Rev Bras Parasitol Vet
Revista Brasileira de Parasitologia Veterinária
Rev. Bras. Parasitol.
Vet.
0103-846X
1984-2961
Colégio Brasileiro de Parasitologia Veterinária
A hematologia é uma importante ferramenta para patologia e
diagnóstico. O presente estudo teve como objetivo descrever os parâmetros
hematológicos de 76 espécimes de Hoplias malabaricus, coletados
em duas lagoas, associados ao parasitismo por monogenético. Os parâmetros
hematológicos foram: contagem de eritrócitos (Er), micro hematócrito (Hct),
hemoglobina (Hb), volume corpuscular médio (VCM), hemoglobina corpuscular (HCM)
e a concentração da hemoglobina cospuscular média (CHCM). Observou-se que não
ocorreram mudanças significativas nos parâmetros sanguíneos relacionados com o
parasitismo. Houve uma correlação negativa entre a temperatura da água o VCM e
Hct, com valores de rs = −0,52,
p<0,0001 e rs =
−0,48, p<0,0001, respectivamente. O valor médio entre
o fator de condição relativo foi de Kn = 1,01, indicando boas
condições e os peixes estavam saudáveis nas lagoas estudadas. Não houve
relação entre a infestação de monogeneas e os parâmetros sanguíneos, ou entre os
fatores ambientais e as monogeneas.
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.
The authors are indebted to Mr. Ricardo Afonso Torres de Oliveira, from
ICMBio (Chico Mendes Institute for Biodiversity Conservation) for his assistance, to
Dr. Maria de los Angeles Perez Lizama, from Nupélia (Limnology, Ichthyology and
Aquaculture Research Center) for her analysis and interpretation of the Condition
Factor, and to Professor Dr. Arício Xavier Linhares for his statistical analysis.
The author gratefully acknowledges PROCAD (National Program of Academic Cooperation,
Brazil) for its financial support of this research.
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Financial support: CAPES
Autoria
Lincoln Lima Corrêa *Corresponding author: Lincoln Lima Corrêa,
Departamento de Biologia Animal, Instituto de Biologia - IB, Universidade
Estadual de Campinas - UNICAMP, Cidade Universitária "Zeferino Vaz", CP 6109,
CEP 13083-862, Campinas, SP, Brasil, e-mail:
lincorre@gmail.com;
lincorre@hotmail.com
Departamento de Biologia Animal, Instituto
de Biologia - IB, Universidade Estadual de Campinas - UNICAMP, Campinas, SP,
BrasilUniversidade Estadual de Campinas -
UNICAMPBrasilCampinas, SP, BrasilDepartamento de Biologia Animal, Instituto
de Biologia - IB, Universidade Estadual de Campinas - UNICAMP, Campinas, SP,
Brasil
Letícia Cucolo Karling
Laboratório de Ictioparasitologia, Núcleo
de Pesquisas em Limnologia, Ictiologia e Aquicultura - NUPéLIA, Universidade
Estadual de Maringá - UEM, Maringá, PR, BrasilUniversidade Estadual de Maringá -
UEMBrasilMaringá, PR, BrasilLaboratório de Ictioparasitologia, Núcleo
de Pesquisas em Limnologia, Ictiologia e Aquicultura - NUPéLIA, Universidade
Estadual de Maringá - UEM, Maringá, PR, Brasil
Ricardo Massato Takemoto
Laboratório de Ictioparasitologia, Núcleo
de Pesquisas em Limnologia, Ictiologia e Aquicultura - NUPéLIA, Universidade
Estadual de Maringá - UEM, Maringá, PR, BrasilUniversidade Estadual de Maringá -
UEMBrasilMaringá, PR, BrasilLaboratório de Ictioparasitologia, Núcleo
de Pesquisas em Limnologia, Ictiologia e Aquicultura - NUPéLIA, Universidade
Estadual de Maringá - UEM, Maringá, PR, Brasil
Paulo Sérgio Ceccarelli
Centro Nacional de Pesquisa e Conservação
de Peixes Continentais - CEPTA, Instituto Chico Mendes de Conservação da
Biodiversidade - ICMBio, Pirassununga, SP, BrasilInstituto Chico Mendes de Conservação da
