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Phytoplankton composition of the water and gastrointestinal tract of the mussel Diplodon enno (Ortmann, 1921) from Sao Francisco river (Bahia, Brazil)/Composicao fitoplanctonica da agua e do trato gastrointestinal do molusco Diplodon enno (Ortmann) do rio Sao Francisco (BA - Brasil).

1. Introduction

Freshwater mussels play important roles in limnological environments seen as they are a link in the food chain and help to maintain water quality (Bogan, 2008; Soares-Gomes and Pires-Vanin, 2005; Vaughn et al., 2008, Vaughn, 2010). Several studies report that freshwater bivalves are excellent freshwater biomonitors of the ecosystem status, in particular as accumulators of metals and trace elements (Elder and Collins, 1991; Ravera et al. 2003; Rodrigues et al. 2012) and being exposed to suspended solids and turbulence (Aldridge et al. 1987). Freshwater bivalves can also represent a great conservational tool because of their high longevity and particular sensitivity to water quality changes (Heller, 1990; Elder and Collins, 1991).

Currently, the species of Unionacea, or freshwater mussels, are among the most threatened groups throughout the world (Lydeard et al., 2004). According to Bogan (1993), although it has only recently begun to be recognized, the extinction of freshwater bivalves is happening since, at least, 1900. Bogan (1993) also stated that if all the endangered mussels disappear in the next 100 years, 54% of the 297 living species of freshwater fauna present in North America will become extinct. Threats to the long-term survival of mussels include: degradation of mussel habitat (sediment loading, erosion, pollutants from improper agricultural, forestry, and mining practices); channelization, dredging and bridge construction; traffic (large vessels or domestic animal crossings); dams or other barriers to fish migration; over-harvest and illegal collecting (since many species of the Superfamily Unionacea are potential producers of pearls and buttons) and competition from non-native invasive species such as the zebra mussel (Dreissena polymorpha), the Asian clam (Corbiculafluminea), and in the particular case of Brazil species such as Limnoperna fortunei and Corbicula fluminalis (Avelar et al., 2014; Dudgeon and Morton, 1984; Gazulha et al., 2012; Panha, 1992; Uthaiwan et al., 2001, 2002; Pereira et al., 2012).

Machado et al. (2005) reported in the Brazilian red list of threatened species, that there are several endangered species from the Unionacea Superfamily in the Bahia area, such as, Diplodon rotundus, Anodontites soleniformes and Anodontites trapesialis proving the impact of human action on the freshwater bivalves in this region. Studies with Unionacea populations in Sao Francisco river are scarce and are essentially based on the population distribution (Lima, 2010).

To deepen the knowledge on the culture and propagation of Unionacea species is the main solution for the maintenance of their natural populations (Gatenby et al. 1997). Dietary studies are uncommon and the nutritional requirements for captive unionids, specifically juveniles, remain undetermined. The species from this superfamily are essentially filter feeders, feeding mainly of microalgae, protozoans, other planktonic microorganisms and organic debris (Kotpal, 1997).

Therefore, the objective of the present work is to analyze qualitatively the phytoplankton taxa composition in the stomach contents of the endangered mussel D. enno and also in the water they live. This represents an initial step towards the development of a suitable diet in order to aid the rearing of this species for reintroduction purposes.

2. Material and Methods

Ten specimens of juveniles of Diplodon enno (Family Hyriidae, Superfamily Unionacea) were collected on the [1.sup.st] of April of 2007, at the water channel that connects Sao Francisco river reservoirs of Moxoto and Paulo Afonso (-9.38971 latitude and -38.238574 longitude), belonging to CHESF (Sao Francisco Hydroelectric Company), City of Paulo Afonso, Bahia, Brazil (see Figure 1). At the time of the collection the river was 300 m wide, 15 m maximum deep and had a flow of 1.3 [m.sup.3][s.sup.-1].

2.1. Determination of physico-chemical parameters of the water

The water samples for physico-chemical parameter were collected simultaneously with the juveniles ofD. enno (see Figure 1 - pin), at each of the four sampling sites (1 m distance between each - W1 to W4). The average value from bottom to surface was registered, within a water column with 3 meters in depth. The values for pH, dissolved oxygen and temperature were determined using a U-22XD water quality analyser (Global Waters Instrumentations, U.S.A.), alkalinity, and hardness were determined with an Environmental Testing Bench Photometer C206 (HANNA, Brazil) and transparency was determined using a Secchi disc.

