Metazoan parasites of Plagioscion squamosissimus, an invasive species in the Tietê River, São Paulo, Brazil

Parasitas metazoários de Plagioscion squamosissimus, uma espécie invasora no Rio Tietê, São Paulo

Abstract

This study focused on the characterization and analysis of communities and infra-communities of metazoan parasites of Plagioscion squamosissimus caught in Promissão Reservoir in the Tietê River in Borborema (21°39′58”S, 49°8′49”W), state of São Paulo, Brazil. Fifty adult specimens caught by professional fishermen in March 2015 were necropsied. The fish presented an average standard length of 25.2 ± 2.2 cm and average weight of 328.82 ± 89.03 g. A total of 5,227 specimens of metazoan parasites were collected: 2,880 (55.1%) adult Diplectanum piscinarius (Monogenoidea: Diplectanidae) and 2,347 (44.9%) Austrodiplostomum compactum metacercariae (Digenea, Diplostomidae), both with 100% prevalence and mean abundance of 57.6 and 46.9, respectively. Parasite diversity was low (species richness = 2), with a Simpson index (D) equal to 0.505, and low values of Brillouin (HB = 0.687) and Margalef diversity (I = 0.117) indices. Berger-Parker’s index of dominance (p = 0.551) indicated a slight dominance of the monogenean parasite D. piscinarius. There was a positive correlation, assessed by Pearson coefficient between parasite abundance of D. piscinarius and standard length (r = 0.43) and weight (r = 0.51) of hosts.

Keywords:
Freshwater fish; South American silver croaker; parasite ecology; Austrodiplostomum compactum; Diplectanum piscinarius

Resumo

O objetivo deste trabalho foi caracterizar e analisar as comunidades e infracomunidades de metazoários parasitos de corvinas capturadas no Reservatório de Promissão, Rio Tietê, município de Borborema (21° 67′S, 49° 14′O), Estado de São Paulo. Foram examinados 50 espécimes, capturados por pescadores profissionais no mês de março de 2015, e os parasitas coletados foram quantificados, preparados e montados para identificação taxonômica e análise das comunidades de parasitos. Os peixes analisados no estudo apresentaram comprimento padrão médio de 25,2 ± 2,2 cm e peso médio de 328,82 ± 89,03 g. Foram coletados 5227 espécimes de parasitas metazoários, sendo 2880 (55,1%) Diplectanum piscinarius (Monogenoidea: Diplectanidae) e 2347 (44,9%) metacercárias de Austrodiplostomum compactum (Digenea, Diplostomidae), ambos com prevalência de 100% e abundância parasitária de 57,6 e 46,9, respectivamente. Foi encontrada baixa diversidade parasitária (riqueza de espécies=2), com índice de Simpson (D) igual a 0,505 e baixos valores dos índices de Shannon (H’=0,688) e de diversidade de Margalef (I=0,177). O índice de dominância de Berger-Parker (d=0,551) indicou uma leve dominância do monogenético D. piscinarius. Houve correlação positiva intermediária, avaliada pelo coeficiente de Pearson, entre a abundância parasitária de D. piscinarius e comprimento padrão (r=0,43) e peso (r=0,51) dos hospedeiros.

Palavras-chave:
Peixe de água doce; corvina; ecologia parasitária; Austrodiplostomum compactum; Diplectanum piscinarius

Introduction

Fish parasites are considered good models to study parasite ecology because it is easy to obtain replicas and to count all the members of these parasitic communities (ROHDE et al., 1995). In recent decades there has been a considerable increase in studies focusing on parasites and other aquatic pathogens, especially those that affect hosts with breeding and commercialization potential, given the significant increase in aquaculture in Brazil and worldwide (LUQUE, 2004).

It is important to study parasite biodiversity because these organisms play an important ecological role such as regulating the abundance or density of host populations, stabilizing food chains and structuring animal communities. Thus, adequate knowledge of parasite diversity is crucial for environmental management and conservation (LUQUE & POULIN, 2007).

The analysis of fish parasite communities can provide important information about their hosts as well as the environment. Areas subjected to environmental impacts can cause changes in the population dynamics of fauna, especially of ichthyic fauna, which directly influences the populations of parasites as well as the prevalence and size of their infrapopulations (PAVANELLI et al., 2004).

