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Brazilian Journal of Biology

versão impressa ISSN 1519-6984versão On-line ISSN 1678-4375

Braz. J. Biol. vol.77 no.2 São Carlos abr./jun. 2017  Epub 15-Ago-2016

http://dx.doi.org/10.1590/1519-6984.20215 

Original Article

Zooplankton community in the Upper Parnaíba River (Northeastern, Brazil)

Comunidade zooplanctônica do alto rio Parnaíba (Nordeste, Brasil)

P. H. S. Picapedraa  * 

C. Fernandesb 

F. A. Lansac-Tôhaa  c 

aPrograma de Pós-graduação em Biologia Comparada, Universidade Estadual de Maringá – UEM, Avenida Colombo, 5790, CEP 87020-900, Maringá, PR, Brazil

bGrupo de Pesquisas em Recursos Pesqueiros e Limnologia, Universidade Estadual do Oeste do Paraná – UNIOESTE, Rua da Faculdade, 645, CEP 85903-000, Toledo, PR, Brazil

cNúcleo de Pesquisas em Limnologia Ictiologia e Aquicultura, Programa de Pós-graduação em Ecologia de Ambientes Aquáticos Continentais, Universidade Estadual de Maringá – UEM, Avenida Colombo, 5790, CEP 87020-900, Maringá, PR, Brazil

Abstract

The objective of the present work is to evaluate the seasonal patterns of species richness and abundance of the zooplankton community in a semi-arid river, Northeastern of Brazil. Zooplankton samples were taken in four hydrological periods along the Upper Parnaíba River: April (low), August (dry), November (rising) 2013 and January (flood) 2014. The zooplankton community consisted of 125 species; the testate amoebae was the most species-rich (56 species) and the most abundant group (71.5%) of total zooplankton abundance. Season-specific differences were highly significant. The overall zooplankton richness and abundance was significantly higher during the low (71 species) and flood (878.47 ind.m–3) period, respectively. The hydrological regime was important in structuring the zooplankton community, emphasising the importance of the Parnaíba River and its seasonal variation for biodiversity conservation in the Brazilian semi-arid region.

Keywords:  potamoplankton; large rivers; semi-arid; environmental variables; seasonality

Resumo

O objetivo deste trabalho foi avaliar os padrões sazonais da riqueza de espécies e abundância da comunidade zooplanctônica em um rio do semi-árido, Nordeste do Brasil. As amostragens do zooplâncton foram realizadas em quatro períodos hidrológicos ao longo do alto rio Parnaíba: Abril (vazante), Agosto (seca), Novembro (enchente) de 2013 e Janeiro (cheia) de 2014. A comunidade zooplanctônica foi constituída por 125 espécies, sendo as amebas testáceas o grupo mais rico em espécies (56 espécies) e o grupo mais abundante (71,5%) do zooplâncton. Diferenças significativas foram registradas entre os períodos. A riqueza e a abundância do zooplâncton foram significativamente maiores durante o período de vazante (71 espécies) e cheia (878,47 ind.m–3), respectivamente. Os resultados mostraram ainda, que o regime hidrológico foi importante na estruturação da comunidade zooplanctônica, ressaltando a importância do rio Parnaíba e sua variação sazonal para a conservação da biodiversidade do semi-árido brasileiro.

Palavras-chave:  potamoplâncton; grandes rios; semi-árido; variáveis ambientais; sazonalidade

1 Introduction

The Parnaíba River and its tributaries form one of major river systems in northeastern Brazil, crossing the semi-arid region that includes the biomes Caatinga and Cerrado (Medeiros et al., 2011). The Brazilian semi-arid region is characterised by the predominance of intermittent rivers and streams, complex weather patterns, scarce rainfall unevenly distributed and low thermal amplitude (Maltchik and Medeiros, 2006; Medeiros et al., 2011). As a result, many of the tributaries of the Parnaíba River have characteristics ranging from extreme flooding to the total absence of water, which contributes to a high degree of spatial variation and habitat heterogeneity (Medeiros et al., 2011).

