Introduction
Studies of the hematological parameters of fish are important since they provide relevant information about the animals' physiological capacity (VILJOEN; VAN VUREN, 1991; BALLARIN et al., 2004; WELLS et al., 2005), serving as a useful tool to evaluate the immunologic system (BALLARIN et al., 2004; TAVARES-DIAS; MORAES, 2004, 2007). Hematocrit, hemoglobin concentration and red blood cell size values are important indicators of the oxygen transport capacity of water, oxygen removal rate, and oxygen availability for tissues (GRAHAM et al., 1985; TAVARES-DIAS; MORAES, 2004; WELLS et al., 2005).
Hematological parameters can also provide information about the health of a given fish population, and are important indicators of changes in the environment or in the physiology of these animals (PAIVA et al., 2000a, b).
Studies have demonstrated that physiological alterations related to water quality, whether or not they are affected by pollution, are reflected in the values of one or more hematological parameters (VAN VUREN, 1986).
Hematological alterations in fish cultivated in Brazil have been characterized in Cyprinus carpio (PAIVA et al., 1997) and Piaractus mesopotamicus (TAVARES-DIAS et al., 1999a) infested by Argulus sp., in Mugil platanus infected by Trypanosoma sp., Haemogregarina, Trichodina, Monogenea, Copepods and Hirudinea (PAIVA et al., 1997); in Piaractus mesopotamicus and Leporinus macrocephalus infected by Monogenea, in Ichthyophthirius multifiliis, Trichodina sp., Piscinoodinium pillulare and Lernaea cyprinacea (TAVARES-DIAS et al., 1999b), in Oreochromis niloticus infected by Ichthyophthirius multifiliis (TAVARES-DIAS et al., 2002), and in Hoplias malabaricus infected by L3 larvae of Contracaecum sp. (CORRÊA et al., 2013).
For fish parasitized by ectoparasites such as Monogenea, environmental changes can be reflected in reproduction, physiology, survival (KHAN; THULIN, 1991) and fish population size (MACKENZIE et al., 1995; MACKENZIE, 1999; MOLES; WADE, 2001; KHAN, 2003). Kohn et al. (2007) described the effect of Gyrodactylus trairae on the surface of the body and Urocleidoides eremitus on the gills of H. malabaricus. More recently, Rosim et al. (2011) described three new species of Urocleidoides on the gills of H. malabaricus (U. malabaricusi, U. cuiabai and U. brasiliensis) and in the nasal cavity (U. naris).
Hoplias malabaricus, a fish of the Erythrinidae family, is widely distributed in South America, except in the Andes region and in the rivers of Patagonia (NAKATANI et al., 2001). This carnivorous species feeds mainly on fish, lives in lentic waters, and possesses significant resistance to low levels of oxygen (SILVANO et al., 2001).
The purpose of this study was to analyze the hematological parameters of H. malabaricus, seeking to determine whether the epidemiological indices of Monogenea are correlated with the condition factor of the fish and with environmental factors.
Materials and Methods
Seventy-six specimens of H. malabaricus (BLOCH, 1794) were captured with gillnets in two lagoons of CEPTA/ICMBio, located in municipality of Pirassununga, SP, Brazil (21° 55′ 55″ S and 47° 22′ 37″ W). One of the lagoons was fed by a spring located outside the study area. The second lagoon was created in 1983 to feed the first lagoon, and has its own spring, which is linked to the first lagoon. Because of this link, the lagoons can be considered a single water body. Fish were collected monthly from February 2008 to March 2009, alternating between the two lagoons, making a total of seven collections. Blood collection and hematological analysis were performed at the Continental Fish Hematology Laboratory (CEPTA/ICMBio). Severing the spinal cord behind the head by pitching is an effective method of killing some fish. Following this procedure, the fish were necropsied to analyze parasites on their gills. The procedures employed in this study were approved by the Ethics Committee for the Use of Animals of UNICAMP-CEUA-N°1477-1. A voucher specimen was catalogued in a scientific collection at the Zoology Museum of the State University of Campinas - UNICAMP.
