Metazoan endoparasites of Brycon orbignyanus (Characidae: Bryconinae) in a neotropical floodplain.
Floods can change the population dynamics of fish populations and their biological and physiological conditions, thus influencing the structure and composition of the fauna of fish parasites (Takemoto et al., 2009). Freshwater fish are vertebrates that can be utilized as a model to study hosts that are home to a large variety of parasite species, being ectoparasites or endoparasites belonging to different phyla (Eiras, Takemoto, & Pavanelli, 2006). Pavanelli, Machado, and Takemoto (1997) published a preliminary list of the helminth parasites of fishes from the floodplain of the Upper Parana River with data collected from 81 host species.
Hydrological cycles are determinants in biological and ecological processes, and are important to the initial development of fish, especially migratory species that colonize the environment during times of flood (Lowe-McConnell, 1999). This is the case of Brycon orbignyanus, a species that performs reproductive migrations during the period from November to January, when food is more abundant. This study aimed at studying the endoparasite fauna of B. orbignyanus, which has a large potential for pisciculture, increasing the range of information to make possible its cultivation. Furthermore, according to Reis et al. (2016) among the 3.130 known freshwater fish species in Brazil, 312 are found on official list of endangered species IN 445/2014, including B. orbignyanus. This is a neotropical fish found in several South American hydrographic basins. This species has high ecological importance and is included in the list of fish threatened with extinction. From the Parana River basin, few species of parasites of B. orbignyanus were referred to this host.
Considering B. orbignyanus importance in economic and ecological scope, the hypothesis is that the size of B. orbignyanus is determinant for the composition and abundance of endoparasite fauna during periods of flood and drought. So, this study aimed to evaluate responses such as richness and abundance during different phases of the hydrological cycle. Moreover, the seasonal variation of the abundance of parasites is different during the sampling period, with an increase during the study period due to accumulation of parasites.
Material and Methods
The study area is part of the Upper Parana River floodplain (Figure 1), in the State of Parana (22[degrees]43'S and 53[degrees]10'W). Samplings were carried out in 36 environments from the Upper Parana River floodplain (including connected and isolated floodplain lakes, backwaters, rivers and channels). This floodplain site is site six within the Brazilian network of Long Term Ecological Research (LTER) sites.
Hydrological levels were obtained daily from the fluviometric station on the Parana River, at the Advanced Research Base of Nupelia, in the municipality of Porto Rico, State of Parana. Limnological data were provided by the Laboratory of Limnology, of the Research Group in Limnology, Ichthyology and Aquaculture-Nupelia, Universidade Estadual de Maringa (UEM). The hosts were caught during the sampling period, since the fish 'disappeared' from the environments sampled in the subsequent collections.
Collection of fish
Fish were caught quarterly in the period between March 2010 and September 2011. This collection was authorized by the Ethics Committee of the Universidade Estadual de Maringa (CEAE-Opinion 123/2010) and collection permission Ibama (22442-1). For sampling, gill nets of different mesh sizes were used over a period of 24 hours, with inspection every 8 hours. The sampling date, the standard length, total weight and sex of each fish were registered. The specimens are deposited in the Fish Collection of Nupelia (UEM).
Collection, fixation and conservation of endoparasites
After collecting the fish, taxonomic identification and determination of host biometric data were noted, then a longitudinal incision was made on the ventral surface of each individual fish and all organs were removed and separated. The visceral cavity and each organ were examined under a stereomicroscope to collect endoparasites. The methodology for setting endoparasites was different according to the parasite group, following the recommendations of Eiras et al. (2006). Species of endoparasites found in B. orbignyanus were identified according to Moravec (1998), Thatcher (2006), Kohn, Fernandes, and Cohen (2007), Eiras, Takemoto, and Pavanelli (2010), and specific literature.
Spearman's rank correlation coefficients ([r.sub.s]) were calculated to determine possible associations between the standard length of hosts and the abundance of infection, the relative condition factor ([K.sub.n]) and species diversity (Zar, 2010). Pearson's correlation coefficients (r) were used as an indication of the possible relationship between host total length and the prevalence of parasites, with previous arcsine transformation of prevalence data (Zar, 2010) and separation of samples of hosts into 11 standard length classes.