2.2. Phytoplankton collection from the water

Collection of phytoplankton samples for analyses followed the procedures described by Kovitvadhi et al. (2002, 2006). Water samples were collected from four different sampling points 1 m appart from each other. The samples were collected by dragging a plankton net (40 pm mesh, 30 cm diameter) through the 3 m deep water column (from bottom to surface). After collection, samples were transferred to four plastic containers (300 ml) and fixed with formaldehyde 4%, being later analyzed in the laboratory at the Bahia State University (UNEB).

2.3. Phytoplankton extraction from the stomach/gut content

Mussels were collected near the margins, at depth of 3 m, through diving. They were easily identified as they were just slightly buried in the sand or sometimes observed between rocks. Mussels were immediately placed in a thermal box containing ice, in order to be anesthetized and then taken to the laboratory where their gastrointestinal content was removed. Ten mussels ranging from 2 to 4 cm length were surgically opened in order to separate the stomach and the intestine from the remaining soft parts. Stomach and the region of the intestine that extends to the heart were carefully separated from the digestive gland. Then, each of these organs was tied on one end and its contents were squeezed in a test tube with water. The gastrointestinal content of each animal was fixed with formaldehyde (4%) and then shaken to suspend the content.

[FIGURE 1 OMITTED]

2.4. Water and stomach/gut phytoplankton analysis

The samples of phytoplankton collected from the water and the gastrointestinal tract of ten bivalves were analysed qualitatively using Palmer Maloney Chambers, counting ten chambers per sampling point. From each test tube, three aliquots of 1 ml were taken and prepared to be observed under a light microscope (Olympus BX41) coupled with a digital camera (Olympus DP70) (400x). The microalgae were identified according to the works of Branco (1978), Bourrelly (1966, 1968) and Lee (1999).

2.5. Phytoplankton frequency index determination

After the analyses, the frequency, indicating how many times one taxon is present in the set of samples index, was determined. The frequency index values were calculated according to the methodology determined by the state of Sao Paulo's Public Environmental and Sanitary Institution (CETESB, 1978). The formula: [F.sub.0] = Ta.100/TA was used, where Ta is the number of samples where the taxon occurred and TA is the total number of samples. The results were presented as percentages, using the following criterion: > 70% = very frequent (VF); 70% 40% = frequent (F); 40% 10% = infrequent (IF); < 10% = sporadically (S). The case of non occurrence was added to the classification applying for this the term absent (A).

3. Results

The water from the river channel was at an average temperature of 26.25[degrees]C ([+ or -] 0.2) and had an average pH of 7.7 ([+ or -] 0.2). The mean values registered for dissolved oxygen and alkalinity were 7.5 mg.[l.sup.-1] ([+ or -] 0.8) and 50 mg.l-1 ([+ or -] 1.2), respectively (as shown in Table 1).

The physical parameters observed in the collected water seem to be within the expected values for Sao Francisco river. Furthermore, four phytoplankton phyla (Cyanophyta, Chlorophyta, Heterokontophyta and Dinophyta) where identified in the gastroinstestinal tract, whereas only three phyla (without Dinophyta) were identified in the water samples.

The results obtained for phytoplankton composition in the water show the importance of Chlorophyta, representing the largest contribution relatively to the number of taxa (54%), the families Hydrodictyaceae and Desmidiaceae stand out with 3 and 4 taxa, respectively. Specimens from the families Heterokontophyta and Cyanophyta were also found in the analysed water samples, even though to a lesser extent 31% and 15% respectively (see Figure 2), no species of Dinophyta were found.

In the gastrointestinal content, as found in the water samples, Chlorophyta was predominant, representing 54% of the total number of taxa. The divisions Heterokontophyta and Cyanophyta were also found in the samples, representing 27% and 14% respectively, Dinophyta had a smaller contribution to the gastrointestinal content representing only 5% of the total number of taxa (see Figure 3).