Studies on zooplankton ecology are underscored in lentic environments, while few studies have demonstrated the ecological importance of zooplankton in fluvial environments (Perbiche-Neves et al., 2012). In the northeastern Brazil, studies on the potamoplankton are scarce, highlighting recent work by Medeiros et al. (2011) and Lucena et al. (2015), although zooplankton studies in lentic environments are not uncommon to the region (e.g., Eskinazi-Sant’Anna et al., 2007; Almeida et al., 2009; Paranhos et al., 2013). The lack of extensive studies on the ecological processes of the Caatinga biome and its water courses, as well as the lack of knowledge about its biodiversity, has led to the incorrect perception that its aquatic biota is poor in species and endemism. Not surprisingly, most of the studies in aquatic systems of the semi-arid region of Brazil were concentrated in artificial lakes from dammed intermittent streams and rivers (Maltchik and Medeiros, 2006).

Rivers of the Brazilian semi-arid are important economically (e.g., as a source of water and fish), culturally, scientifically, environmentally (e.g., as part of the global hydrological cycle) and for conservation (regional biodiversity and endemic hotspots). The most important issues in the conservation of the semi-arid rivers are the need for recognition of important areas to maintain biodiversity and that this biodiversity is closely associated with the natural patterns of flow and hydrological alterations (Maltchik and Medeiros, 2006). Without an understanding of how the extremes of flood and drought affect aquatic fauna, strategies for the conservation of rivers in the Brazilian semi-arid and their biota will not be effective (Maltchik and Medeiros, 2006; Lucena et al., 2015).

In this way, this study aimed to evaluate the seasonal patterns of species richness and abundance of the zooplankton community in the Parnaíba River. We predicted that: (i) the highest species richness coincides with the flood period, indicating an intensive exchange of fauna during this period, given the greater connectivity between environments and (ii) the higher zooplankton abundance coincides with the dry period, indicating no dilution effect during this period, caused by a lower connectivity between environments.

2 Material and Methods

2.1 Study site

The Parnaíba River is on the border between the states of Maranhão and Piauí, Northeastern of Brazil (Figure 1). It is 1,432 kilometres long and drains an area of about 344,112 km2. It is located in a transition area between semi-arid (BSh) and tropical (Aw) climates (Peel et al., 2007). Most tributaries in the middle and lower portions of the river are perennial, while the small rivers and streams in the upper region are intermittent (Rosa et al., 2003; EPE, 2005). Rainfall in the area ranges from 600 to 1,800 mm per year, and the temperature varies between 24-38 °C (CODEVASF, 2010).

Figure 1 Location of sampling sites in the region of the Upper Parnaíba River, Northeastern Brazil. 

The Parnaíba River is divided into upper, middle and lower portions; the upper portion is characterised by steep slopes and deeper valleys, the middle portion has uneven terrain with some waterfalls and the lower portion shows a more gradual slope and wider valleys (EPE, 2005; Brasil, 2006). The vegetation cover in the basin is diverse, from dense to sparse vegetation types associated with the Caatinga and the Cerrado (CODEVASF, 2010).

2.2 Sampling

Zooplankton samplings were conducted in four quarterly collections: April (low), August (dry), November (rising) 2013 and January (flood) 2014. We sampled seven sites in the channel of the Parnaíba River and also a site at the mouth of each tributary, three on the left bank and two on the right bank of the river, totalling 12 sampling sites (Figure 1).

Zooplankton samples were taken with a suction pump filter 600 liters of water per sample through a conical plankton net of 60 μm mesh size. The collected material was placed in a polyethylene bottle (500 mL) properly labelled and fixed in 4% formaldehyde solution buffered with sodium borate (Na3BO3).

Concurrently with the zooplankton sampling, environmental variables were collected (water temperature, dissolved oxygen, pH, electrical conductivity and turbidity) using portable digital devices. Water samples were also taken in containers of 5 liters and subsequently sent to the laboratory of Grupo de Pesquisas em Recursos Pesqueiros e Limnologia (GERPEL) for chlorophyll-a analysis (Golterman et al., 1978). Water level data were provided by the Agência Nacional de Águas (ANA). The water velocity was measured using the mechanic flowmeter (Flowmeter Gereral Oceanics™).

2.3 Analysis of community data

The zooplankton samples were counted in an optical microscope (Olympus), using a Sedgewick-Rafter chamber. Samples were concentrated to 100 mL, and 50 mL were taken with Hensen-Stempel pipettes. The zooplankton community was analysed for species richness and abundance. The total abundance was expressed in terms of individuals per m–3. The individuals were identified using specialized taxonomic literature (Koste, 1978; Vucetich, 1973; Reid, 1985; Matsumura-Tundisi, 1986; Segers, 1995; Velho and Lansac-Tôha, 1996; Velho et al., 1996; Elmoor-Loureiro, 1997; Lansac-Tôha et al., 2002).