[K.sub.n] was calculated using the following formula: [K.sub.n] = where W / [L.sup.b] is weight, L is total length and b is the slope of the weight: length ratio, which is estimated by the equation y = [ax.sup.b] (Le Cren, 1951).
The Mann-Whitney U test was applied to test differences in infracommunity diversity of parasites between [K.sub.n] (Zar, 2010). Parasite prevalence, intensity and abundance were calculated according to Bush, Lafferty, Lotz, and Shostak (1997). The variance: mean ratio of parasite abundance (dispersion index) was used to determine spatial distribution patterns and was tested by the statistical index d. Over-dispersion or degree of aggregation was determined with Green's index (Ludwig & Reynolds, 1988). The Berger-Parker dominance index (total number of specimens of all species in the infracommunity) was calculated (Magurran, 2013). Finally, Brillouin's diversity index was calculated (Zar, 2010).
The analysis included only parasite species with a prevalence greater than 10% (Bush, Aho, & Kennedy, 1990). For a description of the structure and quantitative analysis of the parasites found, we used the parasitic indices described by Bush et al. (1997). The statistical significance level was evaluated at p < 0.05. Statistical analysis was conducted using the software Statistica 7.1 (Statsoft Inc., 2005).
Results and discussion
Out of the 104 fish examined, 72 (69.23%) were parasitized by at least one parasite species. A total of 163 endoparasites belonging to 13 species were collected (Table 1). The majority of parasite specimens collected were larvae of Contracaecum sp. (18.6%), followed by Procamallanus (Spirocamallanus) inopinatus (12.50%) and metacestodes of Monticellia spinulifera (57.69%); Dadaytrema oxycephala was the species that showed the highest mean intensity (Table 1).
Larvae of Contracaecum sp., Hysterothylacium sp., Goezia sp. and encysted Octospiniferoides sp. were found in the mesentery of juvenile individuals of B. orbignyanus.
All species of endoparasites found in this host were recorded for the first time.
In an aquatic ecosystem, fish parasite communities reflect interactions with the aquatic environment, with their hosts and with communities of invertebrates. Parasite assemblages could therefore play a potential role as environmental indicators, decreasing or increasing in diversity, richness, abundance and prevalence according to changes in environmental conditions (Kadlec, Simkova, Jarkovsky, & Gelnar, 2003).
Increases in the abundance of endoparasites in fish of larger size are attributed to cumulative occurrences of the infection process. However, in order for an infection to be established, the niches of invasive parasite forms have to overlap with the host niches (Stewart et al., 2017). For endoparasites, these processes may be linked to cumulative behavioral or trophic changes along the life of the host (Holmes, 1990). Valtonen, Marcogliese, and Julkunen, (2010) observed that omnivores presented the highest diversity of endoparasite species; this could explain the richness of the parasite fauna in B. orbignyanus, omnivore fish that have a high feeding plasticity (Hahn, Agostinho, Gomes, & Bini, 1998).
The intermediate position that B. orbignyanus holds in the food web means that its trophic parasite community is composed of both autogenic species, for example, cestodes, as well as allogeneic species, such as Contracaecum. Thus, these fish can perform the role of intermediate and/or definitive hosts. The position of the hosts within a trophic network should determine whether their fauna consists principally of parasitic helminth larvae or adults, since vulnerability to predation determines the role of an animal's predator-prey relationship (Poulin & Leung, 2011). It is known that the main food resource for B. orbignyanus is of allochthonous origin (Sgnaulin, et al., 2018), as it is an omnivorous species that feeds on plants, small fish and insects (Vaz, Torquato, & Barbosa, 2000). Therefore, these fish can participate in the life cycle of different groups of parasites as second intermediate and/or paratenic hosts, which might explain the presence of larval Octospiniferoides sp. in juveniles and adults of Octospiniferoides incognita in adult fish. Nematoda was the most prevalent group and, it is also one of the groups of parasites with the highest species richness in the study region (Takemoto et al., 2009).
