DNA barcoding as a useful tool for identifying non-native species of freshwater ichthyoplankton in the neotropics

Almeida, Fernanda Simões de; Frantine‐Silva, Wilson; Lima, Same Costa; Garcia, Diego Azevedo Zoccal; Órsi, Mário Luís

doi:10.1007/s10750-017-3443-5

Cited by 17 publications

(15 citation statements)

References 36 publications

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“…Such results follow the pattern found in the Neotropical regions, showing the dominance of Siluriformes and Characiformes (Agostinho et al 1997, Lowe-McConnell 1999, Jarduli et al 2020. Furthermore, among Paranapanema River tributaries, the number of species is lower if compared to the Tibagi River basin, where 158 species were registered (Lobón-Cerviá & Bennemann 2000, Bennemann et al 2006, 2011, Shibatta & Cheida 2003, Hoffmann et al 2005, Oliveira & Bennemann et al 2005, Jerep et al 2006, Sant'Anna et al 2006, Shibatta et al 2002, 2006a, 2006b, Galves et al 2007, Vieira & Shibatta 2007, Orsi 2010, Raio & Bennemann 2010, Garcia et al 2014, Frantine-Silva et al 2015, Almeida et al 2018, Jerep & Shibatta 2017, Claro-Garcia et al 2018, and to the Cinzas River, with 114 species (Hoffmann et al 2005, Vianna & Nogueira, 2008, Orsi 2010, Bennemann et al 2011, Costa et al 2013, Frantine-Silva et al 2015, Almeida et al 2018.…”

Section: Discussionsupporting

confidence: 63%

“…Fish inventories were carried out in the Paranapanema River tributaries, including the Cinzas, Jaguariaíva and Tibagi rivers (e.g., Shibatta et al 2002, Castro et al 2003, Cetra et al 2012, Cionek et al 2012, Costa et al 2013, Hoffmann et al 2005, Cetra et al 2016, Frantine-Silva et al 2015, Almeida et al 2018, Jerep & Shibatta 2017, Claro-García et al 2018, Frota et al 2020, Jarduli et al 2020. However, a comprehensive checklist of the Laranjinha River ichthyofauna has not been published yet, except for a small streams (e.g., Costa et al 2013), and the scientific knowledge of its fish species remains unknown.…”

Section: Introductionmentioning

confidence: 99%

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Inventory of the fish fauna from Laranjinha River, Paranapanema River system, Brazil

et al. 2020

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This work is the most comprehensive survey of the Laranjinha River´s fishes, a tributary of the Cinzas River, Paranapanema River basin. Throughout its course, there is only a low-height dam, including a transposition system located 98 km from its mouth. The sampling was carried out in nine locations, from the source to the mouth, with six field incursions in each location, using different fishing gear. A total of 11,924 fish were collected, distributed in seven orders, 27 families, and 100 species. The most representative order in the number of species was Siluriformes, followed by Characiformes. As for the families, Loricariidae comprised 21% and Characidae 14% of species richness. Phalloceros harpagos was the species with the highest absolute abundance, representing 11.3% of the total, followed by Hypostomus ancistroides with 9.8%. However, considering the average abundance and frequency of occurrence, Hypostomus ancistroides was the most abundant species, followed by Hypostomus cf. paulinus, Psalidodon aff. paranae and Phalloceros harpagos. Among the collected species, the Apteronotus acidops, Brycon orbygnianus, Brycon nattereri, Crenicichla jupiaensis, and Rhinelepis aspera were classified as endangered on the most recent IUCN Red List. Also, from the total sampled fish, 9.8% are considered non-native species. Among the native species recorded, 10 species are large migratory species, which indicates that the Laranjinha River is a route for spawning and maintenance of species diversity in the middle Paranapanema River. Therefore, the Laranjinha River is a heritage of fish diversity and deserves special attention in its preservation.

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Section: Discussionsupporting

confidence: 63%

Section: Introductionmentioning

confidence: 99%

Inventory of the fish fauna from Laranjinha River, Paranapanema River system, Brazil

et al. 2020

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“…These actions caused the release of species with high invasive risk, which are currently widespread (e.g., O. niloticus, Coptodon rendalli, C. kelberi, S. marginatus, P. squamosissimus). It is not possible to confirm that all 50 species are established in these impoundments (i.e., recruiting), but the presence of early life forms collected in different localities (Almeida et al, 2018) indicate that some are reproducing. Furthermore, non-native species were abundant in most samples, summing relevant fraction or dominating local assemblages.…”

Section: Discussionmentioning

confidence: 93%

Fish diversity in the cascade of reservoirs along the Paranapanema River, southeast Brazil

et al. 2018

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The Paranapanema River is a major tributary of the upper Paraná river basin. Eleven hydropower dams regulate its main course, but no study has investigated fish diversity in these impoundments at the basin-scale. The present study investigated spatial patterns of richness, composition, and abundance of native (non-migratory and migratory) and non-native fishes in the cascade of reservoirs along the Paranapanema River. The study is based on data collected from 34 independent studies conducted in nine reservoirs (47 samples). The compilation recorded 161 species, being 111 native (14 migratory) and 50 non-native. Total richness ranged between 56 and 112 species/reservoir, with a mean of 72 (49.9 non-migratory, 8.1 migratory and 14 non-native). The number of non-migratory species showed no spatial trend along the cascade system, but migratory and non-native richness increased toward downstream reaches. We also observed spatial variation in species composition along the cascade system, but some non-native fishes were widely distributed. Migratory fishes showed low relative abundance (usually < 10%), while non-native species were common and more abundant, especially in reservoirs downstream. Our results revealed a high diversity of fishes in the cascade of impoundments, but indicated that migratory fishes are rare, while non-native species are common or dominant.

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“…Molecular data, and especially DNA barcoding, have been recognized as a powerful and simple tool for identifying and monitoring nonindigenous species (Comtet et al, 2015;Darling & Blum, 2007;Hebert et al, 2003;Rius et al, 2015), including fishes (Almeida et al, 2018;Barman et al, 2018;Collins et al, 2013). In this sense, molecular data has not only been used for early detection of such species (Almeida et al, 2018;Comtet et al, 2015) but also to provide crucial insights into their patterns of introduction (Comtet et al, 2015;Rius et al, 2015). Although there is some molecular data available on O. punctatus inside its native region, to date there are no sequences available for the species in its introduced range.…”

mentioning

confidence: 99%

First genetic record of the non‐native muzzled blenny Omobranchus punctatus (Teleostei: Blenniidae) in the Atlantic Coast of Central and South America

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Lasso-Alcalá²,

Xavier

et al. 2020

Journal of Fish Biology

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DNA barcoding as a useful tool for identifying non-native species of freshwater ichthyoplankton in the neotropics

Cited by 17 publications

References 36 publications

Inventory of the fish fauna from Laranjinha River, Paranapanema River system, Brazil

Inventory of the fish fauna from Laranjinha River, Paranapanema River system, Brazil

Fish diversity in the cascade of reservoirs along the Paranapanema River, southeast Brazil

First genetic record of the non‐native muzzled blenny Omobranchus punctatus (Teleostei: Blenniidae) in the Atlantic Coast of Central and South America

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