2.4 Statistical analysis

The non-parametric analysis of variance (Kruskal-Wallis test) (Zar, 1999) was used to assess the seasonal differences in species richness and abundance of the zooplankton community. The Bray-Curtis similarity coefficient was calculated, aiming to quantify the differences in abundance between the hydrological periods. This coefficient calculates the absolute differences and the sums of the abundances of species in the samples; it is strongly influenced by the dominant species and does not consider double-absences. The closer the samples are, the smaller the distance between them, and, therefore, the greater the similarity between them (Valentin, 2000). The abundance of the zooplankton community species was correlated with the environmental variables using a canonical correspondence analysis (CCA). This analysis seeks the largest linear combinations between two data sets and enables a simplified view in a two-dimensional plot (Manly, 2008).

The Kruskal-Wallis test, cluster analysis with Bray-Curtis coefficient and CCA were run using the software PC-ORD® (McCune and Mefford 1997).

3 Results

The river level showed the highest value in flood and lowest in dry period. The increase in the velocity of water was positively correlated with the increase in the river level. The environmental variables pH, electrical conductivity, temperature, turbidity, dissolved oxygen and chlorophyll-a were higher in periods of flood and low water conditions, while the lowest values were recorded in the dry period (Table 1).

Table 1 Mean (± SE) of environmental variables measured in the Parnaíba River (Northeastern Brazil) in low, dry, rising and flood periods. 

Parnaíba River
Environmental variables Low Dry Rising Flood
Fluviometric level (cm) 380 ± 39.83 327 ± 2.5 371 ± 79.6 398 ± 66.3
Water velocity (m/s) 0.95 ± 0.06 0.69 ± 0.07 0.73 ± 0.06 0.83 ± 0.05
pH 6.24 ± 0.1 5.45 ± 0.04 5.82 ± 0.09 6.47 ± 0.2
Electrical conductivity (µS/cm–1) 9.98 ± 0.85 5.25 ± 0.42 6.43 ± 0.69 9.85 ± 1.42
Temperature (°C) 26.7 ± 0.25 24.4 ± 0.26 25.2 ± 0.18 27.8 ± 0.44
Turbidity (NTU) 75.97 ± 19.68 6.6 ± 0.76 34.22 ± 10.07 49.93 ± 14.82
Dissolved oxygen (mg/L–1) 7.53 ± 0.11 6.89 ± 0.16 7.18 ± 0.16 7.26 ± 0.07
Chlorophyll-a (µg/L–1) 0.32 ± 0.15 0.11 ± 0.07 0.37 ± 0.13 3.56 ± 1.7

The zooplankton community was represented by 125 species; the testate amoebae had the highest species richness (56 species), followed by rotifers (52 species), cladocerans (15 species) and copepods (two species). Testate amoebae were represented by 10 families; the greatest richness was observed for Difflugiidae (20 species) and Arcellidae (11 species). Rotifers were distributed in 14 families, of which Brachionidae (11 species) and Lecanidae (10 species) were the most species-rich. Among microcrustaceans, cladocerans were represented by six families; Chydoridae (eight species) showed the highest species richness, and copepods were represented by two species of the family Cyclopidae (Table 2).

Table 2 List of zooplankton taxa recorded in the Parnaíba River (Northeastern Brazil). 

