Elsevier

Limnologica

Volume 85, November 2020, 125822
Limnologica

Response of cladoceran assemblages to restoration of riparian vegetation: A case study in a tropical reservoir of Brazil

https://doi.org/10.1016/j.limno.2020.125822Get rights and content

Abstract

In recent decades, riparian vegetation has been removed from important ecosystems around the world, in spite of its high ecological importance for aquatic biota. Nevertheless, the effects of catchment land use on zooplankton have been little studied. The present study investigated if replanting riparian vegetation in a tropical reservoir influences the richness and abundance of cladoceran communities, by addressing the question of whether cladocerans show differences in richness and abundance among four levels of riparian vegetation conditions: 1) native forest (NF); 2) 30 years after forest replanting (R1); 3) 10 years after forest replanting (R2); and 4) no forest (No-F). Zooplankton samples were obtained from 9 stations in the Volta Grande Reservoir, Minas Gerais, Brazil. Cladocerans in zones NF and R1 showed higher levels of richness and abundance than in zones No-F and R2. Ceriodaphnia reticulata, Ceriodaphnia laticaudata, and Diaphanosoma spinulosum showed higher abundances in zones NF and R1. Cladoceran community structure was influenced by the different levels of riparian vegetation. This study showed that the presence and age of riparian forest positively influence the abundance, richness and diversity of cladoceran assemblages. Furthermore, our results indicated that C. reticulata, C. laticaudata and D. spinulosum are more efficient than other cladocerans in exploiting allochthonous resources provided by riparian forest. Functional diversity was higher in zones NF and R1, suggesting that the trait composition of cladoceran assemblages responds positively to recovery of riparian forest. Overall, our research suggests that cladocerans are good indicators of riparian vegetation conditions and that restoration of riparian forest positively affects cladoceran assemblages of tropical reservoirs.

Introduction

Riparian vegetation is important for aquatic ecosystems, since it provides habitat for many species, controls fluvial erosion, and functions as a biological filter of pollutants between terrestrial and aquatic zones. Riparian vegetation also serves as wildlife habitat and ecological corridors, retains sediment, and protects aquatic ecosystems from agrochemical contamination (Lowrance, 1998; Micheli and Kirchner, 2002). Additionally, these vegetation strips shape habitat heterogeneity and modulate the input of dissolved organic matter, which is used as an allochthonous resource by aquatic organisms (Zalewski et al., 1995; France et al., 1996; Cecilio et al., 2004; Dodson et al., 2005; Tundisi et al., 2008; Seger et al., 2012).

Despite its ecological importance, riparian vegetation has been removed from the margins of waterbodies around the world, due to human occupation and development of industry and agriculture near aquatic systems (Basińska et al., 2014; Chen et al., 2019). Previous studies in subtropical areas have reported that input of dissolved inorganic matter from riparian forests positively affected the abundance and richness of zooplankton species (Carpenter et al., 2005; Czerniawski, 2013; Dodson et al., 2007; Watkins et al., 2011). However, no information is available concerning the effect of riparian forest on zooplankton communities of rivers modified by the construction of reservoirs in tropical ecosystems.

Replanting riparian vegetation is an effective strategy for restoration of impacted watersheds (Newaz et al., 2019; Tundisi et al., 2008). Some evidence shows that particulate organic carbon sourced from riparian grass can partly support aquatic food webs through the trophic link to zooplankton (Taipale et al., 2014). Cladocerans can dominate the zooplankton of freshwater systems such as reservoirs (Guevara et al., 2009) and are good indicators of environmental quality (Eyto et al., 2002; Seminara et al., 2016), especially in human-impacted ecosystems (Leppänen et al., 2018). In addition, changes in species composition as a response to environmental changes may cause shifts in functional groups, affecting ecosystem functioning (Nevalainen and Luoto, 2017). However, little is known about the responses of crustacean species to restoration of forest vegetation in areas impacted by human occupation, industry, and agriculture.

The relationship between riparian forest conservation and aquatic biota has been insufficiently studied in tropical freshwater systems (Zhao et al., 2014; Braghin et al., 2018). In addition, no information is available regarding whether replanting riparian forests has only short-term or longer-lasting effects on planktonic crustacean communities in tropical systems, and how riparian reforestation could affect the richness, abundance and functional diversity of crustacean species in reservoir systems. The present study tested the hypothesis that replanting riparian vegetation around an impacted reservoir may influence cladoceran communities, by addressing the question of whether cladocerans show differences in richness, abundance and contribution of species to functional groups, among four levels of riparian vegetation conditions: 1) preserved native forest; 2) forest 30 years after replanting; 3) forest 10 years after replanting; and 4) no forest.