The South American silver croaker Plagioscion squamosissimus (Heckel, 1840) (Osteichthyes: Sciaenidae) is native to the Amazon, Magdalena, Orinoco, and Essequibo Basins and also to the rivers of Guyana (CASATTI, 2003). This species was introduced in the state of São Paulo through the Pardo River, where it successfully established itself and spread to the Grande River. In 1972, this fish species made its way to the reservoirs of Ilha Solteira and Jupiá in the Paraná River, from where it reached the Tietê River. Currently, it is scattered throughout the Tietê River reservoir system (AGOSTINHO et al., 2005) and has gained relevant economic importance for local fishermen (CRUZ et al., 1990). Studies on the diet of the species characterize it as carnivorous, feeding preferentially on fish and shellfish (HAHN et al., 1999).

Various studies have reported 23 parasitic species in the South American silver croaker, including one cestode (WOODLAND, 1935), two digenetic (THATCHER, 1979; KOHN et al., 1995), 12 monogeneans (KRITSKY & THATCHER, 1984; MARTINS et al., 2000a; KRITSKY & BOEGER, 2002; BOEGER & KRITSKY, 2009), two acanthocephalans (THATCHER, 1980; MELO et al., 2015), four nematodes (MORAVEC et al., 1993; MARTINS et al., 2000b; TAVARES et al., 2007) and two copepod crustaceans (AMADO & ROCHA, 1996; THATCHER, 1998). Most of these studies were conducted in the Amazon and Paraná basins.

Several studies of fish parasites have been carried out in the Tietê River basin, most of which have reported only the occurrence of Austrodiplostomum compactum metacercariae (NOVAES et al., 2006; PAES et al., 2010a, b; ZICA et al., 2010). However, despite the economic and ecological importance of this river, parasitological studies remain scanty. Therefore, the objective of this study was to characterize and analyze communities and infracommunities of metazoan parasites of P. squamosissimus in Promissão Reservoir, in the Tietê River.

Material and Methods

Study area

This study was conducted in Promissão Reservoir (21°39′58”S, 49°8′49”W) in the Tietê River, located in the municipality of Borborema, state of São Paulo (Figure 1). The Tietê River divides the state of São Paulo in half, crossing it from east to west, and is fully inserted in the politicogeographical limits of the state (SMITH et al., 2002). It is abundant in fish in its middle and lower courses, where professional and amateur fishing are common. The course of the Tietê River follows an east-to-west direction towards the capital, and then changes direction towards the northwest (MARUYAMA et al., 2010).

Figure 1
Location of the fishing area (21°39′58”S, 49°8′49”W) of this study in the Tietê River.

For this study, 50 adult South American silver croakers were captured by professional fishermen using artisanal fishing nets. The fish were sedated in a benzocaine bath (1:500 v/v) and then killed by medullary section. Each fish was wrapped individually, placed on ice and transported to the laboratory. Biometrics and taxonomic identification were performed as described by Casatti (2005). The specimens had an average standard length of 25.2 ± 2.2 cm and weighed 328.82 ± 89.03 g.

Parasitological methods

For the parasitological analysis, mucus was scraped from the surface of the body and gills for microscopic inspection. Body surface, fins, nostrils, mouth, eyes, and the inner side of the membrane seals were carefully inspected for the presence of ectoparasites. The nostrils and mouth were washed with saline solution (sodium chloride 0.9%) applied under pressure using wash bottles. The eyes were excised and washed in saline solution. Next, the gills were removed and left gill was soaked in a formalin solution (1:4000) for two hours, then vigorously shaken. All the washing contents were individually placed in Petri dishes for stereomicroscopic evaluation. Evisceration was performed to examine the coelomic cavity. To collect the parasites, the organs were separated, placed in Petri dishes and examined under a stereomicroscope. Cuts were made in the muscles to search for encysted parasites. All the external and internal pathological findings were described in the necropsy record of each fish specimen.

The collected parasites were preserved in 5% formalin solution and prepared in temporary mounts as described by Ergens (1969) and Eiras et al. (2006). Taxonomic identification was done as described by Kritsky & Thatcher (1984) and Kohn et al. (1995). Vouchers were deposited in the Helminthological Collection of the Oswaldo Cruz Foundation (CHIOC/Fiocruz).