Testate Amoebae
ARCELLIDAE
Arcella brasiliensis Cunha, 1913 A. gibbosa Pénard, 1890
A. conica (Playfair, 1918) A. hemisphaerica gibba Deflandre, 1928
A. costata Ehrenberg, 1847 A. megastoma Pénard, 1902
A. crenulata Deflandre, 1928 A. rotundata Playfair, 1918
A. dentata Ehrenberg, 1830 A. vulgaris Ehrenberg, 1830
A. discoides Ehrenberg, 1843
CENTROPYXIDAE
Centropyxis aculeata (Ehrenberg, 1838) C. gibba (Deflandre, 1929)
C. cassis (Wallich, 1864) C. marsupiformis Deflandre, 1929
C. discoides Pénard, 1902 Centropyxis sp.
C. ecornis (Ehrenberg, 1841)
CYPHODERIIDAE
Cyphoderia ampulla (Ehrenberg, 1840)
DIFFLUGIIDAE
Cucurbitella dentata quinquelobata Gauthier-Lièvre and Thomas, 1960 D. litophila Pénard, 1902
Difflugia acuminata Ehrenberg, 1838 D. lobostoma Leidy, 1879
D. compressa (Carter, 1864) D. minuta Rampi, 1950
D. constricta Ehrenberg, 1841 D. oblonga Ehrenberg, 1838
D. corona Wallich, 1864 D. penardi Hopkinson, 1909
D. cylindrus (Thomas, 1953) D. pseudogramen Gauthier-Lièvre and Thomas, 1960
D. distenda (Pénard, 1899) D. pyriformis Perty, 1849
D. elegans Pénard, 1890 Difflugia sp.
D. gramen Pénard, 1902 D. urceolata Carter, 1864
D. linearis Gauthier and Lièvre, 1958 D. cf. yorkui Nicholls, 2007
EUGLYPHIDAE
Euglypha acanthophora (Ehrenberg, 1841) E. laevis (Perty, 1849)
E. denticulata Brown, 1912 Euglypha sp.
E. filifera Pénard, 1890
HYALOSPHENIIDAE
Heleopera sp. H. papilio Leidy, 1874
Hyalosphenia cuneata Stein, 1857
LESQUEREUSIDAE
Lesquereusia spiralis (Ehrenberg, 1840) Netzelia oviformis (Cash, 1909)
Lesquereusia sp.
PARAQUADRULIDAE
Quadrulella symmetrica tubulata (Gauthier-Lievre, 1953)
TRIGONOPYXIDAE
Cyclopyxis impressa (Daday, 1905) Cyclopyxis sp.
C. kahli (Deflandre, 1929)
TRINEMATIIDAE
Trinema enchelys (Ehrenberg, 1838) T. lineare Pénard, 1890
Rotifera
BRACHIONIDAE
Brachionus calyciflorus Pallas, 1766 K. cochlearis (Gosse, 1851)
B. caudatus Barrois and Dadai, 1894 K. lenzi Hauer, 1953
B. dolabratus Harring, 1914 K. tropica (Apstein, 1907)
B. falcatus Zacharias, 1898 Plationus patulus (Müller, 1786)
Kellicottia bostoniensis (Rousselet, 1908) Platyias quadricornis (Ehrenberg, 1832)
Keratella americana Carlin, 1943
COLLOTHECIDAE
Collotheca sp.
CONOCHILIDAE
Conochilus coenobasis (Skorikow, 1914)
EUCHLANIDAE
Dipleuchlanis propatula (Gosse, 1886) Euchlanis dilatata Ehrenberg, 1832
HEXARTHRIDAE
Hexarthra sp.
LECANIDAE
Lecane bulla (Gosse, 1851) L. lunaris (Ehrenberg, 1832)
L. cornuta (Müller, 1786) L. proiecta Hauer, 1956
L. leontina (Turner, 1892) L. quadridentata (Ehrenberg, 1830)
L. ludwigi (Eckstein, 1883) L. signifera (Jennings, 1896)
L. luna (Müller, 1776) Lecane sp.
LEPADELLIDAE
Lepadella cristata (Rousselet, 1893) Lepadella sp.
L. ovalis (Müller, 1786) Paracolurella logima (Myers, 1934)
L. patella (Müller, 1773)
NOTOMMATIDAE
Cephalodella gibba (Ehrenberg, 1830) Notommata copeus Ehrenberg, 1834
Cephalodella sp. Monommata sp.
PHILODINIDAE
Dissotrocha aculeata (Ehrenberg, 1832) Dissotrocha sp.
SYNCHAETIDAE
Ploesoma hudsoni (Imhof, 1891) Polyarthra dolichoptera Idelson, 1925
Synchaeta stylata Wierzejski, 1893 P. vulgaris (Carlin, 1943)
TESTUDINELLIDAE
Testudinella patina (Hermann, 1783) T. tridentata Smirnov, 1931
TRICHOCERCIDAE
Trichocerca bicristata (Gosse, 1887) T. similis (Wierzejski, 1893)
T. cylindrica (Imhof, 1891) Trichocerca sp.
TRICHOTRIIDAE
Macrochaetus sericus (Thorpe, 1893) Trichotria tetractis (Ehrenberg, 1830)
M. collinsii (Gosse, 1867)
TROCHOSPHAERIDAE
Filinia opoliensis (Zacharias, 1898) F. terminalis (Plate, 1886)
Cladocera
BOSMINIDAE
Bosmina hagmanni Stingelin, 1904 Bosmina sp.
CHYDORIDAE
Acroperus tupinamba Sinev and Elmoor-Loureiro, 2010 Chydorus eurynotus Sars, 1901
Alona dentifera (Sars, 1901) Chydorus sp.
A. glabra Sars, 1901 Coronatella poppei (Richard, 1897)
Alonella dadayi Birge, 1910 Picripleuroxus cf. denticulatus (Elmoor-Loureiro, 1997)
DAPHNIIDAE
Ceriodaphnia cornuta Sars, 1886 Daphnia gessneri Herbst, 1967
ILYOCRYPTIDAE
Ilyocryptus spinifer Herrick, 1882
MACROTHRICIDAE
Macrothrix laticornis (Jurine, 1820)
SIDIDAE
Diaphanosoma spinulosum Herbst, 1967
Copepoda
CYCLOPYDAE
Thermocyclops decipiens (Kiefer, 1929) T. minutus (Lowndes, 1934)