Our sampling design allowed us to test, in a space-for-time substitution approach, the responses of cladoceran communities to riparian forest age and spatial distribution. We tested if a short period (10 years) and long period (30 years) after replanting might result in similar patterns of richness, total abundance, and relative contribution of functional groups of cladocerans, compared to an area where the riparian forest has never been removed (preserved native forest) in a tropical reservoir in Brazil. If cladoceran communities from restored zones (10 and 30 years old) have similar richness, abundance and relative contribution of functional groups compared to areas without riparian forest (no-forest zones), the effects of vegetation restoration should be considered negligible for cladoceran communities in this reservoir.

Section snippets

Study area

The study was performed in the Volta Grande Reservoir (20° 02′ 15.52″ S and 48° 13′ 28.38″ W) on the Grande River (part of the Paraná River basin) on the border of Minas Gerais and São Paulo states, Brazil (Freitas and Thomaz, 2011; Viola et al., 2015) (Fig. 1). The reservoir occupies parts of the municipalities of Conceição das Alagoas, Água Comprida and Uberaba in Minas Gerais, and Miguelópolis, Aramina and Igarapava in São Paulo. The reservoir covers an area of approximately 143.4 mil km2

Limnological variables

The environmental variables showed no significant differences among the zones with different riparian vegetation (Kruskal-Wallis, p > 0.05). The results from the ordination analysis (PCA) did not indicate a relationship between the spatial limnological features of the reservoir and the types of riparian vegetation. The mean temperature was 24.8 ± 2 °C and the mean pH was 7.16 ± 0.78. The mean dissolved-oxygen concentration, electrical conductivity and total suspended solids were 8.9 ± 0.9 mg∙L–1

Discussion

The present study showed that different conditions of riparian vegetation (presence and time since replanting) significantly affected the richness, abundance and community structure of cladocerans of a tropical reservoir system in Brazil, and suggested that besides being indicators of water quality in lakes (Eyto et al., 2002; Jeppesen et al., 2011), cladocerans are good indicators of riparian vegetation conditions in tropical reservoirs. Our results do not agree with the findings of Pearson et

Authorship contributions

Conception and design of the study: Eskinazi-Sant’Anna, EM; Leite, MGP. Acquisition of data: Eskinazi-Sant’Anna, EM; Leite, MGP. Analysis and/or interpretation of data: Santos, GS; Eskinazi-Sant’Anna, EM; Cortez-Silva, EE. Drafting the manuscript: Santos, GS; Eskinazi-Sant’Anna, EM; Cortez-Silva, EE. Revising the manuscript critically for important intellectual content: Santos, GS; Eskinazi-Sant’Anna, EM. Approval of the version of the manuscript to be published: Cortez-Silva, EE; Santos, GS;

Declaration of Competing Interest

The authors report no declarations of interest.

Acknowledgements

This study was made possible by the high quality of public universities in Brazil, and their long-standing tradition of training qualified professionals, in spite of the current Brazilian Federal Government’s unwillingness to recognize the importance of public universities, science and biodiversity. CEMIG and FAPEMIG provided financial support to the project (CRA-APQ03055/1). To all staff members of Volta Grande Station for their assistance during field work. We are very grateful to the boatman

References (83)

  • P.M. Andrade et al.

    Diet and feeding of fish from Grande River, located below the Volta Grande Reservoir, MG-SP

    Braz. J. Biol.

    (2005)
  • A.J. Barnett et al.

    Functional diversity of crustacean zooplankton communities: towards a trait-based classification

    Freshw. Biol.

    (2007)
  • A.M. Basińska et al.

    Effect of surrounding trees and dry rush presence on spring zooplankton community in an urban pond complex

    Ann. Limnol. / Int. J. Limnol.

    (2014)
  • F.D.F. Bomfim et al.

    Adjacent environments contribute to the increase of zooplankton species in a neotropical river

    Acta Limnol. Bras.

    (2017)
  • L. Boven et al.

    Impact of hydroperiod on seasonal dynamics in temporary pool cladoceran communities

    Fund. Appl. Limnol.-Arch. Hydrobiol.

    (2009)
  • L.S.M. Braghin et al.