Histopathology

Samples of eyes and gills were collected and immediately fixed in 10% buffered formalin. The material was processed after performing routine methods, with cross sections 4 μm and stained with Hematoxylin/Eosin. Images were recorded with a Olympus BX-51 microscope equipped with an Olympus Q-Color 3 digital camera.

Ecological methods

The total number of each parasite species was determined by total counting. The indices of prevalence of infestation, average intensity and average abundance were calculated for the parasite species found in the fish, using the ecological terminology employed by Bush et al. (1997). To analyze the infracommunities, the following parameters were determined according to Magurran (2004): species richness, Margalef diversity index (I), Berger-Parker dominance index (d), Brillouin index (HB) and Simpson index (D).

Statistical analyses

The effects of length and weight of the hosts were evaluated using the Pearson correlation coefficient and Spearman rank correlation coefficient (ZAR, 1996). Prior to the statistical analysis, the data normality was assessed with the Kolmogorov-Smirnov test at a 5% level of significance. Comparisons were made of the homoscedastic data using Pearson’s correlation coefficient (r) and of the heteroscedastic data using Spearman’s rank correlation coefficient (rs).

Ethical aspects

All the procedures employed in this study were approved by the Ethics Committee on Animal Use of FCAV/UNESP under Protocol no. 10955/14 and by the Chico Mendes Institute for Biodiversity Conservation – ICMBio (SISBIO 44747).

Results

All the South American silver croakers of this study were parasitized. A total of 5,227 metazoan parasite specimens were collected, with an average of 104.54 parasites/fish, comprising 2,880 (55.1%) monogeneans Diplectanum piscinarius, and 2,347 (44.9%) Austrodiplostomum compactum digenetic metacercariae. Table 1 lists the prevalence, intensity range, mean intensity and mean abundance of each of the parasite species, in addition to the infection sites.

Table 1
Indicators of parasite infection observed in South American silver croakers collected in the Promissão Reservoir, Tietê River, SP, Brazil.

Parasite	Prevalence (%)	Intensity Variation	Mean Intensity	Mean Abundance	Site of Infection
Monogenea Diplectanum piscinarius	100	6-172	57.6 ± 33.2	57.6 ± 33.2	gills
Digenea Austrodiplostomum compactum (metacercariae)	100	2-206	46.9 ± 46.8	46.9 ± 46.8	eyes

Austrodiplostomum compactum (Lutz, 1928)

(Digenea: Diplostomidae; CHIOC 38102)

The metacercariae found in the eyes of P. squamosissimus (Figure 2) presents an elongated, dorsoventrally flattened, foliaceous body, slightly concave on the ventral side and convex in the anterior region. The posterior region features a small conical protuberance of varied size. The subterminal oral sucker is flanked by two pseudo-suckers. The pharynx is oval, the esophagus is short, and glandular cells are visible in most of the anterior region of the metacercariae. Small, underdeveloped gonads are visible close to the oval tribocytic organ. The intestinal ceca extend towards the posterior region and the acetabulum is small. Table 2 compares the characteristics observed in this study with data reported by other authors.

Figure 2
Semi-permanent Hoyer mounting of Austrodiplostomum compactum, stained with Mayer’s Carmalumen. BAR=200 µm.

Table 2
Morphometric data of Austrodiplostomum compactum metacercariae obtained from South American silver croakers collected in the Promissão Reservoir, Tietê River, São Paulo, and measurements reported by other authors.

