Distribution and establishment of the alien Australian redclaw crayfish, Cherax quadricarinatus, in the Zambezi Basin
Crayfish are invasive polytrophic keystone species, which are phylogenetically unique on the African continent. The Australian redclaw crayfish Cherax quadricarinatus is invasive in southern African freshwater systems including the Zambezi River Basin. Surveys conducted across the Zambezi Basin (Bot...
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Published in: | Aquatic conservation Vol. 31; no. 11; pp. 3156 - 3168 |
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Abstract | Crayfish are invasive polytrophic keystone species, which are phylogenetically unique on the African continent. The Australian redclaw crayfish Cherax quadricarinatus is invasive in southern African freshwater systems including the Zambezi River Basin. Surveys conducted across the Zambezi Basin (Botswana, Zimbabwe, Namibia and Zambia) between 2017 and 2019 showed that C. quadricarinatus is broadly distributed across the Upper and Middle Zambezi and is rapidly spreading through natural and human‐mediated means across several ecoregions.
The probability of capture (Pcapture), catch per unit effort (CPUE) and population characteristics of C. quadricarinatus from the recent Barotse floodplain invasion were compared with older invasions from Lake Kariba and Kafue River.
The Pcapture and CPUE of C. quadricarinatus in the recently invaded region of the Barotse floodplain were similar to those of the older invasions. Mass and carapace length of C. quadricarinatus from the Barotse floodplain were significantly lower than those of C. quadricarinatus from the older invasions. Sex ratios differed significantly between the three invasive populations. The Barotse floodplain population had a disproportionate investment in females (65.3%) and intersex individuals (8.4%). No crayfish were detected in the Zambezian Headwaters or the Okavango Floodplains ecoregions, but current spread rates are 49 km yr−1 downstream and 12 km yr−1 upstream.
Investment in population management and the prevention of spread will have high conservation value across the invaded regions in order to restrict crayfish ecological impacts via direct predation and competition. In areas where crayfish are in high abundance, existing fisheries are affected through damage to nets, leading to increased net abandonment and ghost gear pollution in invaded regions.
The emphasis should be on developing cohesive transboundary biosecurity policies in southern Africa to limit further spread that will threaten the integrity of freshwater ecosystems. However, long‐term monitoring is needed to gauge invasion risk to sensitive areas such as the Okavango Floodplains ecoregion and determine field‐based ecological impacts. |
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AbstractList | Crayfish are invasive polytrophic keystone species, which are phylogenetically unique on the African continent. The Australian redclaw crayfish Cherax quadricarinatus is invasive in southern African freshwater systems including the Zambezi River Basin. Surveys conducted across the Zambezi Basin (Botswana, Zimbabwe, Namibia and Zambia) between 2017 and 2019 showed that C. quadricarinatus is broadly distributed across the Upper and Middle Zambezi and is rapidly spreading through natural and human‐mediated means across several ecoregions.The probability of capture (Pcapture), catch per unit effort (CPUE) and population characteristics of C. quadricarinatus from the recent Barotse floodplain invasion were compared with older invasions from Lake Kariba and Kafue River.The Pcapture and CPUE of C. quadricarinatus in the recently invaded region of the Barotse floodplain were similar to those of the older invasions. Mass and carapace length of C. quadricarinatus from the Barotse floodplain were significantly lower than those of C. quadricarinatus from the older invasions. Sex ratios differed significantly between the three invasive populations. The Barotse floodplain population had a disproportionate investment in females (65.3%) and intersex individuals (8.4%). No crayfish were detected in the Zambezian Headwaters or the Okavango Floodplains ecoregions, but current spread rates are 49 km yr−1 downstream and 12 km yr−1 upstream.Investment in population management and the prevention of spread will have high conservation value across the invaded regions in order to restrict crayfish ecological impacts via direct predation and competition. In areas where crayfish are in high abundance, existing fisheries are affected through damage to nets, leading to increased net abandonment and ghost gear pollution in invaded regions.The