After the fish were weighed and measured, 3 mL of blood was collected from the caudal vein of each fish, using a syringe containing heparin 25,000 Ul/5mL. Blood samples were used to determine hematocrit and hemoglobin concentration levels, using the methods developed by Collier (1944) and Goldenfarb et al. (1971), respectively. The erythrocyte (Er) count was performed by the indirect method (DACIE; LEWIS, 2007). The hemoglobin concentration (Hb) was determined by the cyanomethemoglobin method and microhematocrit (Hct) by blood centrifugation of the total volume of blood (5 min/12,000 rpm) in capillary tubes. The erythrocyte indices, i.e., mean corpuscular volume (MCV); mean corpuscular hemoglobin (MCH) and mean corpuscular hemoglobin concentration (MCHC) were calculated according to Dacie and Lewis (2007).
The leucocytes and white blood cells counts were performed using blood smears stained by May-Grunwald-Giemsa, according to the methods described by Dacie and Lewis (2007). Blood extensions were photographed using a Zeiss Axioplan2 photomicroscope equipped with Leica IM50 software.
Using this quantification methodology, it was possible to count the number of leucocytes, thrombocytes, and approximately 2,000 erythrocytes in each extension. The total number of leucocytes and thrombocytes was estimated from the proportion of total erythrocytes (using a Neubauer chamber), according to Hrubec and Smith (1998).
Temperature, pH, total dissolved solids (TDS) and conductivity were analyzed using multisensory equipment.
The gills were removed and placed in jars containing formalin 1:4,000 for subsequent collection of Monogenea. The collected Monogenea were fixed in formalin 4%, then stained according to Humason (1979) and mounted in Canada Balsamto study their internal structures and organs. Other specimens were clarified, and the sclerotized structures were analyzed as described by Humason (1979).
Prevalence, mean intensity and parasite abundance values were calculated according to Bush et al. (1997).
The blood parameters were subjected to Student's t-test (P<0.05) for comparison of parasitized and non-parasitized fish.
The nonparametric Spearman rank correlation was used to determine the infestation intensity and the Relative Condition Factor (Kn) of the fish. Pearson's correlation (rs) was used to observe the correlation between infestation intensity of the fish and the hematological parameters. This procedure was performed using PROC CORR (SAS INSTITUTE, 1996), considering all the Monogenea specimens regardless of genus or species. The same procedure was adopted to correlate the biometry of the fish and the frequency of Monogenea. The data were logarithmized for variation analysis and the Duncan test was applied using the PROC GLM (SAS INSTITUTE, 1996). Kn was calculated for each host, according to Gomiero and Braga (2003), using the Gnumeric 1.1 statistical program. Spearman's rank correlation was used to correlate mean intensity of infection, hematological parameters and Kn.
Results
During the collection period, the water temperature varied from 19.1 to 28.7 °C (25.4±2.9 °C), the pH ranged from 7.2 to 9.4 (8.8±0.7), electric conductivity varied from 9.3 to 40.1 µS/cm (20.0±10.7 µS/cm), and TDS was between 4.5 and 11.0 mg/L (8.0±2.6 mg/L).
The total length of the 76 analyzed fish varied from 16 to 38.5cm (25.9±5.4 cm) and the weight varied from 45 to 640 g (228.1±140.4 g). These fish were parasitized by Monogenea of the Dactylogyridae family, Urocleidoides eremitus and Anacanthorus sp. and by one unidentified species (Table 1).
Table 1. Parasitic indexes of H. malabaricus by monogenean collected on the period from February 2008 to March 2009, from Pirassununga lagoons, São Paulo State.
Monogenean | Analyzed Fishes (n) | Parasitized fishes | Prevalence (%) | Mean Intensity |
---|---|---|---|---|
Dactylogyridae* | 76 | 33 | 43.4 | 33.1 |
Urocleidoides eremitus | 76 | 33 | 43.4 | 35.5 |
Anacanthorus sp.* | 76 | 6 | 7.8 | 37.6 |
*No identified species.