Authors	Body		Oral sucker		Pharynx		Tribocytic Organ
	length	width	length	width	length	width	length	width
Kohn et al. (1995) *	1,470-2,740 (2,170)	600-1180 (970)	41-97 (77)	56-116 (79)	64-94 (83)	45-79 (60)	326-650 (507)	251-500 (370)
Santos et al. (2002) *	880-1,840 (1,434)	400-792 (611)	44-90 (65)	40-64 (52)	50-64 (62)	40-60 (49)	200-600 (285)	160-232 (182)
Novaes et al. (2006) *	1,584-1,947 (1,800)	537-709 (642)	45-83(59)	54-77 (68)	53-73 (61)	50-64 (56)	422-434 (428)	220-319 (258)
Yamada et al. (2008) *	680-1,190 (1,037)	310-1010 (568)	19-60 (46)	29-60 (50)	36-96 (60)	14-55 (40)	91-324 (236)	85-228 (152)
Paes et al. (2010a) *	1,301-2,386 (1,911)	482-854 (678)	51-87 (71)	51-92 (73)	49-84 (69)	45-74 (58)	205-554 (401)	127-347 (246)
Zica et al. (2010) *	1,342-2,007 (1,708)	481-711 (601)	41-81 (59)	47-89 (67)	51-99 (72)	35-66 (51)	348-460 (400)	91-199 (145)
Present Study*	1,450-2,166 (1,789)	566-902 (683)	57-86 (72)	49-97 (76)	61-99 (80)	41-75 (58)	302-492 (405)	193-319 (256)

• ^*
  Measurements in µm, mean values in parenthesis.

Diplectanum piscinarius Kritsky and Thatcher, 1984

(Monogenoidea: Diplectanidae; CHIOC 38103)

These monogeneans (Figure 3) have an elongated body, poorly developed cephalic lobes, with four ocelli, a subovate squamodisc, a wide and elongated peduncle, a haptor with similar hooks, two pairs of non-similar anchors, a ventral bar with long tapered ends marked by an anteromedial constriction and absence of posteromedial projection, and a long dorsal bar with medial termination. The copulatory complex is funnel-shaped, lacking an accessory piece. Table 3 describes the morphometrics observed in this study.

Figure 3
Semi-permanent ammonium picrate-glycerin mounting of Diplectanum piscinarius. BAR=100 µm.

Table 3
Morphometric data of Diplectanum piscinarius obtained from South American silver croakers collected in the Promissão Reservoir, Tietê River, SP, Brazil, in comparison to literature.

		Authors
		Kritsky & Thatcher (1984) *	Present Study *
Number of specimen		13	25
Body	length	537-869 (728)	599-928 (762)
	width	69-98 (86)	76-135 (103)
Haptor	length	81-92 (86)	80-103 (82)
	width	191-228 (206)	212-262 (237)
Ventral Anchor	length	66-77 (71)	67-78 (72)
Dorsal Anchor	length	59-68 (64)	60-68 (63)
Ventral Bar	length	77-91 (84)	84-104 (93)
Dorsal Bar	length	76-97 (88)	88-107 (96)
Complex Copulatory organs	length	20-26 (23)	24-33 (29)

• ^*
  Measurements in µm, mean values in parenthesis.

Ecological indicators

A species richness of 2 was observed, and low species diversity was evidenced by a high Simpson (D = 0.505) index and low Brillouin (HB = 0.687) and Margalef diversity (I = 0.117) indices. The Berger-Parker dominance index (d) was 0.551, indicating a slight dominance of D. piscinarius.

Host-parasite relationship

Diplectanum piscinarius specimens were found in some histological sections of the gills. The main lesions observed were epithelial hyperplasia of primary and secondary gill lamellae, dilation of central venous sinus, edema, mononuclear and eosinophilic inflammatory infiltration, expansion of secondary lamellae with congestion, detachment of the epithelial lining of the secondary lamellae, telangiectasia and total fusion of secondary lamellae. The presence of cells with pyknotic nucleus and translucent cytoplasm indicative of necrosis was also observed (Figure 4).

Figure 4
Photomicrographs of the gills. (a) Normal tissue (arrow), blood accumulation in the secondary gill lamellae (arrowhead). HE, BAR=100 µm. (b) Monogenea (M), telangiectasia (T), dilation of the central venous sinus (arrow), epithelial hyperplasia of secondary gill lamellae. HE, BAR=50 µm. (c) Epithelial hyperplasia of secondary gill lamellae (arrowhead), epithelial hyperplasia of primary gill lamellae (*), inflammatory infiltration. HE, BAR=50 µm. (d) Presence of cells with pyknotic nucleus and translucent cytoplasm indicative of necrosis, detail of the fixation of Monogenea (M), detachment of the epithelial lining of secondary lamellae (arrow), edema (*). HE, BAR=20 µm. (e) Intense epithelial hyperplasia of secondary gill lamellae. HE, BAR=100 µm. (f) Total fusion of secondary lamellae (arrow). HE, BAR=100 µm.

