Hematology, micronuclei and nuclear abnormalities in fishes from Sao Francisco river, Minas Gerais state, Brazil/Hematologia, micronucleos e anomalias nucleares em peixes do rio Sao Francisco, Estado de Minas Gerais, Brasil.
The hydrographic basin of Sao Francisco river occupies 631,133 [km.sup.2], which represent 7.4% of Brazilian territory (PAIVA, 1982) with wide and diversified ichthyofauna. Godinho (1993), Britski et al. (1988), Sato and Godinho (1999), Alves and Pompeu (2001) reported 184 species from the fish orders Clupeiformes, Characiformes, Siluriformes, Gymnotiformes, Synbranchiformes, Cyprinodontifor mes, Perciformes characterized as endemic species. The ecophysiological parameters of these fish are practically unknown, and eventually this characterizes a limitation for assessments of environmental quality through biomarkers and culture in captivity.
The application of hematology in animal research is well accepted and considered a routine procedure in diagnostic methods. In addition, knowledge of biochemical parameters is important to understanding ecological interactions and the relationship between endogenous and exogenous factors and may thus serve as an indicator of health and effects of pollutants. However, the use of these parameters is limited by the lack of knowledge of normal values to comparisons, thus the ichthyohematology is indispensable (RANZANIPAIVA; SILVA-SOUZA, 2004).
The presence of micronuclei in peripheral blood erythrocytes has been used as a biomarker of genotoxicity caused by pollutants since 70's (SCHMIDT, 1975). One of the advantages for their use is that 97% of fish blood cells are red blood cells, and only 3% are white blood cells, so this represents a high homogeneity (MITCHELMORE; CHIPMAN, 1998).
Micronuclei are results from acentric chromosome fragments or chromosomes that delay, in relation to others in their migration to the poles of the cell in anaphase (AL-SABT; METCALFE, 1995; HEDDLE, 1973; SCHMIDT, 1975). According Heddle et al. (1991) and Al-Sabti and Metcalfe (1995), micronuclei can also be formed by apoptosis, inactivation of the spindle formation and chromosome damage beyond action of physical agents. Other abnormalities in the nuclei of red blood cells have been mentioned as biomarkers of cyto and genotoxicity and thus used in a complementar analysis of the frequency of micronuclei. Studies by Ayllon and Garcia-Vasquez (2000) and Kirschbaum et al. (2009) showed this correlation indicating that nuclear abnormalities could be primary responses, i.e., prior the formation of micronuclei.
Species respond differently to environmental stimuli and in any specimens have a basal rate of formation of abnormal cells. Therefore, this knowledge may aid to choice of which specie respond significantly indicating the presence of pollutants through biomarkers.
In this context, this study aimed to determine the baseline frequency of micronuclei and nuclear abnormalities in erythrocytes of peripheral blood and describe the types of leukocytes, and erythrocytic characteristics of three tropical fish with importance for aquaculture and biomonitoring: Prochilodus argenteus Agassiz, 1829, Pimelodus maculatus Lacepede, 1803 and Myleus micans Lutken, 1875, of the rivers, Paracatu and San Francisco, at Minas Gerais State, Brazil, in two periods: summer (January) and winter (June).
Material and methods
We used three species: P. argenteus (n = 13, winter / n = 11, summer) with weight 943.0 + 359.3 g and length 37.0 + 2.0; P. maculatus (n = 21, winter / n = 11, summer) with weight and length 211.0 + 39.0 g and 23.5 + 0.5 cm respectively, and M. micans (n = 10, winter) with 430.0 + 0.14 g and 26.9 + 1.9 cm. The fish were collected in the Sao Francisco river (Tres Marias) and Paracatu river (Brasilandia de Minas), during the months of January and June.
After the capture, they were placed in containers with aerated river water and taken to the laboratory. After acclimation to reduce the stress of capture and transport, fish were anesthetized with benzocaine (3%) and we performed biometrics and blood sampling by caudal puncture with the aid of needles and syringes heparinized. With blood samples were determined: total number of erythrocytes (Er) in Newbauer chamber, hematocrit (Ht%) by the method of microhematocrit (GOLDENFARB et al., 1971) and hemoglobin (Hb) by the cianometahemoglobin method (COLLIER, 1944). We calculated the mean corpuscular volume (MCV = Ht / Er x 1000) expressed in fentoliter (fL) and mean corpuscular hemoglobin concentration (MCHC = Hb / Ht x 1000) expressed in grams per deciliter (g d[L.sup.-1]).