Erythrocytes, thrombocytes, and leucocytes were observed in the blood extensions of parasitized and non-parasitized H. malabaricus, and were counted whenever possible. The erythrocytes of the fish were elongated and elliptical cells, with a centralized nucleus. The thrombocytes were stick cells, with the nucleus occupying practically all the cytoplasm. Leucocytes have a characteristic size, shape and color that differ from other cell types.
The mean values of the blood parameters of parasitized and non-parasitized H. malabaricus are given in Table 2.
Table 2. Variation amplitude (Ax), mean () and Standard Deviation (s) of the blood parameters of H. malabaricus parasitized and non parasitized, collected on the period February 2008 to March 2009, from Pirassununga lagoons São Paulo State.
Parameters | Parasitized fishes (n=72) | Non parasitized fishes (n=4) | ||||
---|---|---|---|---|---|---|
Ax | p | Ax | p | |||
Hct (%) | 8-75 | 29.61±13.44 | <0.0001 | 26-63 | 37.75±17.17 | <0.0001 |
Er (106µL) | 1.57-3.23 | 2.65±0.39 | 0.028 | 2.2-3.02 | 2.71±0.36 | 0.015 |
Lc (t) (µL) | 6460-74400 | 32953±16894 | 0.123 | 15150-59400 | 32072.5±19475.6 | 0.353 |
Tb (µL) | 2960-56840 | 15633±10961 | 0.982 | 5800-27300 | 15155±9023.82 | 0.005 |
Hb (g/dL) | 2.14-2.73 | 2.32±0.09 | 0.074 | 2.21-2.43 | 2.29±0.09 | 0.083 |
MCV (fl) | 28.99-388.60 | 116.78±64.94 | <0.0001 | 95.23-286.36 | 147.68±92.78 | <0.0001 |
MCH (pg) | 6.85-14.74 | 8.99±1.67 | 0.173 | 7.62-10.16 | 8.55±1.11 | 0.007 |
MCCH (%) | 2.99-31.98 | 9.33±4.16 | 0.287 | 3.55-8.78 | 6.84±2.29 | 0.035 |
Hct= Hematocrit; Er= Erithrocity; Lc(t)= Total leucocytes; Tb= Trombocity; Hb= Hemoglobin; Mean Corpuscular Volume (MCV); Mean Cellular Hemoglobin (MCH); Mean Concentration of Cellular Hemoglobin (MCCH). Statistically differ between parasitized and non parasitized by t test (P<0.05).
Pearson's correlation indicated that there was no correlation between the blood parameters/biometry of the fish and the blood parameters/intensity of Monogenea, but that there was correlation between blood parameters and some environmental factors such as temperature, TDS and conductivity (Table 3).
Table 3. Correlation values (rs) between the environmental parameters and the hematological parameters of H. malabaricus parasitized collected on the period February 2008 to March 2009, from Pirassununga lagoons São Paulo State.
Eritrogram | pH rs | p | Temperature rs | p | TDS rs | p | Conductivity rs | p | |
---|---|---|---|---|---|---|---|---|---|
Hct (%) | 29.61±13.44 | 0.19 | 0.09 | −0.48 | <0.0001 | 0.45 | <0.0001 | 0.50 | <0.0001 |
Er (106µL) | 2.65±0.39 | 0.24 | 0.03 | 0.36 | 0.001 | −0.34 | 0.002 | −0.44 | <0.0001 |
Lc (t) (µL) | 32,953±16,894 | −0.10 | 0.37 | −0.20 | 0.07 | 0.06 | 0.58 | 0.21 | 0.05 |
Tb (µL) | 15,633±10,961 | −0.10 | 0.36 | −0.26 | 0.02 | 0.49 | <0.0001 | 0.37 | 0.001 |
Hb (g/dL) | 2.32±0.09 | 0.07 | 0.52 | −0.08 | 0.44 | 0.11 | 0.30 | 0.01 | 0.94 |
MCV (fl) | 116.78±64.94 | −0.24 | 0.03 | −0.52 | <0.0001 | 0.47 | <0.0001 | 0.55 | <0.0001 |
MCH (pg) | 8.99±1.67 | −0.26 | 0.02 | −0.40 | 0.001 | 0.33 | 0.003 | 0.43 | <0.0001 |
MCCH (%) | 9.33±4.16 | 0.17 | 0.12 | 0.32 | 0.05 | −0.37 | 0.001 | −0.39 | 0.01 |
Hct= Hematocrit; Er= Erithrocity; Lc (t)= Total leucocytes; Tb= Trombocity; Hb= Hemoglobin; Mean Corpuscular Volume (MCV); Mean Cellular Hemoglobin (MCH); Mean Concentration of Cellular Hemoglobin (MCCH).
