Abstract

Artificial impoundments are frequently built to mitigate the water scarcity in the drylands such as the Caatinga region in Brazil. The São Francisco Interbasin Water Transfer (SF-IWT) megaproject implemented many artificial reservoirs for that purpose. A checklist of fish species from the SF-IWT reservoirs is provided based on samples from eight years of monitoring. The collections were conducted semiannually at 28 reservoirs divided into three groups: the East Axis, North Axis, and Agreste Branch. The SF-IWT reservoirs presented a total of 47 species, 46 were recorded in the North Axis, 27 in the East Axis, and only seven in the Agreste Branch. Characids and cichlids represented most of the species. The three analyzed groups of reservoirs presented distinct communities and the reservoirs’ age, richness and abundance were relevant variables responsible for fish composition. The SF-IWT reservoirs present a diverse and heterogeneous ichthyofauna, typical of lentic environments. The main colonizers of the SF-IWT reservoirs were fish from the São Francisco donor basin, invasive species anthropically released in those sites, and eventual species from the surrounding receiving basins. As the accumulation curves suggested, a continuous effort could reveal additional species, patterns in long-term colonization, and contribute to data on the reservoirs’ future stabilization phase. Since invasive species were present in most reservoirs, along with donor-basin native species with potential to disperse to the receiving basins, a continuous and detailed monitoring is key for management planning and possible impacts assessment.

Keywords
Artificial reservoirs; Brazilian Semiarid; non-native fish; water diversion

Resumo

Barramentos artificiais são comumente construídos para mitigar a escassez hídrica em áreas semiáridas como a região da Caatinga brasileira. O Projeto de Integração do Rio São Francisco (PISF) com Bacias Hidrográficas do Nordeste Setentrional implementou muitos reservatórios artificiais com este propósito. Uma lista de espécies de peixes dos reservatórios do PISF foi obtida após amostragens realizadas em oito anos de monitoramento. As campanhas foram realizadas semestralmente em 28 reservatórios divididos em três grupos: Eixo Leste, Eixo Norte e Ramal do Agreste. Os reservatórios amostrados apresentaram um total de 47 espécies, 46 delas foram registradas no Eixo Norte, 27 no Eixo Leste e apenas sete no Ramal do Agreste. Characidae e Cichlidae foram as famílias mais representativas. Os três grupos de reservatórios analisados apresentaram comunidades distintas e a idade, a riqueza e a abundância de cada reservatório foram as variáveis que mais influenciaram a composição das espécies de peixes. Os reservatórios do PISF apresentaram uma ictiofauna diversa e heterogênea, característica de ambientes lênticos. Os principais colonizadores dos reservatórios do PISF foram peixes da bacia doadora do São Francisco, espécies invasoras antropicamente liberadas nesses locais e eventuais espécies das bacias receptoras do entorno. De acordo com o resultado das curvas de acúmulo, um esforço contínuo poderia revelar espécies adicionais, padrões na colonização em longo prazo e contribuir com dados para a fase futura de estabilização dos reservatórios. Visto que espécies invasoras estiveram presentes em quase todos os reservatórios, juntamente com espécies nativas da bacia doadora com potencial de dispersão para as bacias receptoras, um monitoramento continuo e detalhado é essencial para o planejamento de manejo e avaliação de impactos.

Palavras-chave
Desvio de águas; Peixes não-nativos; Reservatórios artificiais; Semiárido brasileiro

Introduction

The Semiarid Northeast region of Brazil, dominated by the Caatinga biome, has very low precipitation ranging from 200 mm to 800 mm annually, with short rainy periods of two to four months (January to April), and a long dry period (generally from May to December) (Maltchik 1999MALTCHIK, L. 1999. Ecologia de rios intermitentes tropicais. In Perspectivas da limnologia no Brasil (M.L.M. Pompêo, ed.). Gráfica e Editora União, São Luís, p.77–89.). The average annual temperature ranges from 25 to 30° C, with the maximum reaching almost 40° C in hotter months (September to November). These two distinct seasons in the Caatinga, wet and dry with extremely low precipitation, are responsible for the great number of intermittent rivers (Maltchik & Florín 2002MALTCHIK, L. & FLORÍN, M. 2002. Perspectives of hydrological disturbance as the driving force of Brazilian semiarid stream ecosystems. Acta Limnol. Bras. 14(3):35–41.). The deficit in the hydric balance has a major socioeconomic impact in semi-arid regions, leaning policymakers to focus on solutions that minimize social issues and meet economic needs. The implementation of artificial man-made reservoirs is reported as a commonly used way to mitigate the water scarcity in dry regions, supplying water for both economic (e.g., irrigation, agriculture, industry) and domestic use (Thornton & Rast 1993THORNTON, J.A. & RAST, W. 1993. A test of hypotheses relating to the comparative limnology and assessment of eutrophication in semi-arid man-made lakes. In Comparative Reservoir Limnology and Water Quality Management (M. Straškraba, J.G. Tundisi & A. Duncan, eds.). Springer, Dordrecht, p.1–24. https://doi.org/10.1007/978-94-017-1096-1_1
https://doi.org/10.1007/978-94-017-1096-... ).