No damage associated with parasitism by A. compactum was found in the eyes, despite the presence of the parasite in the histological sections (Figure 5). Macroscopically, 34 of the South American silver croakers showed lens opacity in at least one eye, although there were no histopathological signs of cataracts.

Figure 5
Photomicrograph of a fish eye. Presence of the digenetic parasite (D), optic nerve (N) and retina (R). HE, BAR=500 µm.

Only D. piscinarius presented a positive intermediate correlation between standard length and weight and parasite abundance, presenting statistically significant differences by Pearson’s correlation coefficient (p < 0.05). For the digenetic parasites, the correlation between standard length and weight and parasite abundance was evaluated by Spearman’s rank correlation coefficient. No significant degree of correlation was found between the data (p > 0.05) (Table 4).

Table 4
Values of the Spearman rank correlation coefficient (rs) and the Pearson correlation coefficient (r).

	SL – Abundance correlation		W – Abundance correlation
	D. piscinarius	A. compactum	D. piscinarius	A. compactum
rs	-	0.1956	-	0.2279
p	-	0.1733	-	0.1114
r	0.4331*	-	0.5077*	-
p	0.0017	-	0.0002	-

• ^*
  significant values; (SL) standard length; (W) weight; p = level of significance (0.05).

Discussion

Although the literature describes several types of parasites for P. squamosissimus (WOODLAND, 1935; THATCHER, 1979; THATCHER, 1980; KRITSKY & THATCHER, 1984; MORAVEC et al., 1993; KOHN et al., 1995; AMADO & ROCHA, 1996; THATCHER, 1998; MARTINS et al., 2000a, b; KRITSKY & BOEGER, 2002; TAVARES et al., 2007; BOEGER & KRITSKY; 2009; MELO et al., 2015), low diversity and richness of parasites in South American silver croakers were observed in this study. This can be attributed to the fact that most reports refer to studies conducted in regions where the species occurs endemically. Low parasitic diversity was also found in studies carried out in places where this fish species was introduced, such as the Upper Paraná River floodplain (TAKEMOTO et al., 2009), and the Volta Grande Reservoir in the state of Minas Gerais, Brazil (MARTINS et al., 2000a, b; MARTINS et al., 2002). Other studies conducted on this fish from the Tietê River only reported the occurrence of digenetic parasites (PAES et al., 2010a, b), which were also found in this study.

Most reports on A. compactum in P. squamosissimus describe high prevalence rates, often over 90% (KOHN et al., 1995; MARTINS et al., 2002; SANTOS et al., 2002; MACHADO et al., 2005; PAES et al., 2010a,b; RAMOS et al., 2014). Thus, in view of the 100% prevalence rate and high average parasite intensity (46.9), represented by up to 206 parasites in a single host, the data obtained here are similar to the findings of other authors (KOHN et al., 1995; SANTOS et al., 2002; MACHADO et al., 2005; PAES et al., 2010a, b), confirming the parasite’s preference for croakers, as reported by Yamada et al. (2008).

With regard to D. piscinarius, Tavernari et al. (2005) reported a prevalence rate of 97% and an average intensity of 31.8 parasites per host, which is very similar to the present study. The high prevalence rate is like explained by the short life cycle of diplectanids (IANNACONE et al., 2000) and by the fact that the parasite’s eggs stick to the lining of the gills or to tegument, causing constant reinfection of the host (JARA, 1998).

The high prevalence rate of parasites found here may be ascribed to the abnormally long dry season lasting from January to October, which occurred before the completion of this study. In the first 10 months of 2014, the recorded average rainfall in the study area was 45% lower than the average in the same period in 2013 (CIIAGRO, 2015). In this study area, the rainy season usually occurs from October to April and the dry season from May to September, with an average annual rainfall of 1000 to 1300 mm (CASTRO et al., 2008). According to the National Electricity System Operator (ONS, 2015), the Promissão Reservoir was at less than one third of its net volume, ranging from 20 to 36% during practically the entire year of 2014. This low volume of water may have increased the density of the fish population, resulting in the high prevalence rates and intensities of infection observed in this study. Noteworthy to say, other parasites were not favored by the increased fish population density.

