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Valente-Neto F, Dala-Corte RB, Cunico AM, Magalhães ALB, Godoy BS, Leal CG, Castro DMP, Macedo DR, Lima-Junior DP, Gubiani ÉA, Roque FDO, Teresa FB, Oliveira FJM, Becker FG, Brejão GL, Brito J, Zuanon J, Vitule JRS, Dias-Silva K, Casatti L, Lima LB, Montag LFA, Callisto M, Dos Santos MR, Hamada N, Pamplin PAZ, Pompeu PS, Leitão RP, Ruaro R, Couceiro SRM, Abilhoa V, Súarez YR, Martins RT. Cost-effective alternatives to facilitate biomonitoring and bioassessment of neotropical streams. THE SCIENCE OF THE TOTAL ENVIRONMENT 2025; 965:178654. [PMID: 39892239 DOI: 10.1016/j.scitotenv.2025.178654] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/29/2024] [Revised: 01/24/2025] [Accepted: 01/24/2025] [Indexed: 02/03/2025]
Abstract
A reliable response of bioindicators to environmental variation is a cornerstone for effective bioassessment and biomonitoring. Fish and aquatic macroinvertebrates are widely used as bioindicators of different human impacts in freshwater ecosystems, but the cost-effectiveness of their usage can be improved through the use of surrogates. We investigated congruence patterns between using different taxonomic and numeric resolutions for aquatic macroinvertebrates and fish to assess community-environment relationships. We also tested whether dataset characteristics (e.g., area sampled, species pool) could explain the variation in the effectiveness of using different taxonomic and numerical resolutions. We used a Brazilian nationwide database encompassing multiple datasets with a gradient of riparian deforestation each. Our findings suggest that families and genera can effectively represent macroinvertebrate genera and fish species, respectively, when using community matrices for assessing community-environment relationships, with an acceptable loss of information. EPT (Ephemeroptera, Plecoptera, and Trichoptera) and Characiformes or Siluriformes may be used as a surrogate, in some cases, for the entire assemblages of macroinvertebrates and fish, respectively, but their use may result in higher loss of information. Presence-absence data also presented a minimal loss of information compared to abundance data, for both macroinvertebrates and fish. The variation in congruence levels among macroinvertebrate datasets was less predicted by dataset characteristics than fish. Across distinct resolutions, on average, 10 % and 19 % of the variation in community composition of macroinvertebrates and fish, respectively, was explained by broad-scale environmental variables, and the effect size was negatively affected by the dataset's sample size and spatial extent for fish. Whereas identification at species (fish) and genus (macroinvertebrates) level and quantification of all individuals still provide the best scenario, we provide evidence that coarser taxonomical resolution and presence-absence data can be used as cost-effective alternatives to facilitate biomonitoring and bioassessment of freshwaters in the Neotropical region impacted by deforestation.
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Affiliation(s)
- Francisco Valente-Neto
- Laboratório de Interações Multitróficas e Biodiversidade, Departamento de Biologia Animal, Instituto de Biologia, Universidade Estadual de Campinas, Campinas, SP, Brazil.