In the frequency index calculation for the water samples 50% of Cyanophyta species were classified as very frequent (VF) whereas and the remaining 50% were classified only as frequent (F). 50% of the species from the division Heterokontophyta were classified as frequent (F) and the other half as infrequent (IF). Differently, the Chlorophyta division showed 15% of very frequent (VF), 57% of frequent (F) species and 28% of infrequent (IF) species (as shown in Table 2).

Still regarding to the water samples, Coelastrum sp. was present in 100% of the samples followed by Chroococcus sp. with 75%. Scenedesmus sp., Staurastrum sp., Aulacoseira sp. 1, Aulacoseira sp. 2, Monoraphydium sp., Merismopedia sp. and Golenkinia sp. were present in 50% of the samples. The species Navicula sp., Surirella sp. Closterium sp. and Chlorella sp. were identified in only 25% of the samples (as shown in Table 2).

Regarding the gastrointestinal phytoplankton contents, 68% of the Heterokontophyta species were classified as very frequent (VF), 16% as frequent (F) and the remaining 16% as infrequent (IF). Relatively to Chlorophyta, 33% of the identified species were classified as very frequent (VF), 8% as frequent (F) and 59% of Chlorophyta as infrequent (IF)(Table 2). Concerning the Cyanophyta division, 67% of the identified species were classified as frequent (F) and 33% as infrequent (IF) (as shown in Table 2). The only Dinophyta species was classified as infrequent (IF) (Table 2).

The frequency index in relation to the genus and species observed in the gastrointestinal content showed an occurrence of the Staurastrum sp.a and the Aulacoseira sp. 2 in 100% of the samples (as shown in Table 2). Among the other identified species, the following were observed in a large amount of gut/stomach samples: Aulacoseira sp. 1 (90%), Fragilaria crotonensis (90%), Scenedesmus sp. (90%), Surirella sp. (80%), Pediastrum clathratum (70%), Coelastrum sp. (70%) and Navicula sp. (60%). The remaining species occurred in 50% or less of the samples (as shown in Table 2).

4. Discussion

4.1. Physical and chemical water parameters

The distribution of benthic organisms in lotic ecosystems is directly related to the water current, quality and availability of food, type of substratum (sandy, stone, wood, aquatic macrophytes), water temperature, and the concentrations of dissolved oxygen, alkalinity, pH and ammonium (Palmer et al., 1994; Quinn et al. 1994; Townsend et al. 1997).

According to Callisto et al. (2005), the stretch between Moxoto and Paulo Afonso, where the present study was conducted, is in process of artificial eutrophication and has a high biomass of aquatic macrophytes. Callisto et al. (2005) reported as well substrate diversification and an increase in biodiversity and richness of freshwater bivalves. Furthermore, the development of a community dominated by molluscs in both dry and rainy periods was recorded, associated with particular physical and chemical characteristics, as higher pH, high values of total alkalinity and aquatic macrophytes (Callisto et al., 2005).

In the present study the physical parameters registered in Paulo Afonso revealed that the temperature was normal for that time of the year (April, rainy season) and that waters were also relatively well oxygenated. The pH values were above 7 and therefore appropriate for the development of mollusc communities. The alkalinity values found now in the Paulo Afonso region were higher than the values observed by Ishii (1987) and Sampaio and Lopez (2003) in the Sao Francisco river, downstream of Tres Marias dam, and were also higher than the values reported by Callisto et al. (2005) in the Sao Francisco river, measured in 1997 next to Paulo Afonso reservoir. Therefore, the physical parameters of the water: temperature, pH and alkalinity may favour the growth and the maintenance of D. enno mollusc.

4.2. Phytoplankton composition

Precise knowledge of the natural diets of bivalve populations, particularly the phytoplankton composition, is of prime importance for the understanding of growth and dynamics of these populations (Beukema and Cadee, 1991). However, results are very often difficult to interpret because of the various factors of selection of microalgae interacting across the feeding processes of bivalves (Navarro and Iglesias, 1993; Rouillon and Navarro, 2003). The identification and comparison of stomach content and seston phytoplankton compositions in terms of frequency and abundance of species constitutes a useful approach to this subject. Microalgae have been considered as the main food source for captive mollusc bivalves, since they are filter feeders from early juvenile stage (Kovitvadhi et al. 2006).

