complement each other to include most biodiversity. It is a ~100 km resolution.
Freely accessible from this link until 22nd May 2020 https://authors.elsevier.com/c/1aqpU1R~eEhKs
The map can be downloaded from this Figshare link eternally https://doi.org/10.17608/k6.auckland.12082158.v1
Zhao Q, Stephenson F, Lundquist C, Kaschner K, Jayathilake DRM, Costello MJ. 2020. Where Marine Protected Areas would best represent 30% of ocean biodiversity. Biological Conservation 244, 108536. https://doi.org/10.1016/j.biocon.2020.108536 .
This paper built on previous studies by the group that mapped and reviewed current knowledge on marine (1) ecosystems (Zhao et al. 2019a, 2019b, 2020), (2) seagrass and kelp biomes (Jayathilake and Costello 2018, 2019a, 2019b), (3) realms of marine endemicity (Costello et al. 2017, 2018a), (4) habitat classifications, topographic statistics and the three-dimensional nature of the ocean environmental variability (Costello 2009, Costello et al. 2010, 2018b, Costello and Breyer 2017), and (5) the underlying knowledge about biodiversity, biogeography, deep-sea and ocean environment (Costello and Chaudhary 2017, Basher and Costello 2019, Costello et al. 2018b, 2019, 2020), including how poorly mapped it is compared to other Planets.
Previous work also reviewed the benefits of Marine Reserves (Costello 2014, Costello and Ballantine 2015), criteria for prioritizing where to have MPA (Asaad et al. 2017), how connectivity is accommodated by representivity (Costello and Connor 12019), reviewed the distribution of marine biodiversity hotspots (Jefferson and Costello 2019), how to restore giant clams on coral ecosystems (Waters et al. 2013), why marine reserves provide resilience to the effects of climate change (Bates et al. 2019), and designed an MPA network for the Coral Triangle, the most species-rich area in the world oceans (Asaad et al. 2018a, 2018b, 2019a, 2019b).
References to prior publications
Asaad I, Lundquist CJ, Erdmann MV, Costello MJ 2017. Ecological criteria to identify areas for biodiversity conservation. Biological Conservation 213, 309-316.
Asaad I, Lundquist CJ, Erdmann MV, and Costello MJ 2018a. Delineating priority areas for marine biodiversity conservation in the Coral Triangle. Biological Conservation 222, 198–211. https://doi.org/10.1016/j.biocon.2018.03.037
Asaad I, Lundquist CJ, Erdmann MV, and Costello MJ 2018b. Designating spatial priorities for marine biodiversity conservation in the Coral Triangle. Frontiers in Marine Science 5, 400. https://doi.org/10.3389/fmars.2018.00400
Asaad, I., Lundquist, C. J., Erdmann, M. V., Costello, M. J. 2019a. An interactive atlas for marine biodiversity conservation in the Coral Triangle. Earth Syst. Sci. Data 11, 163-174. https://doi.org/10.5194/essd-2018-80.
Asaad I, Lundquist CJ, Erdmann MV, Costello MJ 2019b. The Coral Triangle: the most species rich marine region on earth. In: Encyclopedia of the World’s Biomes. Reference Module in Earth Systems and Environmental Sciences, Elsevier. ISBN 9780124095489. 8 pp. https://doi.org/10.1016/B978-0-12-409548-9.11801-9
Basher Z, Costello MJ, 2019. World Maps of Ocean Environment Variables. In: Encyclopedia of the World’s Biomes. Reference Module in Earth Systems and Environmental Sciences, Elsevier. 11 pp. ISBN 9780124095489. https://doi.org/10.1016/B978-0-12-409548-9.12076-7
Bates AE, Cooke RSC, Duncan MI, Edgar GJ, Bruno J, Benedetti-Cecchi L, Côté IM, Lefcheck JS, Costello MJ, Barrett N, Bird TJ, Fenberg PB, Stuart-Smith RD. 2019. Climate resilience in marine protected areas and the ‘Protection Paradox’. Biological Conservation 236, 305–314. https://doi.org/10.1016/j.biocon.2019.05.005
Costello MJ. 2009. Distinguishing marine habitat classification concepts for ecological data management. Marine Ecology Progress Series 397, 253-268. http://www.int-res.com/abstracts/meps/v397/p253-268/
Costello MJ 2014. Long live Marine Reserves: A review of experiences and benefits. Biological Conservation 176, 289–296. http://dx.doi.org/10.1016/j.biocon.2014.04.023.