emphasis should be on developing cohesive transboundary biosecurity policies in southern Africa to limit further spread that will threaten the integrity of freshwater ecosystems. However, long‐term monitoring is needed to gauge invasion risk to sensitive areas such as the Okavango Floodplains ecoregion and determine field‐based ecological impacts. Crayfish are invasive polytrophic keystone species, which are phylogenetically unique on the African continent. The Australian redclaw crayfish Cherax quadricarinatus is invasive in southern African freshwater systems including the Zambezi River Basin. Surveys conducted across the Zambezi Basin (Botswana, Zimbabwe, Namibia and Zambia) between 2017 and 2019 showed that C. quadricarinatus is broadly distributed across the Upper and Middle Zambezi and is rapidly spreading through natural and human‐mediated means across several ecoregions. The probability of capture (Pcapture), catch per unit effort (CPUE) and population characteristics of C. quadricarinatus from the recent Barotse floodplain invasion were compared with older invasions from Lake Kariba and Kafue River. The Pcapture and CPUE of C. quadricarinatus in the recently invaded region of the Barotse floodplain were similar to those of the older invasions. Mass and carapace length of C. quadricarinatus from the Barotse floodplain were significantly lower than those of C. quadricarinatus from the older invasions. Sex ratios differed significantly between the three invasive populations. The Barotse floodplain population had a disproportionate investment in females (65.3%) and intersex individuals (8.4%). No crayfish were detected in the Zambezian Headwaters or the Okavango Floodplains ecoregions, but current spread rates are 49 km yr−1 downstream and 12 km yr−1 upstream. Investment in population management and the prevention of spread will have high conservation value across the invaded regions in order to restrict crayfish ecological impacts via direct predation and competition. In areas where crayfish are in high abundance, existing fisheries are affected through damage to nets, leading to increased net abandonment and ghost gear pollution in invaded regions. The emphasis should be on developing cohesive transboundary biosecurity policies in southern Africa to limit further spread that will threaten the integrity of freshwater ecosystems. However, long‐term monitoring is needed to gauge invasion risk to sensitive areas such as the Okavango Floodplains ecoregion and determine field‐based ecological impacts. Crayfish are invasive polytrophic keystone species, which are phylogenetically unique on the African continent. The Australian redclaw crayfish Cherax quadricarinatus is invasive in southern African freshwater systems including the Zambezi River Basin. Surveys conducted across the Zambezi Basin (Botswana, Zimbabwe, Namibia and Zambia) between 2017 and 2019 showed that C. quadricarinatus is broadly distributed across the Upper and Middle Zambezi and is rapidly spreading through natural and human‐mediated means across several ecoregions. The probability of capture ( P capture ), catch per unit effort (CPUE) and population characteristics of C. quadricarinatus from the recent Barotse floodplain invasion were compared with older invasions from Lake Kariba and Kafue River. The P capture and CPUE of C. quadricarinatus in the recently invaded region of the Barotse floodplain were similar to those of the older invasions. Mass and carapace length of C. quadricarinatus from the Barotse floodplain were significantly lower than those of C. quadricarinatus from the older invasions. Sex ratios differed significantly between the three invasive populations. The Barotse floodplain population had a disproportionate investment in females (65.3%) and intersex individuals (8.4%). No crayfish were detected in the Zambezian Headwaters or the Okavango Floodplains ecoregions, but current spread rates are 49 km yr −1 downstream and 12 km yr −1 upstream. Investment in population management and the prevention of spread will have high conservation value across the invaded regions in order to restrict crayfish ecological impacts via direct predation and competition. In areas where crayfish are in high abundance, existing fisheries are affected through damage to nets, leading to increased net abandonment and ghost gear pollution in invaded regions. The emphasis should be on developing cohesive transboundary biosecurity policies in southern Africa to limit further spread that will threaten the integrity of freshwater ecosystems. However, long‐term monitoring is needed to gauge invasion risk to sensitive areas such as the Okavango Floodplains ecoregion and determine field‐based ecological impacts. |