Slides were stained with May-Grunwald-Giensa (ROSENFELD, 1947) for differential count (percentage) and total leukocytes and thrombocytes, according to the indirect method adopted by Hrubec and Smith (1998) for determining the absolute number of each leukocyte.
The frequency of erythroblasts, micronuclei and nuclear abnormalities were estimated by counting 2000 cells in extensions. The nuclear abnormalities were grouped together irrespective of form in a single class, in accordance with the method used by Kirschbaum et al. (2009).
The Shapiro-Wilk Test for normality was performed. The results were submitted to the Student test "t" and Pearson correlation for micronuclei, nuclear abnormalities and erythrocytic variables (ZAR, 1999) was done.
The erythrocyte variables of species are in Table 1. In P. argenteus no statistical difference was found for any of the variables between the fish of the rivers Sao Francisco and Paracatu. In the Sao Francisco river the Ht value was higher during the summer. There was no statistical difference for the other indices.
The absolute number of each type of white blood cell, total leukocytes and thrombocytes are in Tables 2 and 3. In P. argenteus from Sao Francisco river, the absolute value of neutrophils and eosinophils in summer were higher than in fish from Paracatu river. Regarding seasonality, the total number of leukocytes and absolute neutrophils, monocytes, eosinophils and basophils were statistically different between the summer and winter. Significant difference statistical in the number of thrombocytes between rivers and seasons was observed.
Pimelodus maculatus from Sao Francisco river had no significant variation regarding seasonality of Ht, MCV, MCHC and Hb. The Er was significant difference statistical between the winter and summer. The leukocytes did not present significant difference statistical in the total number of leukocytes, absolute number of leukocytes and thrombocytes.
The frequency of micronuclei and nuclear abnormalities in erythrocytes are presented in Table 4. Significant difference statistical was not found in individuals of P. argenteus collected in the rivers Sao Francisco and Paracatu. The seasonality did not affect significantly the frequency of nuclear abnormalities, micronuclei and erythroblasts. In P. maculates we did not observe changes in relation to seasonality. The values observed for M. micans was similar to P. argenteus and P. maculatus.
Furthermore, we did not verify correlation between micronuclei, nuclear abnormalities, Er, VCM and erythroblasts in P. argenteus from Sao Francisco river during both periods. In the specimens from the Paracatu river we observed positive and significant correlation between MCV increase and erythroblasts. In P. maculatus there was no significant correlation for any of the erythrocyte variables with micronuclei and nuclear abnormalities in the summer. On the other hand, in winter the MCV and erythroblasts were inversely and proportionally correlated. For M. micans, micronuclei and nuclear abnormalities showed significant positive correlation. Erythroblasts were inversely correlated only with MCV.
Prochilodus argenteus, popularly known as curimata-pacu, is a fish endemic to the Basin of Sao Francisco river, economically important and appreciated by professional fishing. Moreover, is of great interest that the fish satisfactorily respond to reproductive technologies and market acceptance (SATO et al., 1996). The values of MCV in the present study were similar to those reported in Prochilodus lineatus by Ranzani-Paiva and Godinho (1985).
The values observed in Ht directly reflect the increased levels of erythropoiesis, since the Er and MCV had high values during summer. Val et al. (1992), determined in Prochilodus nigrans of Amazonian river, values lower than those registered in our study. In this way, although the fish belong to the same family, we can observe that there is an interspecific variation and influence of latitude, seasonality and physical and chemical parameters of water.
The average of erythrocytes in our study was similar to those observed by Ranzani-Paiva et al. (2000) in P. lineatus from the Parana river. The highest values of these cells in the summer may be directly related to the increase in metabolism, due to the increase in water temperature, which stimulates erythropoiesis in an attempt to increase tissue oxygenation as observed by Lecklin and Nikinmaa (1998).