Costello MJ., Ballantine B. 2015. Biodiversity conservation should focus on no-take Marine Reserves. Trends in Ecology and Evolution 30 (9), 507-509. https://doi.org/10.1016/j.tree.2015.06.011
Costello MJ, Breyer S. 2017. Ocean depths: the mesopelagic and implications for global warming. Current Biology 27 (1), R36-R38. DOI: 1016/j.cub.2016.11.042.
Costello MJ, Chaudhary C. 2017. Marine biodiversity, biogeography, deep-sea gradients, and conservation. Current Biology 27, R511–R527.
Costello MJ, Connor DW. 2019. Connectivity is generally not important for marine reserve planning. Trends in Ecology and Evolution 34(8), 686-688.
Costello MJ, Cheung A, De Hauwere N. 2010. Topography statistics for the surface and seabed area, volume, depth and slope, of the world’s seas, oceans and countries. Environmental Science and Technology 44, 8821-8828. Data at Available online at http://www.marineregions.org/. Consulted on 2014-08-14.
Costello MJ, Tsai P, Wong PS, Cheung A, Basher Z., Chaudhary C. 2017. Marine biogeographic realms and species endemicity. Nature Communications 8 (1057). https://www.nature.com/articles/s41467-017-01121-2 Data and GIS files at Figshare: https://doi.org/10.17608/k6.auckland.5086654.v1 https://doi.org/10.17608/k6.auckland.5596840.v1
Costello MJ, Tsai P, Cheung A, Basher Z., Chaudhary C. 2018a. Reply to ‘Dissimilarity measures affected by richness differences yield biased delimitations of biogeographic realms’. Nature Communications 9, 5085. DOI 1038/s41467-018-07252-4 https://rdcu.be/bcbpe
Costello MJ, Basher Z, Sayre R. Breyer S, Wright D. 2018b. Stratifying ocean sampling globally and with depth to account for environmental variability. (Nature) Scientific Reports 8, 11259. DOI:10.1038/s41598-018-29419-1. Direct download https://rdcu.be/3xmF
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Costello MJ, Zhao Q, Jayathilake, DRM. 2020. Defining marine spatial units: realms, biomes, ecosystems, seascapes, habitats, biotopes, communities and guilds. In: Encyclopedia of the World’s Biomes. Reference Module in Earth Systems and Environmental Sciences, Elsevier. 11 pp. ISBN 9780124095489. https://doi.org/10.1016/B978-0-12-409548-9.12515-1
Jayathilake D.R.M., Costello MJ. 2018. A modelled global distribution of the seagrass biome. Biological Conservation 226, 120-126. https://doi.org/10.1016/j.biocon.2018.07.009
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Jayathilake DR, Costello MJ 2019b. The kelp biome. In: Encyclopedia of the World’s Biomes. Reference Module in Earth Systems and Environmental Sciences, Elsevier. ISBN 9780124095489. 6 pp. https://doi.org/10.1016/B978-0-12-409548-9.11768-3
Jefferson T, Costello MJ 2019. Hotspots of marine biodiversity. In: Encyclopedia of the World’s Biomes. Reference Module in Earth Systems and Environmental Sciences, Elsevier. 11 pp. ISBN 9780124095489. https://doi.org/10.1016/B978-0-12-409548-9.11952-9
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