In the Brazilian semi-arid, the São Francisco Interbasin Water Transfer (SF-IWT) project was the governmental solution to mitigate centuries of water scarcity (Andrade et al. 2011ANDRADE, J.G.P., BARBOSA, P.S.F., SOUZA, L.C.A. & MAKINO, D.L. 2011. Interbasin water transfers: the Brazilian experience and international case comparisons. Water Resour. Manag. 25(8):1915–1934. https://doi.org/10.1007/978-94-024-2080-7_10
https://doi.org/10.1007/978-94-024-2080-... ). The São Francisco River, the largest exclusively Brazilian river, is the main naturally perennial water resource in the Semiarid Caatinga domain (Andrade et al. 2011ANDRADE, J.G.P., BARBOSA, P.S.F., SOUZA, L.C.A. & MAKINO, D.L. 2011. Interbasin water transfers: the Brazilian experience and international case comparisons. Water Resour. Manag. 25(8):1915–1934. https://doi.org/10.1007/978-94-024-2080-7_10
https://doi.org/10.1007/978-94-024-2080-... , Roman 2017ROMAN, P. 2017. The São Francisco Interbasin Water Transfer in Brazil: tribulations of a megaproject through constraints and controversy. Water Altern. 10(2):395–419.) and, therefore, the groundwork for the SF-IWT. The SF-IWT megaproject consists of 477 km of canals, pipes, aqueducts, pump stations, and reservoirs divided into two main axes: East (EA) and North (NA) (Andrade et al. 2011ANDRADE, J.G.P., BARBOSA, P.S.F., SOUZA, L.C.A. & MAKINO, D.L. 2011. Interbasin water transfers: the Brazilian experience and international case comparisons. Water Resour. Manag. 25(8):1915–1934. https://doi.org/10.1007/978-94-024-2080-7_10
https://doi.org/10.1007/978-94-024-2080-... ), diverting water from the donor basin (São Francisco) to eight different receiving basins. By August 2022, 12 of the SF-IWT artificial reservoirs along the EA and 14 along the NA were fully operational. Moreover, the EA sub-division, the Agreste branch (AB), possesses two more fully operational reservoirs. The EA axis provides water to the receiving basins of the Paraíba do Norte, Moxotó, and Pajeú rivers, and its AB to the Ipojuca River basin, located in a region known as “Agreste”. Meanwhile, the NA axis supplies water to receiving basins of the Jaguaribe, Apodi-Mossoró, Piranhas-Açu, and Brígida rivers (Andrade et al. 2011ANDRADE, J.G.P., BARBOSA, P.S.F., SOUZA, L.C.A. & MAKINO, D.L. 2011. Interbasin water transfers: the Brazilian experience and international case comparisons. Water Resour. Manag. 25(8):1915–1934. https://doi.org/10.1007/978-94-024-2080-7_10
https://doi.org/10.1007/978-94-024-2080-... ).

The SF-IWT reservoirs are artificially regulated, receiving water from the perennial Sao Francisco River according to management demands, not following the natural seasonal variation affected by the longer dry and shorter rainy periods. Furthermore, due to these man-regulated dynamics, the SF-IWT reservoirs present distinctive features from other semi-arid reservoirs (Barbosa et al. 2012BARBOSA, J.E.L., MEDEIROS, E.S.F., BRASIL, J., CORDEIRO, R.D.S., CRISPIM, M.C.B. & SILVA, G.H.G.D. 2012. Aquatic systems in semi-arid Brazil: limnology and management. Acta Limnol. Bras. 24(1):103–118. http://dx.doi.org/10.1590/S2179-975X2012005000030
https://doi.org/10.1590/S2179-975X201200... , Barbosa et al. 2021BARBOSA, J.E.L., SEVERIANO, J.S., CAVALCANTE, H., LUCENA-SILVA, D., MENDES, C.F., BARBOSA, V.V., SILVA, R.D.S., OLIVEIRA, D.A. & MOLOZZI, J. 2021. Impacts of Interbasin water transfer on the water quality of receiving reservoirs in a tropical semi-arid region. Hydrobiologia. 848:651–673. http://doi.org/10.1007/s10750-020-04471-z
https://doi.org/10.1007/s10750-020-04471... ). For the same reason, the fish fauna in the SF-IWT reservoirs is directly affected by the water management dynamics. Silva et al. (2020)SILVA, M.J., RAMOS, T.P.A., CARVALHO, F.R., BRITO, M.F.G., RAMOS, R.T.C., ROSA, R.S., SÁNCHEZ-BOTERO, J.I., NOVAES, J.L.C., COSTA, R.S. & LIMA, S.M.Q. 2020. Freshwater fish richness baseline from the São Francisco Interbasin Water Transfer Project in the Brazilian Semiarid. Neotrop. Ichthyol. 18(4):e200063. https://doi.org/10.1590/1982-0224-2020-0063
https://doi.org/10.1590/1982-0224-2020-0... compiled information on the ichthyofauna of five basins surrounding the SF-IWT, generating a comprehensive baseline of that Semiarid region previous to the project’s full implementation. Meanwhile, Silva et al. (2023)SILVA, A.L.B., GALVÃO, G.A., ROCHA, A.A.F., GUTIERRE, S.M.M., SANTOS, G.R., COSTA, B.D.F., PEREIRA, L.C.M. & NICOLA, P.A. 2023. Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project. Neotrop. Ichthyol. 21(1):e220016. https://doi.org/10.1590/1982-0224-2022-0016
https://doi.org/10.1590/1982-0224-2022-0... analyzed the fish fauna that is dispersing through the SF-IWT East Axis reaching the Paraíba do Norte River receiving basin after ten years of water diversion. Nonetheless, previous studies did not discuss the fish taxonomic composition of artificially created SF-IWT reservoirs. Thus, this work aimed to provide a list of fish species recorded in the 28 SF-IWT artificial reservoirs, and the results represent important insights on the changes in the fish community composition that occurred over the eight years of monitoring.

Material and Methods

Sampling area

Field campaigns were conducted twice a year, from 2015 to 2022, in 12 reservoirs of the SF-IWT East Axis (EA), 14 reservoirs in the North Axis (NA), and two reservoirs in its Agreste branch (AB) (Figure 1). All the reservoirs on the East Axis and the Agreste Branch, in addition to six reservoirs on the North Axis are located in the state of Pernambuco, Brazil; five reservoirs of the North Axis are located in the state of Ceará, and three in the state of Paraíba, Brazil. Despite being a sub-section of the EA, the AB was separately considered since it diverts the SF-IWT waters to the Ipojuca River basin, while EA diverts to the Paraíba do Norte River basin. The branch is also located in a unique region of the Caatinga, the Agreste, a transition area between the forest (humid sub-region with tropical vegetation) and the semiarid (a dry sub-region with semi-arid vegetation) (CONDEPE 2005CONDEPE. 2005. Bacia Hidrográfica do rio Ipojuca: Série Bacias Hidrográficas de Pernambuco. Governo do Estado de Pernambuco, Secretaria de Planejamento, Agência Estadual de Planejamento e Pesquisas de Pernambuco. 64 p.).

Figure 1.
Study area showing the 28 São Francisco Interbasin Water Transfer reservoirs, the São Francisco River, and the basins surrounding the transposition project.