The importance of algal species as a food source for captive juvenile mussels is likely a balance between their physical characteristics and nutritional properties (Mummert, 2001). Adult unionids have displayed an ability to sort algae prior to ingestion based on cellular characteristics, such as size, shape, chemical constituents, structure components and specific aggregation properties (Paterson, 1984, 1986; Miura and Yamashiro, 1990; Gatenby et al., 1996; Baker et al., 2000; Baker and Levinton, 2003).

Taking into account the dimension of the particles present in the gastrointestinal contents, the frequency index of Scenedemus sp. (90%), Coelastrum sp. (70%) and Chroococcus sp. (50%), can indicate a facilitated filtration rate for small size species (7-15 [micro]m). According to Morton (1971) and Sprung (1984), small algae cells can be filtered at higher rates, whereas larger ones are filtered at lower rates. Furthermore, the small phytoplankton was predominant in the distribution both in water and gastrointestinal tract, as it is observed for Chlorophyta division (at 54% in both water and tract). This is in accordance with Parker et al. (1998), that pointed out the relative abundance of algal species within the gut contents of adult Amblema plicata and Quadrula pustulosa from the Ohio River was similar to their relative abundance in the external environment.

Nevertheless, other small microalgae absent in the water were found in the gastrointestinal tract in reasonable percentage, such as Chroococcus minutus (50%) and Pediastrum clathratum (70%). This strange observation may be explained by a very fast dynamic fluctuation of these microalgae in the river, associated with a longer digestion time. Another remote possibility is the slow development of the microalgae, which would be accomplished during the digestive process, and so microalgae were living outside (in the water) under an undifferentiated form. Eventually, this same explanation could be applied for the large phytoplankton spectra in the stomach/gut comparatively to the water where some others are absent.

On the other hand, the size and frequency cannot totally explain the considerable presence within the stomach/gut contents of some oversized microalgae (22-43 pm). In fact, Navicula sp. and Surirella sp., both at 25% in the water samples, presented an expressive value of 60% and 80% in the gastrointestinal content, respectively. Moreover, other oversized microalgae, such as Staurastrum sp., Aulacoseira sp. 1 and Aulacoseira sp.2, although showing a moderate occurrence frequency in the water samples (50%), exhibited a maximum percentage of 100% in the tract ofD. enno bivalve. Thus, it is possible to admit that the high prevalence of large size microalgae, observed inside bivalve tract, can be mainly due to the chemical/physical properties of these microalgae, which may represent a nutritional advantage to these bivalves.

4.3. Algal diet perspectives

Gatenby et al. (1997) studied the growth and survival of V iris juveniles testing several different microalgae diets. Juveniles didn't grow as well when fed with chlorophytes, that was justified by the lack of a substantial amount of polyunsaturated fatty acids (PUFA) and by their low nutritional value (Pohl and Zurheide, 1979; Paterson, 1984; Ahlgren et al., 1992; Beck, 2001; Beck and Neves, 2003). On the other hand, the diet composed by diatoms showed better growth results since they are characterized by possessing a high percentage of unsaturated and polyunsaturated fatty acids (UFA and PUFA and oil reserves (lipids) (Erwin, 1973; Werner, 1978; Pohl and Zurheide, 1979; Ahlgren et al. 1992). Based on the results obtained by Gatenby et al. (1997) and analysing of the percentage of species classified with high frequency index observed in the present study, one can conclude that the outstanding presence of diatoms in the gastrointestinal contents is due to their high content in PUFA and UFA, and the high number of taxa of the Chlorophyta division is explained exclusively by the fact that a larger number of taxa were found in the water samples as well.

In summary, algal species have been incorporated, in several works, into the design of direct or recirculating systems of juvenile cultures as the primary food source, due to their apparent significance in the diet of unionoids (Hudson and Isom, 1984; Gatenby et al., 1996, 1997; O'Beirn et al., 1998; Tankersley and Butz, 2000; Henley et al., 2001; Kovitvadhi et al., 2008).