The mean standard length of the fish analyzed was 17.10 [+ or -] 27.69 cm. Among the parasites that showed a prevalence exceeding 10%, a positive and significant correlation was detected between the standard length of B. orbignyanus and the abundance of P. (S.) inopinatus (r = 0.25, p = 0.008) (Figure 2). On the other hand, there was no significant correlation between the standard length of the fish and the prevalence of P. (S.) inopinatus (r = 0.56, p = 0.07). There was also no correlation between prevalence (r = -0.08, p = 0.80) and abundance ([r.sub.s] = 0.05, p = 0.558) of Contracaecum sp. larvae and the standard length of hosts.
The mean total weight of fish was 110.8 [+ or -] 491.22 g. [K.sub.n] was not different between fish parasitized and non-parasitized by P. (S.) inopinatus (Z = 0.55, p = 0.30) and Contracaecum sp. larvae (Z = 0.72, p = 0.23). [K.sub.n] showed no significant correlation with the abundance of P. (S.) inopinatus ([r.sub.s] = 0.05, p = 0.55) and Contracaecum sp. larvae (r = 0.06, p = 0.49), respectively. The lack of significant interaction between [K.sub.n] and abundances of P. (S.) inopinatus and larval Contracaecum sp. indicates that the [K.sub.n] of the fish is not affected by the parasites. Thus, we can affirm that the parasite community of B. orbignyanus causes low pathogenicity to the host. In the case of endoparasites where infection takes place via food, for example, P. (S) inopinatus, the largest fish with a high [K.sub.n] are also those most infected; this may be linked to the fact that fish that consume higher amounts of food can thus exhibit better health and also have more ingested infective forms of these parasites using the route of trophic transmission. This is more likely if the pathogenicity of the nematode in question is low. Acanthocephalans also acquired via food resources should also be considered because they are endowed with proboscis hooks that are used for fixing onto the intestinal wall of the host, causing reductions in the [K.sub.n] of fish. However, the present study was not able to detect considerable damage due to low abundance.
The parasite P. (S.) inopinatus and Contracaecum sp. showed an aggregated distribution type, according to the dispersion index. It is probable that the low value of Green's index was caused by the low abundance of parasites, despite the aggregation (Table 2).
The aggregate pattern observed for the endoparasite of B. orbignyanus is considered characteristic of parasitic systems and is a function of most hosts that are parasitized by parasitic species with a low intensity or are not infected. However, in only a few hosts parasite species are present at a high intensity (Poulin, 2007; Kennedy, 2009). According to Zuben (1997), the aggregate distribution pattern acts to increase the density-dependent regulation, the abundance of both hosts and parasites, and reduce the level of interspecific competition between the parasites. These factors make the present results of great significance in commercial species, such as B. orbignyanus.
Mean infracommunity diversity correlated positively and significantly with the standard length of hosts ([r.sub.s] = 0.30, p = 0.009) (Figure 3A) and the abundance ([r.sub.s] = 0.20, p = 0.03) (Figure 3B) of endoparasites.
The nematodes found belong to three genera: Contracaecum sp., Hysterothylacium sp. and Goezia sp. The presence of these species in the larval stage may be associated with an intermediate position in the trophic web of the host. The predominant species of larvae occurring in B. orbignyanus were species with extremely low specificity, such as nematodes of the genera Contracaecum, Goezia and Hysterothylacium.
The number of species in an infracommunity reflects the number of species present in the locality, i.e. the richness of the community, as well as opportunities for infection and transmission within the locality and thus the probability of being an infected host. When comparing endoparasite diversity among individuals of B. orbignyanus, a positive relationship was found between the body size of the host and parasite species richness, corroborating the hypothesis that larger hosts support a more diverse parasite community. Often the parasite composition may be an indicator of habitat, food type, and even migratory routes of the host.
The mean Berger-Parker dominance index was 3.85 [+ or -] 0.26. Contracaecum sp. (larvae) was the predominant species, with 27 specimens (25.96% of total parasites), followed by the digenean D. oxycephala, nematodes of the species P. (S.) inopinatus and acanthocephalan Octospiniferoides sp. (larvae), resulting in high diversity (Figure 4).