Sampling effort

A three-days-sampling effort was conducted for each analyzed reservoir. Each three-days-sampling corresponded to one campaign. Campaign numbers varied for each sampling site since the reservoirs presented different filling dates (Table 1), according to the SF-IWT construction progress. Fish were caught using trawls (10 m long, 5 mm mesh), sieves (50 cm diameter, 5 mm mesh), cast nets (mesh sizes of 15 and 30 mm between opposite knots), and hand nets (40 cm/side rectangular base, 5 mm mesh), with at least three attempts per sampling-day for each of those methods. Gill nets (10 or 50 m long with mesh sizes of 20, 30, 40, 50, 60, and 80 mm between adjacent knots) were kept for one sampling-night (12–14 hours) at each site. In eventual encounters with fisherman during sampling, we registered the species collected by them and added to our data as one record (one specimen per species).

Processing of collected specimens

Captured fish were promptly identified and released. When identification was not possible in the field, specimens were euthanized by overexposure to 1 g/mL clove oil (based on MCTI – CONCEA 2018), fixed in a 10% formaldehyde solution, preserved in 70° GL alcohol, and transported to be identified in the Laboratório de Ictiologia (CEMAFAUNA, Universidade Federal do Vale do São Francisco – UNIVASF). Voucher specimens were deposited in the Ichthyological Collection of the Museu de Fauna da Caatinga (MFCI), UNIVASF, Petrolina, Brazil. The material was registered in the SisGen (Sistema Nacional de Gestão do Patrimônio Genético e do Conhecimento Tradicional Associado) system, under the license number A8EC2B0. Fish species were identified according to identification keys provided by Britski et al. (1988)BRITSKI, H.A., SATO, Y. & ROSA, A.B.S. 1988. Manual de identificação de peixes da região de Três Marias: com chave de identificação para os peixes da Bacia do Rio São Francisco. CODEVASF, Brasília. and Ramos et al. (2018)RAMOS, T.P.A., LIMA, J.A.D.S., COSTA, S.Y.L., SILVA, M.J.D. & AVELLAR, R.D.C. 2018. Continental ichthyofauna from the Paraíba do Norte River basin pre-transposition of the São Francisco River, Northeastern Brazil. Biota Neotropica. 18(4): e20170471. https://doi.org/10.1590/1676-0611-bn-2017-0471 (last access in 03/03/2023)
https://doi.org/10.1590/1676-0611-bn-201... , original species descriptions, and complemented by reviews of some taxonomic groups. The nomenclature and systematic classification of species were based on Betancur-R et al. (2017)BETANCUR-R, R., WILEY, E.O., ARRATIA, G., ACERO, A., BAILLY, N., MIYA, M., LECOINTRE, G. & ORTI, G. 2017. Phylogenetic classification of bony fishes. BMC Evol. Biol. 17(1):1–40. https://doi.org/10.1186/s12862-017-0958-3
https://doi.org/10.1186/s12862-017-0958-... and Fricke et al. (2023)FRICKE, R., ESCHMEYER, W.N. & VAN DER LAAN, R. 2023. Eschemeyer’s Catalog of Fishes: Genera, Species, References. http://researcharchive.calacademy.org/research/ichthyology/catalog/fishcatmain.asp (last access in 03/03/2023)
http://researcharchive.calacademy.org/re... .

Data analysis

The richness extrapolation estimator (Chao, 2005CHAO, A., CHAZDON, R.L., COLWELL, R.K. & SHEN, T.J. 2005. A new statistical approach for assessing similarity of species composition with incidence and abundance data. Ecol. Lett. 8(2):148–159. https://doi.org/10.1111/j.1461-0248.2004.00707.x
https://doi.org/10.1111/j.1461-0248.2004... ) was calculated and the generated accumulation curve (EstimateS v9.1.0) was used to demonstrate the fish sampling efficiency. We used Chao1 and Chao2 estimators combined to verify whether the estimates were dependent on sample size or stabilized towards the full sampling. The reservoirs’ age (months since filling date), each axis or branch (East, North, Agreste), fish abundance, and richness were used as explanatory variables to assess the relevance of the independent variables (reservoirs). The most suitable model was generated using an ordistep information criterion. The ordistep builds a forward model so that it maximizes the adjusted R2 at every step, and stops when the adjusted R2 starts to decrease, the scope is exceeded, or the selected permutation P-value is exceeded (Blanchet et al. 2008BLANCHET, F.G., LEGENDRE, P. & BORCARD, D. 2008. Forward selection of explanatory variables. Ecology. 89(9):2623–2632. https://doi.org/10.1890/07-0986.1
https://doi.org/10.1890/07-0986.1... ). The model analysis is used to identify predictor variables that significantly explain the patterns observed in the fish assemblage. Furthermore, a db-RDA (Distance-based Redundancy Analysis) was performed to visualize dbLM data, and a PERMANOVA based on the similarity matrix obtained by Euclidean distance, with 999 permutations, helped determine the significance of explanatory variables. Statistical analysis, other than richness estimators, was performed using R software (R Core Team, 2020). The functions used were from package Vegan (Oksanen et al. 2013OKSANEN, J., BLANCHET, F.G., KINDT, R., LEGENDRE, P., MINCHIN, P.R., O’HARA, R.B., SIMPSON, G.L., SOLYMOS, P., STEVENS, M.H.H. & WAGNER, H. 2013. Package ‘vegan’. Community Ecology Package. 2(9):1–295.). Plots were made using the package ggplot2 (Wickham, 2006).

Results

A total of 70,522 individuals representing 47 fish species (Figures 2 and 3) from 18 families, and seven orders were registered (Table 2). The North Axis (NA) presented 46 species, 27 species were registered in the East Axis (EA), and seven in the Agreste Branch (AB). There was one exclusive species from the AB reservoirs (Parotocinclus jumbo Britski & Garavello, 2002), and 20 species were only registered in the NA reservoirs (see Table 2). Anchoviella vaillanti (Steindachner, 1908), Astyanax lacustris (Lütken, 1875), Oreochromis niloticus (Linnaeus, 1758), and Poecilia reticulata Peters, 1859 were the only common species to all three analyzed groups of reservoirs (Figures 2 and 3). The richest order was Characiformes (59.5%; n = 28), followed by Cichliformes (14.9%; n = 7), and Siluriformes (10.6%; n = 5). The fish families with greater species richness were Characidae (25.5%; n = 12), and Cichlidae (14.8%; n = 7). Eight fish were considered non-native to the Caatinga domain, while eight are endemic in the region (Table 2).