The reduction in the percentage of lymphocytes in the winter has also been observed by Dexiang and Ainsworth (1991). Possibly this may be compensated by increased phagocytic capacity. According to Ellis (1981) this lymphopenia is influenced by climatic conditions, especially in the colder seasons (winter and autumn), when the production of adrenocorticotropic hormone (ACTH) and cortisol are altered. Moreover, the temperature may influence the mitogenic activity of the cells.
In P. maculatus we did not find any statistical difference in the erythrocyte indices, the absolute number of leukocytes and thrombocytes, which show low influence of seasonal factors on the hematological condition of the species. Compared with other species of the same family (Pimelodidae), as Pseudoplastystoma corruscans, Ranzani-Paiva et al. (2000) reported low values of Hb and Ht. Since then, we may observe that not always a phylogenetic connection, share certain physiological characteristics. For leukocytes, the neutrophils in P. maculatus were abundant in the summer, and similar to the found by Ranzani-Paiva and Eiras (1992).
The total number of leukocytes observed in M. micans was high when compared with other species of this family, as P. mesopotamicus, C. macropomun (TAVARES-DIAS et al., 1999a) and Brycon amazonicus (TAVARES-DIAS et al., 1999b). The total number of thrombocytes in the present study was lower than found by Tavares-Dias and Mataqueiro (2004) for P. mesopotamicus. For the immature cells, the value was lower than found by Tavares-Dias and Mataqueiro (2004) in P. mesopotamicus. The values found in this study are inedited for M. micans and can serve as basis for further studies
The thrombocytes, although the phagocytic issue is discussed in teleosts, this activity had been found in cartilaginous fish by Walsh and Luer (1998). Suzuki (1986) observed pseudopods in thrombocytes of Oncorhynchus mykiss indicating phagocytosis. Besides that, Veiga et al. (2000), in cytochemical studies, observed the presence of glycogen in the cytoplasm of Salminus maxillosus, and Nakaghi et al. (1995) observed the presence of peroxidase in P. mesopotamicus. In this context, we suggested a dual function for the thrombocytes, phagocytic and aggregatory, helping to control homeostasis (STOSKOPF, 1993; MATUSHIMA; MARIANO, 1996; MARTINS et al., 2006).
In the present study the variation in erythrocyte indices does not allow attributing to pollution, but the increase in MCV is indicative of stress including that caused by pollutants. In this way, some of the high values comparing to other studies may, in principle, be attributed to seasonality.
Correlation between micronuclei and nuclear abnormalities show that each morphological change may be the manifestation from micronucleus in erythrocyte of M. micans. In the other species we not found any correlation between the frequency of micronuclei, nuclear abnormalities, erythroblasts and erythrocytes. Al-Sabti and Metcalfe (1995) report that, under experimental conditions, the frequency of micronuclei in erythrocytes is highly dependent on the levels of hematopoiesis. However, there was no correlation between the increase of erythrocytes and erythroblasts with micronuclei.
In relation to nuclear abnormalities in erythrocytes, there are few explanations for that, in fact, its origin is confirmed. Among the most accepted, we highlight the study by Shimizu et al. (1998). These authors demonstrated that the cell to detect an affected region began a process of repair and elimination of chromatin. The affected part is then moved to the periphery of the nucleus and eliminated by exocytosis. Thus, prior the complete elimination, the nuclear membrane may present imperfections, characterizing the nuclear abnormalities.
The finding of higher number of nuclear abnormalities in micronuclei indicates that the mechanism of exocytosis can be interrupted; not being very efficient, because frequently it cannot eliminate completely the fragment inside the nucleus, remaining in the periphery of nuclear membrane. Other indicium may be the evidence of oxidative stress induced by an environmental tensor. Thus, in oxidative stress, one of the first targets is the membranes that, by having its permeability and selectivity altered by lipid peroxidation, becoming the nucleus more susceptible and, therefore, might to form nuclear abnormalities and micronuclei, respectively.
From the results obtained, it is expected that eventually the hematological values may contribute to assess the effects of pollutants and can be used to monitor environmental quality in rivers and captivity.
The frequency of micronuclei and nuclear abnormalities found was not significantly different between sampling periods and between rivers Sao Francisco and Paracatu, however, the highest values were found in summer. This possibly can be attributed to increased metabolism and consequent formation of endogenous metabolites that can make the membranes more permeable and susceptible to physical and chemical agents. Furthermore, we observed a positive correlation between the increase of micronuclei and nuclear abnormalities in M. micans. This data about frequency of micronuclei, nuclear abnormalities and erythroblasts are unprecedented for these species and may serve as basic data for the adoption of these biomarkers in studies of environmental pollution.