    Effects of dams decrease zooplankton functional β-diversity in river-associated lakes

    Freshw. Biol.

    (2018)
  • K.P. Brodersen et al.

    Reconstruction of trophic state in Danish lakes using subfossil chydorid (Cladocera) assemblages

    Can. J. Fish. Aquat. Sci.

    (1998)
  • J.L. Brooks et al.

    Predation, body size, and composition of plankton

    Science

    (1965)
  • S.R. Carpenter et al.

    Ecosystem subsidies: terrestrial support of aquatic food webs from 13C addition to contrasting lakes

    Ecology

    (2005)
  • E.B. Cecilio et al.

    Effect of size on the energy acquired in species of the fish from a neotropical reservoir

    Brazil. Environ. Biol. Fishes

    (2004)
  • Cemig

    Usina Hidrelétrica Volta Grande [WWW Document]. 2012

    (2012)
  • R. Czerniawski

    Zooplankton community changes between forest and meadow sections in small headwater streams, NW Poland

    Biologia

    (2013)
  • S.I. Dodson et al.

    Land use, water chemistry, aquatic vegetation, and zooplankton community structure of shallow lakes

    Ecol. Appl.

    (2005)
  • S.I. Dodson et al.

    Effect of watershed land use and lake age on zooplankton species richness

    Hydrobiologia

    (2007)
  • C.A. Duigan

    The ecology and distribution of the littoral freshwater Chydoridae (Branchiopoda, Anomopoda) of Ireland, with taxonomic comments on some species

    Hydrobiologia

    (1992)
  • C.A. Duigan et al.

    The late-glacial and early-Holocene palaeoecology of cladoceran microfossil assemblages at Kråkenes, western Norway, with a quantitative reconstruction of temperature changes

    J. Paleolimnol.

    (2000)
  • B.H. Dussart et al.

    A review of systematics, distribution and ecology of tropical freshwater zooplankton

    Hydrobiologia

    (1984)
  • L.M.A. Elmoor-Loureiro

    Manual de identificação de cladóceros límnicos do Brasil

    (1997)
  • E. Eyto et al.

    The use of members of the family Chydoridae (Anomopoda, Branchiopoda) as an indicator of lake ecological quality in Ireland

    Biol. Environ.: Proc. R. Irish Acad.

    (2002)
  • A.S. Ferrão-Filho et al.

    Effects of unicellular and colonial forms of toxic Microcystis aeruginosa from laboratory cultures and natural populations on tropical cladocerans

    Aquat. Microb. Ecol.

    (2003)
  • A.D.S.S. Ferrão-Filho et al.

    Responses of tropical cladocerans to a gradient of resource quality

    Freshw. Biol.

    (2005)
  • A.M. Ferrato

    Zooplâncton. Anexo 3 (185–186). In Orellana, J.A. de. Estudio limnológico de la laguna Paiva (provincia de Santa Fe, Argentina)

    Physis

    (1967)
  • D. Flössner

    Die Haplopoda und Cladocera Mitteleuropas

    (2000)
  • R. France et al.

    Decreased carbon and nutrient input to boreal lakes from particulate organic matter following riparian clear-cutting

    Environ. Manage.

    (1996)
  • A.D. Freitas et al.

    Inorganic carbon shortage may limit the development of submersed macrophytes in habitats of the Paraná River basin

    Acta Limnol. Bras.

    (2011)
  • J. García-Chicote et al.

    Zooplankton species as indicators of trophic state in reservoirs from Mediterranean river basins

    Inland Waters

    (2019)
  • M.F. Gutierrez et al.

    Salinity shapes zooplankton communities and functional diversity and has complex effects on size structure in lakes

    Hydrobiologia

    (2018)
  • M.A. Hanson et al.

    Influences of forest harvest and environmental gradients on aquatic invertebrate communities of seasonal ponds

    Wetlands

    (2009)
  • R.C. Hart

    Zooplankton feeding rates in relation to suspended sediment content: potential influences on community structure in a turbid reservoir

    Freshw. Biol.

    (1988)
  • M.J. Jennings et al.

    Is littoral habitat affected by residential development and land use in watersheds of Wisconsin lakes?

    Lake Reserv. Manage.

    (2003)
  • E. Jeppesen et al.

    Fish-induced changes in zooplankton grazing on phytoplankton and bacterioplankton: a long-term study in shallow hypertrophic Lake Søbygaard

    J. Plankton Res.

    (1996)
  • Cited by (5)

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