Figure 2.
Clupeiformes and Characiformes collected in in the São Francisco Interbasin Water Transfer reservoirs: a. Anchoviella vaillanti, b. Hoplias gr. malabaricus, c. Metynnis lippincottianus, d. Myleus micans, e. Pygocentrus piraya, f. Serrasalmus brandtii, g. Leporinus piau, h. Leporinus taeniatus, i. Megaleporinus obtusidens, j. Schizodon knerii, k. Steindachnerina elegans, l. Steindachnerina notonota, m. Prochilodus brevis, n. Triportheus guentheri, o. Bryconops aff. affinis, p. Acestrorhynchus britskii, q. Acestrorhynchus lacustris, r. Astyanax lacustris, s. Compsura heterura, t. Hemigrammus brevis, u. Hemigrammus marginatus, v. Moenkhausia costae, w. Phenacogaster franciscoensis, x. Psalidodon fasciatus, y. Psellogrammus kennedyi, z. Roeboides xenodon, a1. Serrapinnus heterodon, and b1. Serrapinnus piaba. Scale bar = 1 cm.

Figure 3.
Gymnotiformes, Siluriformes, Cichliformes, Cyprinodontiformes, and Acanthuriformes collected in the São Francisco Interbasin Water Transfer reservoirs: a. Sternopygus macrurus, b. Hoplosternum littorale, c. Hypostomus pusarum, d. Parotocinclus jumbo, e. Trachelyopterus galeatus, f. Pimelodus maculatus, g. Cichla monoculus, h. Cichla temensis, i. Cichlasoma orientale, j. Cichlasoma sanctifranciscense, k. Saxatilia brasiliensis, l. Oreochromis niloticus, m. Parachromis managuensis, n. Poecilia hollandi, o. Poecilia reticulata, p. Poecilia vivipara, q. Pachyurus francisci, and r. Plagioscion squamosissimus. Scale bar = 1 cm.

The most abundant species in the EA reservoirs were As. lacustris (30%), A. vaillanti (27%), M. costae (14%), and O. niloticus (8%). In NA reservoirs, the predominant species were As. lacustris (34%), A. vaillanti (22%), and Hemigrammus marginatus (9%). Meanwhile, in AB the species with the largest number of individuals were O. niloticus (47%), As. lacustris (22%), and Parachromis managuensis (17%). In general, the most predominant species were As. lacustris (32%), A. vaillanti (24%), and M. costae (8%) (Figures 2 and Figure 3). During the first years of sampling in the reservoirs, the same species were recurrent recorded in most of them: A. vaillanti, As. lacustris, H. malabaricus, M. costae, and O. niloticus (Supplementary File S1).

Data suggests that increasing the sampling effort would result in collecting additional species since the species accumulation curves did not present a tendency to stabilize, except for the Agreste Branch (Figure 4). The richness estimators indicated that the East Axis would present additional six species (observed n = 27), and seven in the North Axis (observed n = 46).

Figure 4.
Species accumulation curve with expected number of species – S(est) – and the richness extrapolation estimators Chao 1 (abundance-based data) and Chao 2 (incidence-based data). Sample collections made in the three group of reservoirs from the São Francisco Interbasin Water Transfer project: East Axis, North Axis, Agreste Branch.

The forward selection model applied to fish assemblage (abundance, richness) and reservoir (age, location) characteristics (Figure 1, Table 1) identified richness, abundance, age, and location (Axis) as good predictors (Table 3). The first db-RDA axis (CAP 33.1%) distinguished reservoirs location and age (Figure 5). The second db-RDA axis was related to reservoir richness and abundance, explaining 16.5% of the variation in fish composition. Areias (EA) and Tucutu (NA) reservoirs are represented in the farther left of CAP1 since those were the reservoirs most influenced by richness and abundance.

Figure 5.
Ordination of 28 reservoirs in the São Francisco Interbasin Water Transfer project according to the distance-based redundancy analysis (db-RDA), with the effect of reservoir age on fish assemblages. Represented species are the most strongly related to the ordination axes: R2 > 0.5.

Discussion

The São Francisco Interbasin Water Transfer artificial reservoirs presented 47 fish species, the great majority represented in the North Axis, about half of them were presented in the East Axis, and only seven were found in the Agreste Branch. Characids and cichlids represented most of the reported species. The three analyzed groups of reservoirs presented distinct fish compositions, however, AB shared most species with both axes. The reservoirs’ richness, abundance, and age were relevant variables responsible for fish composition, separating axes and species groups. The species that first colonized the reservoirs and recurrently occurred in fist years of sampling, considered as pioneer species, were: A. vaillanti, As. lacustris, O. niloticus, M. costae, and H. malabaricus.

All the SF-IWT reservoirs are less than ten years old, still in the colonization formation stage (Agostinho et al. 1999AGOSTINHO, A.A., MIRANDA, L.E., BINI, L.M., GOMES, L.C., THOMAZ, S.M. & SUZUKI, H.I. 1999. Patterns of colonization in Neotropical reservoirs and prognoses on aging. In Theoretical reservoir ecology and its applications (J.G. Tundisi & M. Straskraba, eds.). Backhuys Publishers, Leiden, p.227–265.). The instability of reservoir conditions can last 5 to 30 years after its formation, with fish community stabilization estimated to happen between 15 and 40 years (Agostinho et al. 1999AGOSTINHO, A.A., MIRANDA, L.E., BINI, L.M., GOMES, L.C., THOMAZ, S.M. & SUZUKI, H.I. 1999. Patterns of colonization in Neotropical reservoirs and prognoses on aging. In Theoretical reservoir ecology and its applications (J.G. Tundisi & M. Straskraba, eds.). Backhuys Publishers, Leiden, p.227–265., Agostinho et al. 2016AGOSTINHO, A.A., GOMES, L.C., SANTOS, N.C.L., ORTEGA, J.C.G. & PELICICE, F.M. 2016. Fish assemblages in Neotropical reservoirs: Colonization patterns, impacts and management. Fish. Res. 173:26–36. https://doi.org/10.1016/j.fishres.2015.04.006
https://doi.org/10.1016/j.fishres.2015.0... ). The richness observed in each SF-IWT reservoirs was at maximum of 29 species, which is close to the average richness of n = 30 found in most Neotropical reservoirs (Agostinho et al. 2007AGOSTINHO, A.A., GOMES, L.C. & PELICICE, F.M. 2007. Ecologia e manejo de recursos pesqueiros em reservatórios do Brasil. EDUEM, Maringá.). In general, small diversity and richness are expected for Neotropical impounded areas (Agostinho et al. 2007AGOSTINHO, A.A., GOMES, L.C. & PELICICE, F.M. 2007. Ecologia e manejo de recursos pesqueiros em reservatórios do Brasil. EDUEM, Maringá., Agostinho et al. 2016AGOSTINHO, A.A., GOMES, L.C., SANTOS, N.C.L., ORTEGA, J.C.G. & PELICICE, F.M. 2016. Fish assemblages in Neotropical reservoirs: Colonization patterns, impacts and management. Fish. Res. 173:26–36. https://doi.org/10.1016/j.fishres.2015.04.006
https://doi.org/10.1016/j.fishres.2015.0... ), especially new ones such as SF-IWT reservoirs. We observed a positive correlation between age and richness. Reservoirs were as richer as they were older. However, despite those observed peaks of richness in the colonization phase of the reservoirs, it is expected that after reaching the stabilization phase, reservoirs older than 20 years present lower richness than the younger ones (Agostinho et al. 2007AGOSTINHO, A.A., GOMES, L.C. & PELICICE, F.M. 2007. Ecologia e manejo de recursos pesqueiros em reservatórios do Brasil. EDUEM, Maringá.). Those richness variations are the consequence of several variables such as the reservoir location, distance from the species matrix (rivers), impoundment area, and anthropogenic activities in and around the reservoirs.