The mean Kn of the H. malabaricus specimens was 1.01, indicating healthy conditions in the studied lagoons. Only one positive correlation was found between Kn and thrombocytes (Table 4).
Table 4. Spearman rank correlation (rs) between the Relative Condition Factor (Kn) and the hematological parameters of H. malabaricus collected on the period February 2008 to March 2009, from Pirassununga lagoons São Paulo State.
Eritrogram | r s | p | |
---|---|---|---|
Hct (%) | 29.61±13.44 | 0.01 | 0.89 |
Er (106µL) | 2.65±0.39 | −0.18 | −0.01 |
Tb (µL) | 15,633±10,961 | 0.29 | −0.01 |
MCV (fl) | 116.78±64.94 | 0.09 | 0.40 |
MCCH (%) | 9.33±4.16 | 0.01 | 0.92 |
Hct= Hematocrit; Er= Erythrocyte count; Tb= Thrombocyte count; Mean Corpuscular Volume (MCV); Mean Concentration of Cellular Hemoglobin (MCCH).
Discussion
Hoplias malabaricus is a species that lives in the lower depths of lentic water with abundant aquatic vegetation, and this species is tolerant to low concentrations of dissolved oxygen (TAPHORN, 1992); SHIBATTA et al., 2002). Therefore, it can be assumed that the environmental conditions in which "traira" are found are also preferred by the parasites that cohabit with it. A recent study by Madi and Ueta (2009) demonstrated that Ancyrocephalinae (Monogenea: Dactylogyridae), a parasite of Geophagus brasiliensis, can serve as an environmental indicator. However, the authors reported higher mean intensity values than in this study.
The H. malabaricus specimens taken from the lagoons in Pirassununga, SP, Brazil showed similar hematocrit and erythrocyte values as those described by Paiva et al. (2000b) for Prochilodus lineatus and Schizodon borellii taken from the Paraná River and parasitized by Dactylogyridae and Cucullanus pinnai, although hemoglobin, MCV and MCHC concentrations were higher than in this study. These differences can probably be ascribed to the feeding habitat and physiology of these fish.
Studies have demonstrated that hematological parameters such as Hct, MCV and MCH may indicate alterations in water quality (VAN VUREN, 1986), particularly with regard to temperature, TDS, conductivity and dissolved oxygen.
The parasitized and non-parasitized fish showed no significant difference in hematological data, but a higher number of erythrocytes and hematocrit level was found in the parasitized animals. However, this slight increase differs from that reported by Montero et al. (2004). It also differs from the results reported by Paiva and Tavares-Dias (2002) for the marine fish Mugil platanus infected by Trichodina, Monogenea, Copepodes and Hirudinea, probably because this fish species was infested by parasites other than Monogenea and lived in an estuary region.
In the present study, the number of erythrocytes and conductivity were negatively correlated, reinforcing the belief that erythrocytes may be bioindicators of environmental stress (PAIVA et al., 2000a).