Data of monthly variation of water level in the Upper Parana River floodplain with respect to the years 2010 and 2011 indicate very irregular annual cycles. The study highlights the remarkable absence of floods in the months from June to September 2010 and June 2011, with the lowest level registered in September 2011. The highest levels of the hydrometric occurred in March 2010, reaching the maximum value (approximately 5.5 m) in March 2011
Higher temperatures and hydrological levels were observed between December 2010 and March 2011, and also a greater abundance of endoparasites (Figure 5).
The mean diversity was 1.60 [+ or -] 0.73 for the year 2010 and 1.77 [+ or -] 0.86 for 2011, obtaining thus a higher endoparasite richness despite the lower abundance during this period. The dynamics of fish assemblages from of the upper Parana River was quarterly analyzed and indicated that parasite assemblage structure was predictably linked to environmental characteristics that varied along temporal and spatial scales.
In the present study, we observed a higher endoparasite abundance during episodes of high water, indicating an increased availability of intermediate hosts in those periods of the hydrological cycle. In neotropical floodplains, temperature variations are not as pronounced as in regions that present more definite alterations, demonstrating seasonal influence on the occurrence of endoparasites. Even though endoparasite species, such as Rhabdochona acuminata, P. (S.) inopinatus and Echinorhynchus briconi are being reported for the first time in B. orbignyanus, endoparasites have been found in other species of Brycon such as B. falcatus, B. melanopterus, B. cephalus, B. amazonicus and B. hilarii (Moravec, 1998).
Therefore, between the phases of the hydrological cycle, increases in species richness and diversity of endoparasites were observed (mainly nematodes). In the present study, the species richness of parasites showed no association with various host characteristics, except for the size of the fish.
Variations in species richness of parasites between hosts not only provide a good model for studies of diversification of the community but are also of great interest in the context of disease risk prediction and conservation targets. The relationships between parasite species richness and host and attributes were not established, probably because of the interconnections between the different microhabitats during the period of high water levels that minimize the heterogeneity of the ecosystem and its biota. All parasite species found in B. orbignyanus were recorded for the first time in this host, especially in the Upper Parana River floodplain.
Received on November 16, 2017.
Accepted on October 9, 2018.
We would like to thank: the Research Group in Limnology, Ichthyology and Aquaculture (Nupelia) of the Universidade Estadual de Maringa (UEM), for logistical support; the LTER project by collecting fish; the Coordenacao de Aperfeicoamento de Pessoal de Nivel Superior (CAPES) for the supply of scholarships during the course of postgraduate research; Conselho Nacional de Desenvolvimento Cientifico e Tecnologico (CNPq) for financing the LTER project. We would to thank especially the Ichthyoparasitology laboratory, Nupelia (UEM).
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Eliane da Silva Fernandes (1,2) *, Guilherme Pomaro Casali (1,3) and Ricardo Massato Takemoto (1,2,3)
(1) Laboratorio de Ictioparasitologia, Nucleo de Pesquisas em Limnologia, Ictiologia e Aquicultura, Universidade Estadual de Maringa, Av. Colombo, 5790, 87020-900, Maringa, Parana, Brazil. (2) Programa de Pos-graduacao em Ecologia de Ambientes Aquaticos Continentais, Universidade Estadual de Maringa, Maringa, Parana, Brazil. (3) Programa de Pos-graduacao em Biologia Comparada, Universidade Estadual de Maringa, Maringa, Parana, Brazil. * Author for correspondence. E-mail: firstname.lastname@example.org
Caption: Figure 1. Study area in the Upper Parana River floodplain located in the states of Parana and Mato Grosso do Sul, Brazil.
Caption: Figure 2. Correlation between abundance of Procamallanus (Spirocamallanus) inopinatus and standard length of B. orbignyanus from the floodplain of the upper Parana River, collected between March 2010 and September 2011.
Caption: Figure 3. Correlation between infracommunity richness (A), and abundance of endoparasites (B) and standard length of Brycon orbignyanus from the floodplain of the upper Parana River, collected between March 2010 and September 2011.
Caption: Figure 4. Berger-Parker dominance index for endoparasite species of Brycon orbignyanus from the floodplain of the upper Parana River, collected between March 2010 and September 2011.