Besides age, the reservoirs’ location has influenced the fish composition in SF-IWT reservoirs. The main species matrix (São Francisco River), has its water pumped through all SF-IWT canals and reservoirs, serving as a major species pool. However, the East and North Axes reservoirs are surrounded by other basins along their path: the Moxotó, and Pajeú (São Francisco) sub-basins surrounding EA, Ipojuca basin surrounding AB, and the Brígida (São Francisco) sub-basin, Jaguaribe, Apodi-Mossoró, and Piranhas-Açu basins surrounding the NA. The EA had all of its native species originating from the São Francisco River (Silva et al. 2023SILVA, A.L.B., GALVÃO, G.A., ROCHA, A.A.F., GUTIERRE, S.M.M., SANTOS, G.R., COSTA, B.D.F., PEREIRA, L.C.M. & NICOLA, P.A. 2023. Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project. Neotrop. Ichthyol. 21(1):e220016. https://doi.org/10.1590/1982-0224-2022-0016
https://doi.org/10.1590/1982-0224-2022-0... ) since its surrounding basins are mainly subsections of the São Francisco and not independent basins, as seen for the NA. Meanwhile, the four different basins surrounding the NA together with the São Francisco basin, supplied the NA reservoirs with a larger number of species, many exclusive, when compared to the EA. Moreover, the NA catchment is located in a lotic portion of the São Francisco River, which is naturally richer compared to the lentic reservoir catchment of EA. These watershed species matrixes helped determine the distinction in fish assemblage between regions.

The most abundant species were As. lacustris, A. vaillanti, C. monoculus, H. marginatus, H. brevis, H. gracilis, M. costae, O. niloticus, and P. vivipara. Following a pattern described in the literature for the Neotropical region, there was a prevalence of specimens from the Characidae family (As. lacustris, M. costae and Hemigrammus spp.), characterized by small-sized sedentary species, with generalist habit, high tolerance, and efficient reproductive strategies (opportunistic sensuWinemiller 1989WINEMILLER, K.O. 1989. Patterns of variation in life history among South American fishes in seasonal environments. Oecologia. 81:225–241. https://doi.org/10.1007/BF00379810
https://doi.org/10.1007/BF00379810... , Agostinho et al. 1999AGOSTINHO, A.A., MIRANDA, L.E., BINI, L.M., GOMES, L.C., THOMAZ, S.M. & SUZUKI, H.I. 1999. Patterns of colonization in Neotropical reservoirs and prognoses on aging. In Theoretical reservoir ecology and its applications (J.G. Tundisi & M. Straskraba, eds.). Backhuys Publishers, Leiden, p.227–265., Agostinho et al. 2007AGOSTINHO, A.A., GOMES, L.C. & PELICICE, F.M. 2007. Ecologia e manejo de recursos pesqueiros em reservatórios do Brasil. EDUEM, Maringá., Dagosta & De Pinna 2019DAGOSTA, F.C.P. & DE PINNA, M. 2019. The Fishes of the Amazon: Distribution and Biogeographical Patterns, with a Comprehensive List of Species. B. Am. Mus. Nat. Hist. 431:1–163. https://doi.org/10.1206/0003-0090.431.1.1
https://doi.org/10.1206/0003-0090.431.1.... ). The second most abundant species was the anchovy A. vaillanti. The species demonstrated a great colonization capacity, with fast establishment and spread through all reservoirs. Anchoviella vaillanti successful residence in SF-IWT reservoirs can be explained by the species efficient trophic and reproductive strategies (Silva et al. 2023SILVA, A.L.B., GALVÃO, G.A., ROCHA, A.A.F., GUTIERRE, S.M.M., SANTOS, G.R., COSTA, B.D.F., PEREIRA, L.C.M. & NICOLA, P.A. 2023. Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project. Neotrop. Ichthyol. 21(1):e220016. https://doi.org/10.1590/1982-0224-2022-0016
https://doi.org/10.1590/1982-0224-2022-0... ). The other prevalent group, Cichlidae was represented by the non-natives: O. niloticus and Cichla spp. Cichlids in general present great reproductive, feeding, and abiotic plasticity, as well as high adaptability to lentic environments (Agostinho et al. 2021AGOSTINHO, A.A., ORTEGA, J.C.G., BAILLY, D., GRAÇA, W.J., PELICICE, F.M. & JÚLIO, H.F. 2021. Introduced Cichlids in the Americas: distribution patterns, invasion ecology and impacts. In The behavior, ecology and evolution of Cichlid fishes (M.E. Abate & D.L. Noakes, eds.). Fish Fish. 40:313–361. https://doi.org/10.1007/978-94-024-2080-7_10
https://doi.org/10.1007/978-94-024-2080-... ), being already widely dispersed in many Caatinga-region reservoirs (Costa et al. 2017COSTA, S.Y.L., BARBOSA, J.E.D.L., VIANA, L.G. & RAMOS, T.P.A. 2017. Composition of the ichthyofauna in Brazilian semiarid reservoirs. Biota Neotropica. 17(3): e20170334. http://dx.doi.org/10.1590/1676-0611-BN-2017-0334 (last access on 03/03/2023)
https://doi.org/10.1590/1676-0611-BN-201... , Silva et al. 2020SILVA, M.J., RAMOS, T.P.A., CARVALHO, F.R., BRITO, M.F.G., RAMOS, R.T.C., ROSA, R.S., SÁNCHEZ-BOTERO, J.I., NOVAES, J.L.C., COSTA, R.S. & LIMA, S.M.Q. 2020. Freshwater fish richness baseline from the São Francisco Interbasin Water Transfer Project in the Brazilian Semiarid. Neotrop. Ichthyol. 18(4):e200063. https://doi.org/10.1590/1982-0224-2020-0063
https://doi.org/10.1590/1982-0224-2020-0... , Silva et al. 2023SILVA, A.L.B., GALVÃO, G.A., ROCHA, A.A.F., GUTIERRE, S.M.M., SANTOS, G.R., COSTA, B.D.F., PEREIRA, L.C.M. & NICOLA, P.A. 2023. Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project. Neotrop. Ichthyol. 21(1):e220016. https://doi.org/10.1590/1982-0224-2022-0016
https://doi.org/10.1590/1982-0224-2022-0... ).

