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      Limited hybridization between introduced and Critically Endangered indigenous tilapia fishes in northern Tanzania

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          Abstract

          Hybridization between introduced and indigenous species can lead to loss of unique genetic resources and precipitate extinction. In Tanzania, the Nile tilapia ( Oreochromis niloticus) and blue-spotted tilapia ( Oreochromis leucostictus) have been widely introduced to non-native habitats for aquaculture and development of capture fisheries. Here, we aimed to quantify interspecific hybridization between these introduced species and the indigenous species Oreochromis esculentus, Oreochromis jipe and Oreochromis korogwe. In the Pangani basin, several hybrids were observed ( O. niloticus ×  O. jipe, O. leucostictus × O. jipe, O. niloticus ×  O. korogwe), although hybrids were relatively uncommon within samples relative to purebreds. Hybrids between the native O. jipe ×  O. korogwe were also observed. In the Lake Victoria basin, no evidence of hybrids was found. Analysis of body shape using geometric morphometrics suggested that although purebreds could be discriminated from one another, hybrids could not be readily identified on body and head shape alone. These results provide the first evidence of hybridization between the introduced species and the Critically Endangered O. jipe in Tanzania. Given uncertainty regarding benefits of introduced species over large-bodied indigenous species in aquaculture and capture fisheries, we suggest that future introductions of hybridization-prone species should be carefully evaluated.

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          The online version of this article (10.1007/s10750-018-3572-5) contains supplementary material, which is available to authorized users.

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          Scenarios of changes in biodiversity for the year 2100 can now be developed based on scenarios of changes in atmospheric carbon dioxide, climate, vegetation, and land use and the known sensitivity of biodiversity to these changes. This study identified a ranking of the importance of drivers of change, a ranking of the biomes with respect to expected changes, and the major sources of uncertainties. For terrestrial ecosystems, land-use change probably will have the largest effect, followed by climate change, nitrogen deposition, biotic exchange, and elevated carbon dioxide concentration. For freshwater ecosystems, biotic exchange is much more important. Mediterranean climate and grassland ecosystems likely will experience the greatest proportional change in biodiversity because of the substantial influence of all drivers of biodiversity change. Northern temperate ecosystems are estimated to experience the least biodiversity change because major land-use change has already occurred. Plausible changes in biodiversity in other biomes depend on interactions among the causes of biodiversity change. These interactions represent one of the largest uncertainties in projections of future biodiversity change.
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            Invasive species are a leading cause of animal extinctions.

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              Cichlid Fish Diversity Threatened by Eutrophication That Curbs Sexual Selection

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                Author and article information

                Contributors
                bssjb@leeds.ac.uk
                Journal
                Hydrobiologia
                Hydrobiologia
                Hydrobiologia
                Springer International Publishing (Cham )
                0018-8158
                18 April 2018
                18 April 2018
                2019
                : 832
                : 1
                : 257-268
                Affiliations
                [1 ]ISNI 0000 0004 1936 7603, GRID grid.5337.2, School of Biological Sciences, , University of Bristol, ; Life Sciences Building, 24 Tyndall Avenue, Bristol, BS8 1TQ UK
                [2 ]ISNI 0000 0004 1936 8403, GRID grid.9909.9, School of Biology, , University of Leeds, ; Miall Building, Leeds, LS2 9JT UK
                [3 ]GRID grid.463660.1, Tanzania Fisheries Research Institute (TAFIRI), ; P.O. Box 9750, Dar es Salaam, Tanzania
                [4 ]ISNI 0000 0004 0648 0244, GRID grid.8193.3, Department of Aquatic Sciences and Fisheries, , University of Dar es Salaam, ; P.O. Box 35064, Dar es Salaam, Tanzania
                [5 ]ISNI 0000 0004 0412 8669, GRID grid.9481.4, Evolutionary and Environmental Genomics Group, School of Environmental Sciences, , University of Hull, ; Hull, HU5 7RX UK
                [6 ]ISNI 0000000118820937, GRID grid.7362.0, School of Biological Sciences, , Bangor University, ; Bangor, Gwynedd, LL57 2UW UK
                Article
                3572
                10.1007/s10750-018-3572-5
                6394572
                30880834
                7d1161db-5abb-4078-86a6-c48bba81e8f2
                © The Author(s) 2018

                Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License ( http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.

                History
                : 14 November 2017
                : 26 February 2018
                : 27 February 2018
                Funding
                Funded by: FundRef http://dx.doi.org/10.13039/501100000268, Biotechnology and Biological Sciences Research Council;
                Award ID: BB/MO26736/1
                Award Recipient :
                Funded by: FundRef http://dx.doi.org/10.13039/501100000275, Leverhulme Trust;
                Award ID: AA100023
                Award ID: AA130107
                Award Recipient :
                Categories
                Advances in Cichlid Research III
                Custom metadata
                © Springer Nature Switzerland AG 2019

                cichlid fish,introgression,conservation,freshwater fish,invasion biology

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