Biochemical and physiological biomarkers in Prochilodus lineatus submitted to in situ tests in an urban stream in southern Brazil
Introduction
In urban aquatic environments fish may be exposed to a myriad of substances at the same time produced by different kinds of anthropogenic activities. The exposure to two or more chemicals may result in biological reponses quantitatively or qualitatively different from that expected from the action of the chemicals alone (Rand et al., 1995). In Brazil, as in other developing countries, criteria for the classification of water courses are exclusively based on physical and chemical factors (CONAMA, 1992) and chemical analyses are normally restricted to identification of a limited range of contaminants in water, mainly metals, and provide little information concerning the presence of organic contaminants such as hydrocarbons and pesticides in water and sediment. Therefore, alternative methodologies for water quality assessment and environmental monitoring other than chemical monitoring are urgent needed (Bozzetti and Schulz, 2004).
In situ tests are useful tools in ecotoxicology, mainly because they integrate ecological relevance in toxicity testing, by incorporating field fluctuations in a cost-effective way (Castro et al., 2004). In this kind of field work, focusing on environmental quality, healthy organisms are taken to the field-site and exposed directly to the potentially contaminated environment (Stien et al., 1998, Pacheco and Santos, 1999, Parrot et al., 2000, Olsen et al., 2001, Pyle et al., 2001). Here, the actual situation is identified in the field and there is no need to extrapolate laboratory results to particular local conditions (Chappie and Burton, 1997). However, it is important to have in mind that despite providing a more realistic exposure regime, outdoor field tests do not provide more realistic concentration–response information than typically generated from laboratory tests (Graney et al., 1995).
Biological changes in fish that are related to the exposure or to the effects of contaminants are called biomarkers (Peakall, 1994) and their use has led to good results in environmental risk assessment (McCarthy and Shugart, 1990, Van der Oost et al., 2003). Prominent among these biomarkers are haematological data (Soivio et al., 1973, Sampath et al., 1993) and physiological variables, such as plasma levels of metabolites (Adams et al., 1990, DiGiulio et al., 1995) and ions (Engelhardt et al., 1981, Alkindi et al., 1996, Martinez and Souza, 2002), levels of hormones like cortisol (Hontela et al., 1996, Barton et al., 1998, Hontela, 1998, Benguira and Hontela, 2000) and biochemical variables such as detoxifying enzyme activities (Paris-Palacios et al., 2000, Teles et al., 2003, Ahmad et al., 2004). In order to make use of biomarkers its normal range of variation must be known; in other words, it is necessary to distinguish the natural variance of a given biomarker from altered values indicating stress due to contamination (Ranzani-Paiva et al., 2000, Olsen et al., 2001). In addition, the interfering effects of season on biomarkers must be elucidated, especially in tropical and subtropical regions, where interactions can be very complex (Wilhelm Filho, 1996).
In Brazil, there have been few field studies focusing on the use of native fish biomarkers as tools for water quality assessment (Wilhelm Filho et al., 2001, Winkaler et al., 2001, Martinez and Cólus, 2002, Martinez and Souza, 2002). The neotropical fish Prochilodus lineatus (Valenciennes, 1847) (=P. scrofa Steindachner, 1881), represents a well suited species to environmental monitoring as it is a bottom feeder fish which is in contact with xenobiotics in water and in sediment and also has been shown to be sensitive to variations in water quality (Mazon and Fernandes, 1999, Da Silva et al., 2004, Martinez et al., 2004).
Cambé stream and its tributaries constitute the main hydrological basin of Londrina, a city of 500,000 inhabitants in Paraná state, Southern Brazil; the Cambé crosses the entire city and is widely used for recreational purposes, despite being heavily impaired by anthropogenic activities. It receives diffuse and point source discharges of industrial, domestic and agricultural wastes since its headwaters. Previous chemical water analyses of the upper reaches of Cambé stream showed large amounts of metals, mainly lead and aluminum (Yabe and Oliveira, 1998). In addition, Winkaler et al. (2001) showed that feral fish from these upper areas present impaired health and more recently, Lemos et al. (2005) demonstrated that its water induces DNA damage, detected by comet assay.
Thus, the objectives of the present study were to verify the suitability of a short-term in situ test with Prochilodus lineatus and to evaluate from a set of biochemical and physiological biomarkers the ones which could work as sensitive tools for the assessment of the environmental quality of Cambé stream.
Section snippets
In situ tests
Juveniles of P. lineatus (Characiformes, Prochilodontidae) weighing 28.6 ± 0.8 g (mean ± S.E., n = 53) were obtained from the University Hatchery Station. In situ tests were performed in the winter of 2002 (August and September) and summer of 2003 (February and March) at three sites on the upper part of Cambé stream, with strong anthropogenic influence, and at a reference site on the Apertados stream (Fig. 1). This stream is away from the urban area, present a well preserved riparian forest and is
Water analysis
Physical and chemical data on the water, obtained at the sampling-sites in each season, are given in Table 1. DO was higher than 5 mg O2 L−1 in both seasons and the pH stayed close to 7. The conductivity at all the sites on the Cambé was higher than that at the reference site, being everywhere above 100 (μS cm−1). Concentrations of sulphate, phosphate, nitrite and nitrate were all found to be raised at sites B and C, in comparison with site A.
Hemoglobin content (Hb)
The fish in the study had an average blood hemoglobin
Discussion
Physical and chemical variables are essential in the assessment of water quality and they provide important information on the alterations that may occur as the season changes. The temperatures and rainfall presented here varied as expected in subtropical climate: all sites were hotter and wetter in summer than in winter, on average. The reference site, in relation to the ones along Cambé stream, showed lower value of conductivity, higher value of DO and a constant value of pH, which indicate
Conclusions
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Amongst the variables analyzed here, glycemia, interrenal cell size and GST activity were best able to distinguish between the most pollution-affected sites and the reference.
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Considering the number of variables that exhibited alterations with respect to reference-site values and its location, downstream of the other sites, site C showed to be the most impaired site on the Cambé stream.
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Considerable refinement of some handling techniques used during sampling will be necessary if the resulting
Acknowledgments
This study was supported by grants from the Brazilian research funding institutions CNPq and Araucária Foundation to C.B.R. Martinez. The authors are grateful to the Universidade Estadual de Londrina Hatchery Station (EPUEL) for supplying the fish and to Dr Marisa N. Fernandes and Ms. Guilherme H. D. Pinheiro for help in the cortisol assay. M.M.P.Camargo thanks CAPES for the scholarship.
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2021, Environmental PollutionCitation Excerpt :In addition, the accumulation of intracellular substances, mainly in fish exposed to 100 and 1000 μg L−1 of MgHP, were signs of biliary stagnation and suggests a degenerative process associated to possible obstruction of bile canaliculi. Similar features was reported in eel Anguilla anguilla L. exposed to benzo[a]pyrene and dehydroabietic acid (Pacheco and Santos, 2002) and P. lineatus submitted to in situ tests in an degraded urban stream in southern Brazil (Camargo and Martinez, 2006) and exposed to other agrochemicals as the diflubenzuron (Maduenho and Martinez., 2008; Benze et al., 2016). The nuclear alterations observed in the liver of P. lineatus exposed to higher MgHP concentration (100 and 1000 μg L−1) were probably related to increased nucleus activity, degeneration and/or genotoxicity.