Moreover, Lima et al. (2002) studied the growth of A. cygnea's young adults mentioning a strong increase in the weight of the animals during autumn, which was related to the high percentage of diatoms during that season. Similar results were presented by Beukema & Cadee (1991) and Gatenby et al. (1997). Based on the analysis of the present findings, we suggest a mixture of smaller chlorophytes and large diatoms as an appropriate diet to rear the mussel D. enno. Nevertheless, these statements regarding the influence of size and frequency of microalgae should be deeply studied in laboratory works, in order to offer better nutritional conditions for the survival and maintenance of D. enno.

http://dx.doi.org/10.1590/1519-6984.14514

Acknowledgements

We would like to thank to Dr. Jose Carlos Nascimento de Barros, to Dr. Tamara Almeida, Dr. Maria Cristina Mansur and Dr. Igor Christo Miyahira for all the suggestions and advice. This work was partially supported by the Portuguese Foundation for Science and Technology (FCT) under the projects PTDC/AAC-AMB/117688/2010 and CIIMARPlurianual Program.

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T. Alves (a, b), P. Lima (b), G. M. S. Lima (c), M. C. C. Cunha (d), S. Ferreira (b, e), B. Domingues (b, e) and J. Machado (b, e) *

(a) Instituto Federal de Educacao, Ciencia e Tecnologia da Paraiba, Av. 1[degrees] de Maio, 720, Jaguaribe, CEP 58015-430, Joao Pessoa, PB, Brazil

(b) Departamento de Producao Aquatica, Instituto de Ciencias Biomedicas de Abel Salazar - ICBAS, Universidade do Porto, Rua de Jorge Viterbo Ferreira, 228, CEP 4050-313, Porto, Portugal

(c) Universidade do Estado da Bahia - UNEB, Rua da Gangorra, 503, General Dutra, CEP 48608-240, Paulo Afonso, BA, Brazil

(d) Laboratorio de Ecofisiologia de Microalgas e Microbiologia, Instituto de Tecnologia de Pernambuco - ITEP, Av. Prof Luiz Freire, 700, Cidade Universitaria, CEP 50740-540, Recife, PE, Brazil

(e) Centro Interdisciplinar de Investigacao Maritima e Ambiental - CIIMAR, Universidade do Porto, Rua dos Bragas, 289, CEP 4050-123, Porto, Portugal

* e-mail: jmachado@icbas.up.pt

Received: August 4, 2014--Accepted: November 6, 2014--Distributed: February 29, 2016

(With 3 figures)
Table 1. Mean water physical and chemical parameters
from the four water samples (1 m distance between each)
registered in the stretch between Moxoto reservoir and Paulo
Afonso reservoir at the time of sampling (SD = standard
deviation).

                                    Mean [+ or -] SD

Temperature ([degrees]C)            26.25 [+ or -] 0.2
Dissolved Oxygen (mg. l-1)          7.5 [+ or -] 0.8
Alkalinity (mg. l-1)               50.0 [+ or -] 1.2
pH                                  7.7 [+ or -] 0.2
Transparency (m)                    1.8 [+ or -] 0.2

Table 2. Spectrum and frequency of occurrence of phytoplankton
taxa identified in water samples and gastrointestinal tracts of
10 D. enno samples from Sao Francisco river and its
classification according to the CETESB (1978) criteria.

                            Microalgae present in water

                         W1   W2   W3   W4   [F.sub.0]

Cyanophyta

Chroococcus sp.          x    -    x    x       VF
Merismopedia sp.         -    -    x    x        F
Chroococcus minutus      -    -    -    -        A

Chlorophyta

Chlorella sp.            -    -    -    x       IF
Coelastrum sp.           x    x    x    x       VF
Scenedesmus sp.          x    -    -    x        F
Pandorina sp.            -    -    -    -        A
Pediastrum duplex        -    -    -    -        A
Pediastrum simplex       -    -    -    -        A
Pediastrum clathratum    -    -    -    -        A
Monoraphidium sp.        -    x    -    x        F
Golenkinia sp.           x    x    -    -        F
Cosmarium sp.            -    -    -    -        A
Staurastrum                                      A
cf. leptocladium
Staurastrum sp.          -    x    -    x        F
Closterium sp.           -    -    x    -       IF