In the different hydrological periods, the highest number of species (71 species) was registered in the low period, followed by periods of dry (69 species), rising (67 species) and flood (60 species). Testate amoebae showed higher species richness during the flood period (38 species), and was the most species-rich group in all studied periods, except in the low period, when the number of species was similar to that of rotifers. Rotifers presented the highest species richness during the dry period (32 species). Among microcrustaceans, cladocerans showed higher richness in the low and rising periods (eight species) and copepods during the flood period (two species) (Figure 2a). The variation in the mean richness values was driven by the expressive contribution of testate amoebae and rotifers (Figure 2b). There was a significant difference (Kruskal-Wallis test p < 0.05) in mean species richness between hydrological periods for testate amoebae, cladocerans and rotifers.

Figure 2 (a) Number of species (%); (b) mean species richness (± SE); (c) abundance (%) and (d) mean abundance (± SE) of Testate amoebae, Rotifera, Cladocera and Copepoda during low, dry, rising and flood periods in the Parnaíba River, Northeastern Brazil. 

Regarding the zooplankton abundance, the highest value (878.47 ind.m–3) was recorded during the flood period, followed by rising (633.68 ind.m–3), dry (595 ind.m–3) and low (473.61 ind.m–3) periods (Table 3). Testate amoebae showed greater abundance during the flood period (767.71 ind.m-3), rotifers during the dry period (308.61 ind.m–3), cladocerans during the rising period (40.63 ind.m–3) and copepods during the flood period (35.83 ind.m–3) (Figure 2c, Table 3).

Table 3 Mean abundance (± SE) of Testate amoebae, Rotifera, Cladocera and Copepoda during low, dry, rising and flood periods in the Parnaíba River, Northeastern Brazil. 

Parnaíba River
Zooplankton Low Dry Rising Flood
Testate amoebae 341.11 ± 54.1 264.17 ± 24.65 464.24 ± 113.37 767.71 ± 93.31
Rotifera 86.11 ± 15.96 308.61 ± 56.41 104.51 ± 14.15 77.78 ± 16.33
Cladocera 10.56 ± 3.04 21.94 ± 9.47 40.63 ± 15.32 1.74 ± 0.61
Copepoda 35.83 ± 8.19 0.28 ± 0.28 24.31 ± 5.1 31.25 ± 13.06
Total 473.61 ± 47.01 595 ± 59.7 633.68 ± 114.53 878.47 ± 90.99

The variation in the mean values of abundance was mainly related to the large contribution of testate amoebae and rotifers (Figure 2d). Testate amoebae was the most abundant group in the study, representing 71.5% of the zooplankton abundance, followed by rotifers (22%), whereas microcrustaceans were the least abundant in the community (3.5% copepods and 3% cladocerans). Young stages (nauplii and copepodids) were the main contributors to the abundance of copepods. There was a significant difference (Kruskal-Wallis test p < 0.05) in the mean abundance of all zooplankton groups between hydrological periods.

The cluster analysis (Bray-Curtis coefficient) applied to hydrological periods separated the dry period from the others due to a higher contribution of Filinia opoliensis (Zacharias, 1898) in the community during this period. The remaining periods (low, rising and flood) showed similarity values around 50% and were grouped separately with high similarity (Figure 3a).