Caption: Figure 5. Temperature, water level and abundance of endoparasites during the sampling period (March 2010- September 2011).
Table 1. Endoparasites of Brycon orbignyanus from the floodplain of the upper Parana River, collected between March 2010 and September 2011. Taxonomic group Parasites Prevalence (%) Acanthocephala Echinorhynchus briconi Machado 2.88 Filho, 1959 Octospiniferoides incognita Schmidt 1.92 & Hugghins, 1973 Octospiniferoides sp. (larva) 8.65 Bullock, 1957 Cestoda Monticellia spinulifera 57.69 * (metacestode) Woodland, 1935 Digenea Dadaytrema oxycephala (Diesing, 5.76 1936) Nematoda Contracaecum sp. (larva) Railliet & 18.26 * Henry, 1912 Goezia (larva) Zeder, 1800 0.96 Hysterothylacium (larva) Ward & 2.88 Magath, 1917 Ichthyouris sp. Inglis, 1962 0.96 Procamallanus (Spirocamallanus) 3.84 hilarii Vaz & Pereira, 1934 P. (S.) inopinatus Travassos, 12.50 * Artigas & Pereira, 1928 P. (S.) paraguayensis Petter, 1990 1.92 Rhabdochona acuminata Molin, 1860 1.92 Taxonomic group Parasites Mean intensity Acanthocephala Echinorhynchus briconi Machado 2.33 Filho, 1959 Octospiniferoides incognita Schmidt 1.5 & Hugghins, 1973 Octospiniferoides sp. (larva) 1.77 Bullock, 1957 Cestoda Monticellia spinulifera -- (metacestode) Woodland, 1935 Digenea Dadaytrema oxycephala (Diesing, 3 1936) Nematoda Contracaecum sp. (larva) Railliet & 1.42 Henry, 1912 Goezia (larva) Zeder, 1800 1 Hysterothylacium (larva) Ward & 1.33 Magath, 1917 Ichthyouris sp. Inglis, 1962 2 Procamallanus (Spirocamallanus) 1.25 hilarii Vaz & Pereira, 1934 P. (S.) inopinatus Travassos, 1.23 Artigas & Pereira, 1928 P. (S.) paraguayensis Petter, 1990 1 Rhabdochona acuminata Molin, 1860 1.5 Taxonomic group Parasites Mean abundance Acanthocephala Echinorhynchus briconi Machado 0.06 Filho, 1959 Octospiniferoides incognita Schmidt 0.02 & Hugghins, 1973 Octospiniferoides sp. (larva) 0.15 Bullock, 1957 Cestoda Monticellia spinulifera -- (metacestode) Woodland, 1935 Digenea Dadaytrema oxycephala (Diesing, 0.17 1936) Nematoda Contracaecum sp. (larva) Railliet & 0.26 Henry, 1912 Goezia (larva) Zeder, 1800 0.01 Hysterothylacium (larva) Ward & 0.03 Magath, 1917 Ichthyouris sp. Inglis, 1962 0.02 Procamallanus (Spirocamallanus) 0.05 hilarii Vaz & Pereira, 1934 P. (S.) inopinatus Travassos, 0.15 Artigas & Pereira, 1928 P. (S.) paraguayensis Petter, 1990 0.02 Rhabdochona acuminata Molin, 1860 0.03 Table 2. Dispersion index (DI), d statistic, Green's index (GI) and pattern of distribution of endoparasite species of Brycon orbignyanus from the floodplain of the upper Parana River, collected between March 2010 and September 2011. Parasite species DI d GI Procamallanus (Spirocamallanus) inopinatus 1.35 2.41 0.02 Contracaecum sp. (larvae) 1.64 4.12 0.02 Parasite species Distribution Procamallanus (Spirocamallanus) inopinatus Aggregate Contracaecum sp. (larvae) Aggregate
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|Author:||Fernandes, Eliane da Silva; Casali, Guilherme Pomaro; Takemoto, Ricardo Massato|
|Publication:||Acta Scientiarum. Biological Sciences (UEM)|
|Date:||Jan 1, 2019|
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