Author | Khaebeb, Fernandu H. Jacobs, Francois J. Ellender, Bruce R. Mwale, Chanda South, Josie Nhiwatiwa, Tamuka Chisule, Gethings Rennie, Craig L. Weyl, Olaf L. F. Richardson, Naomi Musando, Bumango Chomba, Machaya Madzivanzira, Takudzwa C. Coppinger, Christine R. Chalmers, Russell |
Author_xml | – sequence: 1 givenname: Takudzwa C. orcidid: 0000-0001-9683-5798 surname: Madzivanzira fullname: Madzivanzira, Takudzwa C. email: taku1945@live.com organization: South African Institute for Aquatic Biodiversity (SAIAB) – sequence: 2 givenname: Josie orcidid: 0000-0002-6339-4225 surname: South fullname: South, Josie organization: Centre for Invasion Biology, SAIAB – sequence: 3 givenname: Bruce R. surname: Ellender fullname: Ellender, Bruce R. organization: South African Institute for Aquatic Biodiversity – sequence: 4 givenname: Russell surname: Chalmers fullname: Chalmers, Russell organization: Aquatic Ecosystem Services – sequence: 5 givenname: Gethings surname: Chisule fullname: Chisule, Gethings organization: Ministry of Fisheries and Livestock – sequence: 6 givenname: Christine R. orcidid: 0000-0001-5634-2518 surname: Coppinger fullname: Coppinger, Christine R. organization: University College Dublin – sequence: 7 givenname: Fernandu H. orcidid: 0000-0002-9684-4130 surname: Khaebeb fullname: Khaebeb, Fernandu H. organization: Kamutjonga Inland Fisheries Institute – sequence: 8 givenname: Francois J. orcidid: 0000-0002-0354-3022 surname: Jacobs fullname: Jacobs, Francois J. organization: Kamutjonga Inland Fisheries Institute – sequence: 9 givenname: Machaya surname: Chomba fullname: Chomba, Machaya organization: Worldwide Fund for Nature – sequence: 10 givenname: Bumango surname: Musando fullname: Musando, Bumango organization: Department of Fisheries – sequence: 11 givenname: Chanda orcidid: 0000-0001-6370-4601 surname: Mwale fullname: Mwale, Chanda organization: Worldwide Fund for Nature – sequence: 12 givenname: Tamuka orcidid: 0000-0002-5295-0724 surname: Nhiwatiwa fullname: Nhiwatiwa, Tamuka organization: University of Zimbabwe Lake Kariba Research Station – sequence: 13 givenname: Craig L. orcidid: 0000-0001-5690-7590 surname: Rennie fullname: Rennie, Craig L. organization: South African Institute for Aquatic Biodiversity (SAIAB) – sequence: 14 givenname: Naomi surname: Richardson fullname: Richardson, Naomi organization: Aquatic Ecosystem Services – sequence: 15 givenname: Olaf L. F. orcidid: 0000-0002-8935-3296 surname: Weyl fullname: Weyl, Olaf L. F. organization: Centre for Invasion Biology, SAIAB |
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CitedBy_id | crossref_primary_10_1016_j_aquaculture_2023_740377 crossref_primary_10_3897_neobiota_72_71868 crossref_primary_10_1016_j_scitotenv_2021_152325 crossref_primary_10_1051_bioconf_202411305039 crossref_primary_10_1007_s10530_023_03074_8 crossref_primary_10_1016_j_gecco_2022_e02301 crossref_primary_10_1111_lre_12394 |
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Notes | Funding information National Research Foundation (NRF)‐South African Research Chairs Initiative of the Department of Science and Innovation (DSI) Inland Fisheries and Freshwater Ecology, Grant/Award Number: 110507; Worldwide Fund for Nature (WWF) Upper Zambezi Programme that is funded by DOB Ecology; WWF Shared Resources‐Joint Solutions (SRJS) strategic partnership between IUCN Netherlands, WWF Netherlands and the Netherlands Ministry of Foreign Affairs (DGIS); NRF–SAIAB Institutional Support system; DSI–NRF Centre of Excellence for Invasion Biology; DOB Ecology Deceased |
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Snippet | Crayfish are invasive polytrophic keystone species, which are phylogenetically unique on the African continent. The Australian redclaw crayfish Cherax... Crayfish are invasive polytrophic keystone species, which are phylogenetically unique on the African continent. The Australian redclaw crayfish Cherax... |
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SubjectTerms | Barotse floodplain Biosecurity Carapace Catch per unit effort Cherax quadricarinatus CPUE Crayfish Fisheries Floodplains Freshwater Freshwater crustaceans Freshwater ecosystems freshwater invasions Headwaters Inland water environment Interspecific relationships Invasions Invasive species Kafue Keystone species Lake Kariba Lakes Okavango delta Phylogeny Population characteristics population dynamics Predation Probability theory Regions River basins Rivers Sex ratio Surveys Transboundary pollution |
Title | Distribution and establishment of the alien Australian redclaw crayfish, Cherax quadricarinatus, in the Zambezi Basin |
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