Figure 3 (a) Dendrogram of cluster analysis: the Bray-Curtis similarity coefficient per hydrological period (low, dry, rising and flood) of the Parnaíba River (Northeastern Brazil) and (b) canonical correspondence analysis (CCA) of environmental variables and zooplankton species abundance. Code: L = Low; D = Dry; R = Rising; F = Flood; Wv = Water velocity (m/s); EC = Electrical conductivity (µS/cm–1); Te = Temperature (°C); Tu = Turbidity (NTU); DO = Dissolved oxygen (mg/L–1); Ch = Chlorophyll-a (µg/L–1). 

The CCA indicated a significant correlation (p < 0.05) between the environmental variables and the abundance of zooplankton groups. The axis 1 of CCA explained 11.7% of the data variability and the axis 2 explained 7.3%, totalling 19% of the variability. In general, the analysis shows a clear separation of the dry and rising periods from the other hydrological periods. Most species of testate amoebae were grouped in the low and flood periods, positively correlated with the water velocity, electrical conductivity, temperature, turbidity, chlorophyll-a and pH; however, in the flood, they were dispersed and positively correlated with dissolved oxygen. Rotifers were concentrated in the dry period, negatively correlated to the environmental variables, and dispersed in the other periods. Among microcrustaceans, cladocerans were concentrated mainly in the rising period, positively correlated with dissolved oxygen, and the copepods (including nauplii and copepodids in CCA) in the low and flood periods, positively correlated with the water velocity, electrical conductivity, temperature, turbidity, chlorophyll-a and pH (Figure 3b).

4 Discussion

This study showed that the region of the Upper Parnaíba River has a well-marked seasonal variation given the differences in environmental variables, and the hydrological regime is the main driver of the physical, chemical and biological dynamics of the Upper Parnaíba River. The increase in the river’s level was positively associated with higher values of environmental variables, especially chlorophyll-a, water velocity and turbidity (mainly from suspended sediment).

Among different zooplankton groups, the testate amoebae were the most abundant and the most species-rich group. The families with the highest number of species (Difflugiidae and Arcellidae) have been identified as prevalent in several studies in various aquatic habitats (Velho et al., 2004; Alves et al., 2012; Lansac-Tôha et al., 2009; 2014; Arrieira et al., 2015).

The family Arcellidae, expressive in plankton, usually has small species, of low density and with shells made of endogenous materials secreted by the amoeba, which allows the occupation of the planktonic habitat (Lansac-Tôha et al., 2014). The family Difflugiidae presents species in plankton with the same type of morphology, i.e. spherical shells. This morphological type, along with the types of shells of most of Arcellidae species (hemispherical), is commonly found in plankton (Lansac-Tôha et al., 2014). However, these authors also identified elongated and flattened shapes, which were also observed in plankton in this study, and these species are identified as typical of aquatic macrophytes in the littoral region and sediment.

Among the rotifers, Brachionidae is one of the most important taxa of freshwater zooplankton, whose species usually have planktonic habits, while Lecanidae is related to the benthos and periphyton, especially in sites rich in vegetation, occurring occasionally in the plankton (Almeida et al., 2009). The dominance of these two families is probably due to the great plasticity of the organisms of these families in relation to limnological conditions and food available. The species of these families are usually predominant in tropical rivers and lakes (e.g., Bonecker et al., 2009; Lansac-Tôha et al., 2009; Lucena et al., 2015).

Among the cladocerans, the predominance of Chydoridae is common for river environments, although this type of environment is considered less favourable for the establishment of this group due to predation by fish and high water flow (Viroux, 2002), which suggests that life in lotic environments is related to some specialisation and adaptation to turbulence, which are not evident in cladocerans.

Copepods were represented only by Cyclopidae species, which is related to the ability of this group to inhabit different environments and compartments (littoral, pelagic and benthic zones), unlike the calanoid group, whose species are characteristic of lentic environments (Perbiche-Neves et al., 2012). Most individuals found in the sampled sites were young stages (nauplii and copepodids). Adult copepods have few records in rivers: the young forms are more numerous (Paggi, 1984). This predominance of young stages of copepods in the zooplankton community was also reported by other authors (e.g., Nogueira et al., 2008; Almeida et al., 2009; Lansac-Tôha et al., 2009) and is frequently linked to high mortality rates of adult forms, which are more susceptible to predation by planktivorous fish (Paranhos et al., 2013).