In Brazil, the first description of A. compactum was made by Kohn et al. (1995), and since then, this parasite has been reported in over 30 species, indicating low host specificity (RAMOS et al., 2014). The presence of this parasite in fish eyes can cause total or partial loss of vision, making the fish more vulnerable to predation and facilitating the parasite’s transmission to the definitive host (EIRAS, 1994).

Earlier studies have reported a positive correlation between A. compactum infection intensity and the host’s standard weight and length (MACHADO et al., 2005; PAES et al., 2010b). However, this study did not find a significant correlation between infection by this parasite and the host’s characteristics (standard length: rs=0.195, P=0.1733; weight: rs=0.2279; P=0.1114). Kennedy & Burrough (1977) stated that the host’s length and the parasite intensity of Diplostomum spp. are rarely correlated, and that in some cases there may be a negative correlation, depending on the longevity of metacercariae species. Thus, if the species’ longevity is low, new infections are offset by mortality rates of older parasites (KENNEDY & BURROUGH, 1978). In this study, the parasite intensity and/or chronicity of infection were most likely insufficient to reduce the hosts’ visual acuity to the point that would render them more susceptible to predation. As the animals of this study showed no signs of associated disease, the infection may have been recent, which would explain the absence of a correlation between infection and the host’s characteristics.

The occurrence of this parasite infecting several species of fish in different aquatic ecosystems suggests that it was introduced along with croaker fish and that it found the right conditions to develop its cycle, adapting to the new ecosystem and to the fish in it (MACHADO et al., 2005; YAMADA et al., 2008; TAKEMOTO et al., 2009). Therefore, studies regarding the impact of the infection in native fish should be developed, in order to evaluate a possible environmental impact of its introduction in new areas. Moreover, infection by diplostomids in fish may be a matter of public health concern because of their zoonotic potential (EIRAS, 1994).

Diplectanum piscinarius was first described parasitizing the gills of P. squamosissimus collected in Lake Januáca in Manaus, state of Amazonas, Brazil (KRITSKY & THATCHER, 1984). Although monogenetic parasites present a higher degree of specificity than other groups of parasites (BUSH et al., 2001), D. piscinarius has also been reported in Pachyurus bonariensis (BRAGA et al., 2014). Massive infections with this parasite may lead to hemorrhage, inflammation and hyperplasia of the gill epithelium, increased mucus production, and lamellar fusion, which are harmful to the breathing process (WOO, 2006).

Unlike A. compactum, infection by D. piscinarius showed a positive correlation between parasitic intensity and standard length (r=0.4331; P=0.0017) and weight (r=0.5077; P=0.0002) of the hosts, a finding that had not previously been reported (MARTINS et al., 2000a; TAVERNARI et al., 2005). The infestation by Diplectanum sp. in Cynoscion analis, another Sciaenidae fish, showed a positive correlation between parasite intensity and standard length of the host (IANNACONE et al., 2000). This data indicates a cumulative effect of the infection by D. piscinarius, possibly due to the larger size of the host (larger surface for parasitism) and/or longer exposure to the parasite (TAVERNARI et al., 2005).

The ecological and histopathological data obtained here indicates that the parasites and parasite intensities found in this study cause only minor injuries. However, such lesions demonstrate the pathogenic potential of these parasites, particularly of monogenean parasites.

Conclusions

This study allowed us to infer that monogenean and digenetic parasites are prevalent in the parasite community of South American silver croakers in the Promissão Reservoir, since the community comprises only D. piscinarius and A. compactum. It can also be stated that the hosts’ weight and standard length influence the intensity of parasitism by D. piscinarius in P. squamosissimus, with an intermediate positive correlation for both biometric parameters. Future studies are necessary to determine if this parasitological status will be permanent after the severe drought or if the parasitefauna will increase in diversity over the years.

Acknowledgements

The authors gratefully acknowledge the financial support of CAPES, Brazil’s Federal Agency for the Support and Improvement of Higher Education, and one of the anonymous reviewers for the valuable commentaries and suggestions.

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Publication Dates

• Publication in this collection
  Apr-Jun 2017

History

• Received
  16 Dec 2016
• Accepted
  22 May 2017