Reservoirs assemblages are supposed to be similar to the surrounding basins (Rahel 2007). However, constant man-mediated non-native fish releases in reservoirs cause biotic differentiations (Daga et al. 2015DAGA, V.S., SKÓRA, F., PADIAL, A.A., ABILHOA, V., GUBIANI, E. A. & VITULE, J.R.S. 2015. Homogenization dynamics of the fish assemblages in Neotropical reservoirs: comparing the roles of introduced species and their vectors. Hydrobiologia. 746:327–347. https://doi.org/10.1007/s10750-014-2032-0
https://doi.org/10.1007/s10750-014-2032-... ). The ichthyofauna of the SF-IWT reservoirs was composed mainly by species native to the Caatinga domain, except for the non-natives: O. niloticus, P. managuensis, C. monoculus, C. temensis, H. littorale, P. reticulata, M. lippincottianus, and P. squamosissimus. This is a small but yet very common group of species, constantly released in the Northeast Brazilian reservoirs (for commercial or recreative purposes), that are widely spread in most of the Caatinga domain basins, considered well-established invasive species in the region (Leão et al. 2011LEÃO, T.C.C., ALMEIDA, W.R., DECHOUM, M.S. & ZILLER, S.R. 2011. Espécies exóticas invasoras no Nordeste do Brasil – contextualização, manejo e políticas públicas. CEPAN, Recife., Brito et al. 2020BRITO, M.F.G., DAGA, V.S. & VITULE, J.R.S. 2020. Fisheries and biotic homogenization of freshwater fish in the Brazilian semiarid region. Hydrobiologia. 847:3877–3895. https://doi.org/10.1007/s10750-020-04236-8
https://doi.org/10.1007/s10750-020-04236... , Silva et al. 2020SILVA, M.J., RAMOS, T.P.A., CARVALHO, F.R., BRITO, M.F.G., RAMOS, R.T.C., ROSA, R.S., SÁNCHEZ-BOTERO, J.I., NOVAES, J.L.C., COSTA, R.S. & LIMA, S.M.Q. 2020. Freshwater fish richness baseline from the São Francisco Interbasin Water Transfer Project in the Brazilian Semiarid. Neotrop. Ichthyol. 18(4):e200063. https://doi.org/10.1590/1982-0224-2020-0063
https://doi.org/10.1590/1982-0224-2020-0... , D’Avilla et al. 2021D’AVILLA, T., COSTA-NETO, E.M. & BRITO, M.F.G. 2021. Impacts on fisheries assessed by local ecological knowledge in a reservoir cascade in the lower São Francisco River, northeastern Brazil. Neotrop. Ichthyol. 2021; 19(3):e200156. https://doi.org/10.1590/1982-0224-2020-0156
https://doi.org/10.1590/1982-0224-2020-0... ). These invasives represented more than 12% of the total abundance in our study, compared to endemics that represented just 9%. As pointed by Agostinho et al. (2007)AGOSTINHO, A.A., GOMES, L.C. & PELICICE, F.M. 2007. Ecologia e manejo de recursos pesqueiros em reservatórios do Brasil. EDUEM, Maringá., non-native species are usually more successful in recent reservoirs, such as the SF-IWT reservoirs, mainly due to their resistance and opportunism during environmental disturbances (e.g., reservoir formation), the abundant presence of small preys (e.g., As. lacustris, M. costae, and A. vaillanti), absence of natural predators, and few large competitors present (for Semiarid reservoirs also discussed by Brito et al. 2020BRITO, M.F.G., DAGA, V.S. & VITULE, J.R.S. 2020. Fisheries and biotic homogenization of freshwater fish in the Brazilian semiarid region. Hydrobiologia. 847:3877–3895. https://doi.org/10.1007/s10750-020-04236-8
https://doi.org/10.1007/s10750-020-04236... ). Moreover, the parental care and fractionated-type spawning strategies seen in most of the presented invasives (equilibrium sensuWinemiller 1989WINEMILLER, K.O. 1989. Patterns of variation in life history among South American fishes in seasonal environments. Oecologia. 81:225–241. https://doi.org/10.1007/BF00379810
https://doi.org/10.1007/BF00379810... , Assis et al. 2017ASSIS, D. A. S., DIAS-FILHO, V. A., MAGALHÃES, A. L. B. & BRITO, M. F. G. 2017. Establishment of the non-native fish Metynnis lippincottianus (Cope 1870) (Characiformes: Serrasalmidae) in lower São Francisco River, northeastern Brazil. Stud. Neotrop. Fauna E. 52(3):228–238. https://doi.org/10.1080/01650521.2017.1348057
https://doi.org/10.1080/01650521.2017.13... , Brito et al. 2020BRITO, M.F.G., DAGA, V.S. & VITULE, J.R.S. 2020. Fisheries and biotic homogenization of freshwater fish in the Brazilian semiarid region. Hydrobiologia. 847:3877–3895. https://doi.org/10.1007/s10750-020-04236-8
https://doi.org/10.1007/s10750-020-04236... ), associated with generalist diet, represent major advantages to establishment in reservoirs (Agostinho et al. 2007AGOSTINHO, A.A., GOMES, L.C. & PELICICE, F.M. 2007. Ecologia e manejo de recursos pesqueiros em reservatórios do Brasil. EDUEM, Maringá.). For example, Oreochromis niloticus is well known in the literature for dominating reservoirs, being highly prolific, having high resistance to environmental variations (Canonico et al. 2005, Attayde et al. 2011ATTAYDE, J.L., BRASIL, J. & MENESCAL, A. 2011. Impacts of introducing Nile tilapia on the fisheries of a tropical reservoir in North-Eastern Brazil. Fisheries Manag. Ecol. 18(6):437–443. https://doi.org/10.1111/j.1365-2400.2011.00796.x
https://doi.org/10.1111/j.1365-2400.2011... ), and contributing to the homogenization of species in invaded sites (Canonico et al. 2005, Leão et al. 2011LEÃO, T.C.C., ALMEIDA, W.R., DECHOUM, M.S. & ZILLER, S.R. 2011. Espécies exóticas invasoras no Nordeste do Brasil – contextualização, manejo e políticas públicas. CEPAN, Recife., Vitule & Prodocimo 2012VITULE, J.R.S. & PRODOCIMO, V. 2012. Introdução de espécies não nativas e invasões biológicas. Estud. Biol. 34(83):225–237. https://doi.org/10.7213/estud.biol.7335
https://doi.org/10.7213/estud.biol.7335... , Daga et al. 2015DAGA, V.S., SKÓRA, F., PADIAL, A.A., ABILHOA, V., GUBIANI, E. A. & VITULE, J.R.S. 2015. Homogenization dynamics of the fish assemblages in Neotropical reservoirs: comparing the roles of introduced species and their vectors. Hydrobiologia. 746:327–347. https://doi.org/10.1007/s10750-014-2032-0
https://doi.org/10.1007/s10750-014-2032-... ). Moreover, the dominance of Parachromis managuensis and Cichla spp. in some reservoirs may explain the reduced richness and low abundance of native predators (Pelicice & Agostinho 2009PELICICE, F.M. & AGOSTINHO, A.A. 2009. Fish fauna destruction after the introduction of a non-native predator (Cichla kelberi) in a Neotropical reservoir. Biol. Invasions. 11:1789–1801. https://doi.org/10.1007/s10530-008-9358-3
https://doi.org/10.1007/s10530-008-9358-... ), since the invasive predators can inhibit the natives’ growth and compete for food resources (Carvalho et al. 2014CARVALHO, D.C., OLIVEIRA, D.A.A., SAMPAIO, I. & BEHEREGARAY, L.B. 2014. Analysis of propagule pressure and genetic diversity in the invasibility of a freshwater apex predator: the peacock bass (genus Cichla). Neotrop. Ichthyol. 12(1):105–116. https://doi.org/10.1590/S1679-62252014000100011
https://doi.org/10.1590/S1679-6225201400... , França et al. 2017FRANÇA, E.J., ALMEIDA, C.A.C., ALMEIDA-NETO, M.S., SANTOS, R.E., MAGALHÃES, A.L.B., EL-DEIR, A.C.A. & SEVERI, W. 2017. Novelty on the market, novelty in the environment: The invasion of non-native fish jaguar guapote (Perciformes) in northeastern Brazil. Neotrop. Biol. Conserv. 12(1):12–18. https://doi.org/10.4013/nbc.2017.121.02
https://doi.org/10.4013/nbc.2017.121.02... , Resende et al. 2020RESENDE, A.G.A., FRANÇA, E.J., OLIVEIRA, C.D.L.D. & SANTANA, F.M. 2020. Maturity, growth and natural mortality rate of the introduced fish Parachromis managuensis (Perciformes: Cichlidae) in the semiarid region of Brazil.Acta Limnol. Bras. 32:e29. https://doi.org/10.1590/S2179-975X2820
https://doi.org/10.1590/S2179-975X2820... , Sastraprawira et al. 2020SASTRAPRAWIRA, S.M., RAZAK, I.H.A., SHAHIMI, S., PATI, S., EDINUR, H.A., JOHN, A.B., AHMAD, A., KUMARAN, J.V, MARTIN, M.B., CHONG, J.L., CHOWDHURY, A.J.K. & NELSON, B. R. 2020. A review on introduced Cichla spp. and emerging concerns. Heliyon. 6(11):e05370. https://doi.org/10.1016/j.heliyon.2020.e05370
https://doi.org/10.1016/j.heliyon.2020.e... ). Cichla spp. are also known to succeed in reservoirs due to reproductive strategies, opportunistic feeding behavior, cannibalism of young, and resistance to environmental changes (Gomiero & Braga 2004GOMIERO, L.M. & BRAGA. F.M.S. 2004. Reproduction of species of the genus Cichla in a reservoir in Southeastern Brazil. Braz. J. Biol. 64(3b):613–624. https://doi.org/10.1590/S1519-69842004000400008
https://doi.org/10.1590/S1519-6984200400... , Carvalho et al. 2014CARVALHO, D.C., OLIVEIRA, D.A.A., SAMPAIO, I. & BEHEREGARAY, L.B. 2014. Analysis of propagule pressure and genetic diversity in the invasibility of a freshwater apex predator: the peacock bass (genus Cichla). Neotrop. Ichthyol. 12(1):105–116. https://doi.org/10.1590/S1679-62252014000100011
https://doi.org/10.1590/S1679-6225201400... , D’Avilla et al 2021D’AVILLA, T., COSTA-NETO, E.M. & BRITO, M.F.G. 2021. Impacts on fisheries assessed by local ecological knowledge in a reservoir cascade in the lower São Francisco River, northeastern Brazil. Neotrop. Ichthyol. 2021; 19(3):e200156. https://doi.org/10.1590/1982-0224-2020-0156
https://doi.org/10.1590/1982-0224-2020-0... ).