| | - Renato B Dala-Corte
- Departamento de Ecologia, Universidade Federal de Goiás, Goiânia, GO, Brazil; Princeton School of Public and International Affairs, Princeton University, Princeton, NJ, USA
| | - Almir M Cunico
- Laboratório de Ecologia, Pesca e Ictiologia, Departamento de Biodiversidade, Setor Palotina, Universidade Federal do Paraná, Palotina, PR, Brazil
| | - André L B Magalhães
- Programa de Pós-Graduação em Ecologia de Biomas Tropicais, Departamento de Biodiversidade, Instituto de Ciências Exatas e Biológicas, Universidade Federal de Ouro Preto (UFOP), Ouro Preto, MG, Brazil
| | - Bruno S Godoy
- Núcleo de Ecologia Aquática e Pesca da Amazônia, Universidade Federal do Pará, Belém, PA, Brazil
| | | | - Diego M P Castro
- Laboratório de Ecologia de Bentos, Departamento de Genética, Ecologia e Evolução, Instituto de Ciências Biológicas, Universidade Federal de Minas Gerais, Belo Horizonte, MG, Brazil
| | - Diego R Macedo
- Departamento de Geografia, Instituto de Geociências, Universidade Federal de Minas Gerais, Belo Horizonte, MG, Brazil
| | - Dilermando P Lima-Junior
- Laboratório de Ecologia e Conservação de Ecossistemas Aquáticos, Universidade Federal de Mato Grosso, Pontal do Araguaia, MT, Brazil
| | - Éder A Gubiani
- Laboratório de Ictiologia e Estatística Pesqueira, Instituto Neotropical de Pesquisas Ambientais, Grupo de Pesquisas em Recursos Pesqueiros e Limnologia, Programa de Pós-Graduação em Conservação e Manejo de Recursos Naturais, Programa de Pós-Graduação em Recursos Pesqueiros e Engenharia de Pesca, Universidade Estadual do Oeste do Paraná, Toledo, PR, Brazil
| | - Fabio de O Roque
- Universidade Federal de Mato Grosso do Sul, Campo Grande, MS, Brazil; Knowledge Center on Biodiversity, Belo Horizonte, MG, Brazil
| | - Fabrício B Teresa
- Laboratório de Biogeografia e Ecologia Aquática, Universidade Estadual de Goiás, Anápolis, GO, Brazil
| | - Fagner Junior Machado Oliveira
- Laboratório de Ecologia e Conservação de Ecossistemas Aquáticos, Universidade Federal de Mato Grosso, Pontal do Araguaia, MT, Brazil
| | - Fernando G Becker
- Laboratório de Ecologia de Paisagens, Departamento de Ecologia, Universidade Federal do Rio Grande do Sul, Porto Alegre, RS, Brazil
| | - Gabriel L Brejão
- Universidade Estadual Paulista (UNESP), Instituto de Biociências, Rio Claro, SP, Brazil
| | - Janaina Brito
- Secretaria de Educação do Estado de Mato Grosso, Diretoria Regional de Educação, Barra do Garças, MT, Brazil
| | - Jansen Zuanon
- Instituto Nacional de Pesquisas da Amazônia, Manaus, AM, Brazil; Universidade Santa Cecília, Santos, SP, Brazil
| | - Jean R S Vitule
- Laboratório de Ecologia e Conservação, Setor de Tecnologia, Departamento de Engenharia Ambiental, Universidade Federal do Paraná, Curitiba, PR, Brazil
| | - Karina Dias-Silva
- Programa de Pós-Graduação em Ecologia, Universidade Federal do Pará, Belém, PA, Brazil
| | - Lilian Casatti
- Universidade Estadual Paulista (UNESP), Departamento de Ciências Biológicas, São José do Rio Preto, SP, Brazil
| | - Luciano B Lima
- Laboratório de Ecologia e Conservação de Ecossistemas Aquáticos, Universidade Federal de Mato Grosso, Pontal do Araguaia, MT, Brazil
| | - Luciano F A Montag
- Laboratório de Ecologia e Conservação, Instituto de Ciências Biológicas, Universidade Federal do Pará, Belém, PA, Brazil
| | - Marcos Callisto
- Laboratório de Ecologia de Bentos, Departamento de Genética, Ecologia e Evolução, Instituto de Ciências Biológicas, Universidade Federal de Minas Gerais, Belo Horizonte, MG, Brazil
| | - Mireile R Dos Santos
- Departamento de Ciências e Biologia, Colégio Pedro II, Campus São Cristóvão II, Rio de Janeiro, RJ, Brazil
| | - Neusa Hamada
- Coordenação de Biodiversidade, Instituto Nacional de Pesquisas da Amazônia, Manaus, AM, Brazil
| | - Paulo A Z Pamplin
- Instituto de Ciência e Tecnologia, Universidade Federal de Alfenas, Poços de Caldas, MG, Brazil
| | - Paulo S Pompeu
- Departamento de Ecologia e Conservação, Universidade Federal de Lavras, Lavras, MG, Brazil
| | - Rafael P Leitão
- Laboratório de Ecologia de Peixes, Departamento de Genética, Ecologia e Evolução, Instituto de Ciências Biológicas, Universidade Federal de Minas Gerais, Belo Horizonte, MG, Brazil