Ecological studies on the zooplanktonic fauna in the Parnaíba River channel are lacking. The few existing studies are mostly restricted to the fauna of rotifers and microcrustaceans (e.g., Medeiros et al., 2011; Lucena et al., 2015). Studies on testate protozoa are non-existent in the region, precluding comparisons.

The cluster analysis (Bray-Curtis coefficient) distinguished the dry period from the others. This is explained by the greater difference found in the total species abundance, evidenced by a greater contribution of F. opoliensis to the zooplankton community in the dry period. Suggesting that this species found better conditions in which to settle and colonise the environment in this period. The other periods presented high similarity, which did not allow a clear view of the predominance of any particular taxon.

The CCA showed that testate amoebae were grouped in periods with higher water levels. The data suggest that the increase in the abundance of these protists is mainly due to the higher water velocity and turbidity in the Parnaíba River basin. Although testate amoebae are mainly associated with sediment and littoral vegetation, they are considered common in plankton, transported to the water column with the suspension of sediment caused by water turbulence (Velho et al., 2004; Alves et al., 2012; Lansac-Tôha et al., 2009, 2014; Arrieira et al., 2015).

The abundance of rotifer species was concentrated in the dry period; the lower water velocity may have favoured the colonisation of this group. Thorp and Mantovani (2005) and Baranyi et al. (2002) reported that the abundances of rotifers were significantly reduced during periods of higher water flow; only in periods of lower water flow the appearance of sandbar islands promoted hydrological retention areas favouring an increase in the abundance of these organisms.

The low correlation of microcrustaceans with environmental variables may be related to the hydrological characteristics of the region, which do not provide ideal sites for development of these organisms, mainly due to the influence of the water velocity. Organisms with higher swimming capacities can develop in these environments, as slower organisms are transported by the current. Thorp and Mantovani (2005) found similar results in rivers of the semi-arid in large plains in the USA, suggesting that the water velocity and the suspension of high loads of sediment act directly in reducing the abundance and number of microcrustacean species, dispersing them and preventing successful colonisation.

There is widespread consensus that potamoplankton is regulated mainly by abiotic factors (Baranyi et al., 2002). According to Thorp and Mantovani (2005), especially the turbidity and the hydrological retention (influenced by the flow velocity and low velocity areas - slackwaters) are important for potamoplankton.

In other Brazilian rivers, it is recognised that the flow and lateral connectivity of the river with the floodplain wetlands are the main structuring factors for the zooplankton biodiversity (e.g., Bozelli and Huszar, 2003; Casanova and Henry, 2004; Lansac-Tôha et al., 2009). Nevertheless, due to the absence of floodplain wetlands in semi-arid rivers, this factor is not important. The Brazilian semi-arid waterways are geomorphologically characterised as courses with no meanders and no floodplains, with floods restricted to the main river channel (Maltchik and Medeiros, 2006). On the other hand, during the floods, longitudinal connections between isolated water bodies seems to be an important factor in the spread and maintenance of biodiversity in these systems (Medeiros and Maltchik, 2001; Medeiros et al., 2011; Lucena et al., 2015).

The predicted proposals that could explain the increase in zooplanktonic species richness and abundance during the flood and dry periods, respectively, were rejected. Therefore, our results suggest that the Parnaíba River has characteristics common to other rivers found in the Brazilian semi-arid region, including well-marked seasonality, where hydrological periods reflect directly on the river flow velocity, pointed out as the main factor that drives the zooplankton community structure, transporting the organisms from the sediment and aquatic macrophytes of the littoral region to the plankton. This study also highlighted the importance of the Parnaíba River and its seasonal variation for biodiversity conservation in the Brazilian semi-arid region.

Acknowledgements

The authors are grateful to Dr. Luiz Felipe Machado Velho and Dr. Geziele Mucio Alves for suggestions. The Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) for the doctoral scholarship to the first author. We thank Grupo de Pesquisas em Recursos Pesqueiros e Limnologia (GERPEL) of the Universidade Estadual do Oeste do Paraná (UNIOESTE) for providing logistical support for collecting and analysing materials.

(With 3 figures)

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Received: November 26, 2015; Accepted: February 03, 2016

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