Although crucial on the socioeconomic perspective, the construction of interconnected artificial reservoirs by SF-IWT project raised a major environmental concern: the dispersal of fish species between historically separated basins (Silva et al. 2020SILVA, M.J., RAMOS, T.P.A., CARVALHO, F.R., BRITO, M.F.G., RAMOS, R.T.C., ROSA, R.S., SÁNCHEZ-BOTERO, J.I., NOVAES, J.L.C., COSTA, R.S. & LIMA, S.M.Q. 2020. Freshwater fish richness baseline from the São Francisco Interbasin Water Transfer Project in the Brazilian Semiarid. Neotrop. Ichthyol. 18(4):e200063. https://doi.org/10.1590/1982-0224-2020-0063
https://doi.org/10.1590/1982-0224-2020-0... ). Some recorded species, despite considered native to the Caatinga domain, are exclusively native or endemic to the donor basin, the São Francisco. Therefore, those São Francisco River species were geographically isolated from the receiving basins before the SF-IWT implementation. The spread and introduction of M. costae e A. vaillanti thought EA reaching the Paraíba do Norte receiving basin was discussed by Ramos et al. (2021) and Silva et al. (2023)SILVA, A.L.B., GALVÃO, G.A., ROCHA, A.A.F., GUTIERRE, S.M.M., SANTOS, G.R., COSTA, B.D.F., PEREIRA, L.C.M. & NICOLA, P.A. 2023. Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project. Neotrop. Ichthyol. 21(1):e220016. https://doi.org/10.1590/1982-0224-2022-0016
https://doi.org/10.1590/1982-0224-2022-0... , however no impact by these species was yet detected. Remarkably, A. vaillanti is also spreading through NA and has already been detected in the Jaguaribe basin (in prep.). We also observed the spread of Cichlasoma sanctifranciscense through all the EA reservoirs and canals over time, and this species was already registered in the Paraíba do Norte basin in April 2023 (in prep.). Meanwhile, reports of Megaleporinus obtusidens in the Paraíba do Norte and Jaguaribe basins are speculated to be accidental, non-related to the SF-IWT, since just one specimen was captured in one reservoir (Tucutu) during all monitoring time, and none along the reservoirs SF-IWT (as seem for C. sanctifranciscense). Other São Francisco basin species that did not reach the receiving basins yet but we detected spreading through NA reservoirs are: Steindachnerina elegans, Bryconops aff. affinis, H. brevis, and Roeboides xenodon. All of those species present efficient life strategies that allow successful spread and colonization in reservoirs (Winemiller 1989WINEMILLER, K.O. 1989. Patterns of variation in life history among South American fishes in seasonal environments. Oecologia. 81:225–241. https://doi.org/10.1007/BF00379810
https://doi.org/10.1007/BF00379810... , Agostinho et al. 1999AGOSTINHO, A.A., MIRANDA, L.E., BINI, L.M., GOMES, L.C., THOMAZ, S.M. & SUZUKI, H.I. 1999. Patterns of colonization in Neotropical reservoirs and prognoses on aging. In Theoretical reservoir ecology and its applications (J.G. Tundisi & M. Straskraba, eds.). Backhuys Publishers, Leiden, p.227–265., Agostinho et al. 2007AGOSTINHO, A.A., GOMES, L.C. & PELICICE, F.M. 2007. Ecologia e manejo de recursos pesqueiros em reservatórios do Brasil. EDUEM, Maringá.). The constant influx of donor-basin-fish-propagules into the SF-IWT reservoirs seems to guarantee a viable propagule number, supporting these opportunistic species to overcome demographic and ecological barriers, determining a successful establishment and spread (Simberloff 2009SIMBERLOFF, D. 2009. The Role of Propagule Pressure in Biological Invasions. Annu. Rev. Ecol. Evol. S. 40:81–102. https://doi.org/10.1146/annurev.ecolsys.110308.120304
https://doi.org/10.1146/annurev.ecolsys.... ).