The function of thrombocyte cells in fish is still controversial (TAVARES-DIAS; MORAES, 2004). These cells are characteristic of birds, reptiles, amphibians and fish, and their role in blood coagulation is well described. Albeit not of the leukocyte cell lineage, the participation in inflammatory exudates and the phagocytic function of these cells have been studied extensively, and their role in the organic defense of different of animal species has been reported (DIAS; SINHORINI, 1991; MATUSHIMA; MARIANO, 1996).
Leucocytes and thrombocytes have therefore been placed in a single group and designated as blood cells for organic defense (TAVARES-DIAS et al., 1998a, b). The literature reports that the average number of total thrombocytes in freshwater teleosts may vary from 2,000 to 68,400 µL of blood (UEDA et al., 1997), while in H. malabaricus the number varies from 28,200 to 76,000 µL of blood (TAVARES-DIAS; MORAES, 2004) . The number of thrombocytes found in the present study varied from 2,960 to 56,840 µL of blood in parasitized fish and from 5,800 to 27,300 µL of blood in non- parasitized fish, which is consistent with previous studies and correlated with TDS (Table 3). However, other than this correlation, the number of thrombocytes was uncorrelated with the Monogenea infestation, confirming the absence of pathogenicity.
Parasitism by Monogenea is common in fish in natural environments, and is rarely fatal when abundance is controlled by the host's immune system (TAVARES-DIAS; MORAES, 2004). Knowledge about the host-parasite relationship and the physiological condition of fish may be helpful in controlling these parasites through the application of fish breeding methods, although the occurrence of those parasites is inevitable and may sometimes result in serious pathology.
Many parasites can live on the host without causing any damage (THATCHER, 1981). In the present study, ectoparasitism by Monogenea did not alter the hematological parameters of H. malabaricus. This is most likely due to the equilibrium between host and parasite. However, this equilibrium can be modified by any change in water quality and/or by rapid temperature fluctuations (PAIVA et al., 1997). The results of the present study were similar to those reported by Paiva et al. (1997) for Mugil platanus parasitized by Monogenea. On the other hand, Rio-Zaragoza et al. (2010) did not find a hematological response in Lutjanus guttatus, Steindachner (1869) experimentally infected with Dactylogyridae, which showed an elevated number of erythrocytes and thrombocytes. At the three levels of infection, all the erythrocyte parameters (Hct; Hb; MCV and MCHC) were increased when compared to the control group.
The analysis of Kn variations between populations and individuals may be used to demonstrate a biological characteristic, such as environmental quality and the availability of feeding resources (BOLGER; CONNOLLY, 1989), and also of the parasite species on their hosts in a natural environment (PAIVA et al., 2000a) or in confinement (TAVARES-DIAS et al., 2002). In the host-parasite relationship, it is common to observe a negative correlation between Kn and levels of parasitism. However, Lizama et al. (2004) observed a positive correlation between Kn and the abundance of some parasite species infesting Prochilodus lineatus, suggesting that larger fish with a higher Kn value can withstand higher levels of parasitism. The results of the present study corroborate this finding.
It was expected that a higher level of infestation would elicit a stress response in the host, which would be observable in its hematological parameters. However, the results of the present study demonstrated that a high intensity of monogenean infestation is apparently not reflected in hematological parameters, nor does it cause stress in parasitized fish, which could lead to the development of pathology. The present study provides useful information for the evaluation of fish physiology and the determination of ideal conditions for breeding in captivity.
Hematological parameters were found to be highly sensitive to environmental parameters, particularly with respect to the presence of Monogenea in the natural environment.
Taxonomic Summary
Host: Hoplias malabaricus Bloch (1794); Specimen deposited: (ZUEC-PIS 7302)
Parasites: Monogenea: Urocleidoides sp.; Specimen deposited: (ZUEC-PLA 22); Monogenea: Urocleidoides eremitus (Kritsky, Thatcher & Boeger, 1986); Specimen deposited: (ZUEC-PLA 23); Monogenea: Anacanthorus sp.; Specimen deposited: (ZUEC-PLA 24)
Location: Pirassununga, SP, Brazil (21° 55′ 55″ S and 47° 22′ 37″ W)
Site of infestation: Gill.