| | - Renata Ruaro
- Laboratório de Biomonitoramento e Ecologia Aplicada, Programa de Pós-graduação em Ciência e Tecnologia Ambiental, Universidade Tecnológica Federal do Paraná, Curitiba, PR, Brazil
| | - Sheyla R M Couceiro
- Laboratório de Ecologia e Taxonomia de Invertebrados Aquáticos, Universidade Federal do Oeste do Pará, Santarém, PA, Brazil
| | - Vinícius Abilhoa
- Museu de História Natural Capão da Imbuia, Prefeitura de Curitiba, Curitiba, PR, Brazil
| | - Yzel R Súarez
- Laboratório de Ecologia, Centro de Estudos em Recursos Naturais, Universidade Estadual de Mato Grosso do Sul, Dourados, MS, Brazil
| | - Renato T Martins
- Coordenação de Biodiversidade, Instituto Nacional de Pesquisas da Amazônia, Manaus, AM, Brazil
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Schulz R, Bundschuh M, Entling MH, Jungkunst HF, Lorke A, Schwenk K, Schäfer RB. A synthesis of anthropogenic stress effects on emergence-mediated aquatic-terrestrial linkages and riparian food webs. THE SCIENCE OF THE TOTAL ENVIRONMENT 2024; 908:168186. [PMID: 37914130 DOI: 10.1016/j.scitotenv.2023.168186] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/09/2023] [Revised: 10/23/2023] [Accepted: 10/27/2023] [Indexed: 11/03/2023]
Abstract
Anthropogenic stress alters the linkage between aquatic and terrestrial ecosystems in various ways. Here, we review the contemporary literature on how alterations in aquatic systems through environmental pollution, invasive species and hydromorphological changes carry-over to terrestrial ecosystems and the food webs therein. We consider both the aquatic insect emergence and flooding as pathways through which stressors can propagate from the aquatic to the terrestrial system. We specifically synthesize and contextualize results on the roles of pollutants in the emergence pathway and their top-down consequences. Our review revealed that the emergence and flooding pathway are only considered in isolation and that the overall effects of invasive species or pollutants on food webs at the water-land interface require further attention. While very few recent studies looked at invasive species, a larger number of studies focused on metal transfer compared to pesticides, pharmaceuticals or PCBs, and multiple stress studies up to now left aquatic-terrestrial linkages unconsidered. Recent research on pollutants and emergence used aquatic-terrestrial mesocosms to elucidate the effects of aquatic stressors such as the mosquito control agent Bti, metals or pesticides to understand the effects on riparian spiders. Quality parameters, such as the structural and functional composition of emergent insect communities, the fatty acid profiles, yet also the composition of pollutants transferred to land prove to be important for the effects on riparian spiders. Process-based models including quality of emergence are useful to predict the resulting top-down directed food web effects in the terrestrial recipient ecosystem. In conclusion, we present and recommend a combination of empirical and modelling approaches in order to understand the complexity of aquatic-terrestrial stressor propagation and its spatial and temporal variation.
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Affiliation(s)
- Ralf Schulz
- iES Landau, Institute for Environmental Sciences, RPTU Kaiserslautern-Landau, Landau, Germany.
| | - Mirco Bundschuh
- iES Landau, Institute for Environmental Sciences, RPTU Kaiserslautern-Landau, Landau, Germany; Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, Uppsala, Sweden
| | - Martin H Entling
- iES Landau, Institute for Environmental Sciences, RPTU Kaiserslautern-Landau, Landau, Germany
| | - Hermann F Jungkunst
- iES Landau, Institute for Environmental Sciences, RPTU Kaiserslautern-Landau, Landau, Germany
| | - Andreas Lorke
- iES Landau, Institute for Environmental Sciences, RPTU Kaiserslautern-Landau, Landau, Germany
| | - Klaus Schwenk
- iES Landau, Institute for Environmental Sciences, RPTU Kaiserslautern-Landau, Landau, Germany
| | - Ralf B Schäfer
- iES Landau, Institute for Environmental Sciences, RPTU Kaiserslautern-Landau, Landau, Germany
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