The balance between socioeconomic and environmental benefits/impacts should be extensively discussed prior to implementation of megaprojects such as the SF-IWT. The SF-IWT reservoirs are artificial impoundments especially built to mitigate the shortage of water in the driest region of Brazil and represented a great change in the Caatinga region, bringing water and species to places that were previously dominated by dry lands and intermittent rivers. Those reservoirs constantly undergo several anthropogenic actions, mainly related to water fluctuation and species introduction. The human-induced changes are dramatic in fish colonization and establishment success (Jia et al. 2020JIA, Y., KENNARD, M., LIU, Y., SUI, X., LI, K., WANG, G. & CHEN, Y. 2020. Human disturbance and long-term changes in fish taxonomic, functional and phylogenetic diversity in the Yellow River, China. Hydrobiologia. 847:3711–3725. https://doi.org/10.1007/s10750-020-04244-8
https://doi.org/10.1007/s10750-020-04244... ). This reinforces the importance of monitoring the reservoirs over time and registering the ichthyofauna development over the years. As the accumulation curves suggested, a continuous effort could reveal additional species, patterns in long-term colonization, and serve as base-data on the reservoirs’ future stabilization phase. Our data indicate that the fish fauna from the São Francisco donor basin are the main colonizers of the SF-IWT-created new environments, along with invasive species deliberately released in those sites, and eventual species from the surrounding receiving basins. Considering the presented potential of SF-IWT system to serve as dispersal bridge from donor to receiving basins, prevention measures are key points to minimize introduction risks. To avoid the translocation of species, we reinforce that the physical and electrical barriers described by Silva et al. (2023)SILVA, A.L.B., GALVÃO, G.A., ROCHA, A.A.F., GUTIERRE, S.M.M., SANTOS, G.R., COSTA, B.D.F., PEREIRA, L.C.M. & NICOLA, P.A. 2023. Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project. Neotrop. Ichthyol. 21(1):e220016. https://doi.org/10.1590/1982-0224-2022-0016
https://doi.org/10.1590/1982-0224-2022-0... should be implemented to mitigate the introduction of new species in the receiving basins. As for species that already reached the previous isolated basins, a continuous and detailed monitoring is essential for management planning and possible impacts assessment.

Acknowledgments

The samples’ collecting permit was provided by the Brazilian Institute of the Environment and Renewable Natural Resources (IBAMA): Authorization for Capture, Collection, and Transport of Biological Material No. 94/2014 and subsequent renewals. We thank the Secretaria Nacional de Segurança Hídrica (SNSH) of Ministério da Integração e do Desenvolvimento Regional (MIDR), the UNIVASF and CEMAFAUNA for the financial support. We also acknowledge researchers of CEMAFAUNA MSc. Karlla Rios and Dr. Paula Batista for providing collaboration, guidance, and logistical support.

Data Availability

The datasets generated during and/or analyzed during the current study are available at: https://doi.org/10.48331/scielodata.ELHXGF and https://sisgen.gov.br/paginas/pubpesqatividade.aspx (Código de Cadastro: A8EC2B0)

References

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