Biodiversidade - ICMBioBrasilPirassununga, SP, BrasilCentro Nacional de Pesquisa e Conservação
de Peixes Continentais - CEPTA, Instituto Chico Mendes de Conservação da
Biodiversidade - ICMBio, Pirassununga, SP, Brasil
Marlene Tiduko Ueta
Departamento de Biologia Animal, Instituto
de Biologia - IB, Universidade Estadual de Campinas - UNICAMP, Campinas, SP,
BrasilUniversidade Estadual de Campinas -
UNICAMPBrasilCampinas, SP, BrasilDepartamento de Biologia Animal, Instituto
de Biologia - IB, Universidade Estadual de Campinas - UNICAMP, Campinas, SP,
Brasil
*Corresponding author: Lincoln Lima Corrêa,
Departamento de Biologia Animal, Instituto de Biologia - IB, Universidade
Estadual de Campinas - UNICAMP, Cidade Universitária "Zeferino Vaz", CP 6109,
CEP 13083-862, Campinas, SP, Brasil, e-mail:lincorre@gmail.com;
lincorre@hotmail.com
SCIMAGO INSTITUTIONS RANKINGS
Departamento de Biologia Animal, Instituto
de Biologia - IB, Universidade Estadual de Campinas - UNICAMP, Campinas, SP,
BrasilUniversidade Estadual de Campinas -
UNICAMPBrasilCampinas, SP, BrasilDepartamento de Biologia Animal, Instituto
de Biologia - IB, Universidade Estadual de Campinas - UNICAMP, Campinas, SP,
Brasil
Laboratório de Ictioparasitologia, Núcleo
de Pesquisas em Limnologia, Ictiologia e Aquicultura - NUPéLIA, Universidade
Estadual de Maringá - UEM, Maringá, PR, BrasilUniversidade Estadual de Maringá -
UEMBrasilMaringá, PR, BrasilLaboratório de Ictioparasitologia, Núcleo
de Pesquisas em Limnologia, Ictiologia e Aquicultura - NUPéLIA, Universidade
Estadual de Maringá - UEM, Maringá, PR, Brasil
Centro Nacional de Pesquisa e Conservação
de Peixes Continentais - CEPTA, Instituto Chico Mendes de Conservação da
Biodiversidade - ICMBio, Pirassununga, SP, BrasilInstituto Chico Mendes de Conservação da
Biodiversidade - ICMBioBrasilPirassununga, SP, BrasilCentro Nacional de Pesquisa e Conservação
de Peixes Continentais - CEPTA, Instituto Chico Mendes de Conservação da
Biodiversidade - ICMBio, Pirassununga, SP, Brasil
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.
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.
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.
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.
table_chartTable 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**
No identified species.
76
33
43.4
33.1
Urocleidoides eremitus
76
33
43.4
35.5
Anacanthorus sp.**
No identified species.
76
6
7.8
37.6
table_chartTable 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
table_chartTable 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
table_chartTable 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
rs
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
Como citar
Corrêa, Lincoln Lima et al. Parâmetros hematológicos de|Hoplias malabaricus(Characiformes: Erythrinidae) parasitados por monogenea em lagoas de Pirassununga, Brasil. Revista Brasileira de Parasitologia Veterinária [online]. 2013, v. 22, n. 4 [Acessado 12 Abril 2025], pp. 457-462. Disponível em: <https://doi.org/10.1590/S1984-29612013000400003>. ISSN 1984-2961. https://doi.org/10.1590/S1984-29612013000400003.
Colégio Brasileiro de Parasitologia VeterináriaFCAV/UNESP - Departamento de Patologia Veterinária, Via de acesso Prof. Paulo Donato Castellane s/n, Zona Rural, , 14884-900 Jaboticabal - SP, Brasil, Fone: (16) 3209-7100 RAMAL 7934 -
Jaboticabal -
SP -
Brazil E-mail: cbpv_rbpv.fcav@unesp.br
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