To Andrea Senatore Grillo, Mariangela Macchione and Silvia Vicente for the manuscript review and suggestions to this investigation, to
the anonymous reviewers, whose suggestions improved the article.
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Received on May 20, 2009.
Accepted on August 13, 2009.
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Robson Seriani (1) *, Maria Jose Tavares Ranzani-Paiva (1), Angela Teresa Silva-Souza (3) and Silvia Roseli Napoleao (1,2)
(1) Laboratorio de Patologia de Organismos Aquaticos, Instituto de Pesca, Av. Francisco Matarazzo, 455, 05001-900, Sao Paulo, Sao Paulo, Brazil. (2) Programa de Pos-graduacao em Aquicultura e Pesca, Instituto de Pesca, Sao Paulo, Sao Paulo, Brazil. (3) Departamento de Biologia Animal e Vegetal, Universidade Estadual de Londrina, Londrina, Parana, Brazil. *Author for correspondence. E-mail: firstname.lastname@example.org
Table 1. Erythrocytic variables of P. argenteus, P. maculatus and M. micans of the Sao Francisco and Paracatu rivers, Minas Gerais State, where (*) indicates statistical difference (p < 0.05). Summer River Species Erythroblasts (2000 cells) S. Francisco P. argenteus 2.7 [+ or -] 2.2 Paracatu P. argenteus 1.6 [+ or -] 1.4 S. Francisco P. maculatus 2.1 [+ or -] 2.0 Winter River Species Erythroblasts (2000 cells) S. Francisco M. micans 2.6 [+ or -] 9.3 S. Francisco P. argenteus 3.8 [+ or -] 4.5 S. Francisco P. maculatus 2.1 [+ or -] 2.0 Summer River Hematocrit (%) Erythrocytes ([10.sup.6] uL) S. Francisco 42.7 [+ or -] 3.0 ** 217.7 [+ or -] 38.3 Paracatu 38.4 [+ or -] 6.8 218.9 [+ or -] 57.7 S. Francisco 45.0 [+ or -] 5.0 257.8 [+ or -] 53.62* Winter River Hematocrit (%) Erythrocytes ([10.sup.6] uL) S. Francisco 32.9 [+ or -] 7.4 126.1 [+ or -] 36.5 S. Francisco 35.4 [+ or -] 5.4 198.6 [+ or -] 42.0 S. Francisco 40.0 [+ or -] 2.0 200.8 [+ or -] 23.6 Summer River Hemoglobin MCV (fL) (g [dL.sup.-1]) S. Francisco 8.9 [+ or -] 1.2 212.0 [+ or -] 38.0 Paracatu 8.5 [+ or -] 1.6 212.0 [+ or -] 188.3 S. Francisco 9.1 [+ or -] 1.2 205.6 [+ or -] 57.4 Winter River Hemoglobin MCV (fL) (g [dL.sup.-1]) S. Francisco 7.1 [+ or -] 1.7 279.0 [+ or -] 102.4 S. Francisco 16.1 [+ or -] 2.1 186.8[+ or -] 5.4 S. Francisco 9.6 [+ or -] 1.2 * 206.0 [+ or -] 57.4 Summer River MCHC (g [dL.sup.-1]) S. Francisco 21.0 [+ or -] 2.3 Paracatu 22.3 [+ or -] 3.2 S. Francisco 20.2 [+ or -] 2.5 Winter River MCHC (g [dL.sup.-1]) S. Francisco 21.5 [+ or -] 2.1 S. Francisco 45.7 [+ or -] 28.5 S. Francisco 20.3 [+ or -] 2.3 * = difference from the same specimen, ** = sazonal difference. Table 2. Absolute number of lymphocytes, neutrophils, monocytes, eosinophils and basophils of P. argenteus, P. maculatus and M. micans from Sao Francisco and Paracatu rivers, Minas Gerais State, where (*) indicates statistical difference (p < 0.05). Summer River Species Lymphocytes ([micro]L) S. Francisco P. argenteus 11234.7 [+ or -] 7056.2 Paracatu P. argenteus 6638.6 [+ or -] 7268.7 S. Francisco P. maculatus 8558.1 [+ or -] 3468.32 Summer River Neutrophils ([micro]L) Monocytes ([micro]L) S. Francisco 17767.6 [+ or -] 1783.1 [+ or -] 7771.8 *,** 797.8 *,** Paracatu 10451 [+ or -] 1948.4 [+ or -] 6679.0 1193.0 S. Francisco 19961.4 [+ or -] 1846.0 [+ or -] 13329.0 691.9 Summer River Eosinophils ([micro]L) Basophils ([micro]L) S. Francisco 1081.8 [+ or -] 2073.6 [+ or -] 707.3 *,** 2013.7 *,** Paracatu 378.7 [+ or -] 2083.2 [+ or -] 436.1 3418.0 S. Francisco 7.7 [+ or -] 43.6 [+ or -] 2.5 63.83 Winter River Species Lymphocytes ([micro]L) S. Francisco M. micans 10192.7 [+ or -] 7056.2 S. Francisco P. argenteus 7610.3 [+ or -] 4184.1 S. Francisco P. maculatus 13214.5 [+ or -] 11648.4 Winter River Neutrophils ([micro]L) Monocytes ([micro]L) S. Francisco 929.7 [+ or -] 1332.5 1163.5 [+ or -] 1113.0 S. Francisco 4179.3 [+ or -] 3259.6 447.7 [+ or -] 286.7 S. Francisco 1625.1 [+ or -] 964.4 10807.4 [+ or -] 10130.3 Winter River Eosinophils ([micro]L) Basophils ([micro]L) S. Francisco 1565.8 [+ or -] 1354.2 302.6 [+ or -] 754.7 S. Francisco 313.3 [+ or -] 540.1 323.3 [+ or -] 519.7 S. Francisco 669.1 [+ or -] 920.5 34.52 [+ or -] 56.78 * = difference from the same specimen, ** = sazonal difference. Table 3. Total number of leukocytes and thrombocytes of P. argenteus, P. maculatus and M. micans from Sao Francisco and Paracatu rivers, Minas Gerais State, where (*) indicates statistical difference (p < 0.05). Summer River Species Leukocytes ([micro]L) S. Francisco P. argenteus 34012 [+ or -] 14661 ** S. Francisco P. maculatus 30584 [+ or -] 15465 Winter S. Francisco P. argenteus 18175 [+ or -] 8530 S. Francisco P. maculatus 13214 [+ or -] 11648 S. Francisco M. micans 14742 [+ or -] 9340 Summer S. Francisco P. argenteus 20412 [+ or -] 14661 Paracatu P. argenteus 21610 [+ or -] 15109 Summer River Thrombocytes ([micro]L) S. Francisco 17767.6 [+ or -] 7771.8 *,** S. Francisco 19961.4 [+ or -] 13329.0 Winter S. Francisco 5440 [+ or -] 2484 S. Francisco 14571 [+ or -] 11314 S. Francisco 12948 [+ or -] 7192 Summer S. Francisco 11165 [+ or -] 10119 Paracatu 13735 [+ or -] 22001 Table 4. Frequency of micronuclei and nuclear abnormalities in peripheral blood erythrocytes of P. argenteus, P. maculatus and M. micans deriving from the rivers Sao Francisco and Paracatu, Minas Gerais State. Summer River Species Micronuclei 2000 cells) S. Francisco P. argenteus 0.7 [+ or -] 0.4 Paracatu P. argenteus 0.2 [+ or -] 0.1 S. Francisco P. maculatus 0.1 [+ or -] 0.04 Winter S. Francisco M. micans 0.7 [+ or -] 0.3 S. Francisco P. argenteus 0.2 [+ or -] 0.1 S. Francisco P. maculatus 0.1 [+ or -] 0.04 Summer River Nuclear Abnormalities (2000 cells) S. Francisco 3.8 [+ or -] 1.5 Paracatu 1.0 [+ or -] 0.4 S. Francisco 0.6 [+ or -] 0.2 Winter S. Francisco 3.8 [+ or -] 1.5 S. Francisco 1.0 [+ or -] 0.4 S. Francisco 0.6 [+ or -] 0.2