Dinophyta

Gymnodinium sp.          -    -    -    -        A

Heterokontophyta

Aulacoseira sp. 1        -    x    x    -        F
Aulacoseira sp. 2        -    x    -    x        F
Cymbella sp.             -    -    -    -        A
Fragilaria crotonensis   -    -    -    -        A
Surirella sp.            x    -    -    -       IF
Navicula sp.             -    x    -    -       IF

                              Microalgae from the
                        gastrointestinal tract of D. enno

                         G1   G2   G3   G4   G5   G6   G7

Cyanophyta

Chroococcus sp.          -    -    x    x    x    x    -
Merismopedia sp.         -    x    -    -    x    x    -
Chroococcus minutus      -    x    -    x    x    x    x

Chlorophyta

Chlorella sp.            x    -    x    -    -    -    -
Coelastrum sp.           x    x    -    x    -    x    x
Scenedesmus sp.          -    x    x    x    x    x    x
Pandorina sp.            -    x    -    -    -    -    -
Pediastrum duplex        x    -    x    x    -    -    x
Pediastrum simplex       -    -    -    -    -    -    -
Pediastrum clathratum    x    -    x    x    x    x    x
Monoraphidium sp.        -    x    -    x    -    -    -
Golenkinia sp.           -    -    -    -    -    -    -
Cosmarium sp.            -    -    -    x    -    -    -
Staurastrum
cf. leptocladium         x              x    x         x
Staurastrum sp.          x    x    x    x    x    x    x
Closterium sp.           -    -    -         x    -    x

Dinophyta

Gymnodinium sp.          -    -    -    -    -    x    x

Heterokontophyta

Aulacoseira sp. 1        x    x    x    x    x    x    x
Aulacoseira sp. 2        x    x    x    x    x    x    x
Cymbella sp.             -    -    x    x    -    -    -
Fragilaria crotonensis   -    x    x    x    x    x    x
Surirella sp.            -    x    x    x    x    x    x
Navicula sp.             -    x    x    x    x    -    x

                              Microalgae from the
                         gastrointestinal tract of D. enno

                         G8   G9   G10   [F.sub.0]

Cyanophyta

Chroococcus sp.          -    x     -        F
Merismopedia sp.         -    x     -       IF
Chroococcus minutus      -    -     -        F

Chlorophyta

Chlorella sp.            -    -     x       IF
Coelastrum sp.           -    x     x       VF
Scenedesmus sp.          x    x     x       VF
Pandorina sp.            -    -     x       IF
Pediastrum duplex        -    -     -       IF
Pediastrum simplex       -    x             IF
Pediastrum clathratum    -    -     x       VF
Monoraphidium sp.        -    x     -       IF
Golenkinia sp.           -    -     -        A
Cosmarium sp.            -    -     -       IF
Staurastrum                                  F
cf. leptocladium                    x
Staurastrum sp.          x    x     x       VF
Closterium sp.           -    -     -       IF

Dinophyta

Gymnodinium sp.          -    -     -       IF

Heterokontophyta

Aulacoseira sp. 1        x    -     x       VF
Aulacoseira sp. 2        x    x     x       VF
Cymbella sp.             -    -     -       IF
Fragilaria crotonensis   x    x     x       VF
Surirella sp.            x    -     x       VF
Navicula sp.             -    -     x        F

"x" = present; "-" = absent; "VF" = very frequent; "F" = frequent;
"IF" = infrequent; "A" = absent

Figure 2. Proportion of the number species per division in
the water samples from the channel that links the reservoirs
of Moxoto to the reservoir of Paulo Afonso.

Cyanophyta         15%
Chlorophyta        54%
Heterokontophyta   31%

Note: Table made from pie chart.

Figure 3. Proportion of the number species per division within the
gastrointestinal tract of D. enno (n = 10) collected from the
channel that links the reservoirs of Moxoto to the reservoir of
Paulo Afonso.

Cyanophyta         14%
Chlorophyta        55%
Dinophyta          4%
Heterokontophyta   27%

Note: Table made from pie chart.
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Title Annotation:Original Article
Author:Alves, T.; Lima, P.; Lima, G.M.S.; Cunha, M.C.C.; Ferreira, S.; Domingues, B.; Machado, J.
Publication:Brazilian Journal of Biology
Date:Apr 1, 2016
Words:5985
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