Abstract
In aquaculture conditions, severe parasitic infections cause negative impacts on fish health and economic losses. The parasite load has been associated with anemia, which reduces the number of erythrocytes in fish. Therefore, the evaluation of hematological parameters as a feasible tool for diagnosing and monitoring fish health allows us to determine the indirect effect of parasites on the health status of fish. Our aim was to evaluate changes in the blood cell parameters of Lagocephalus laevigatus associated with parasitism. A total of 99 puffer fish were collected from the coast of Seybaplaya, Campeche. Each fish had 20 µl of peripheral blood drawn, and blood smears were performed in triplicate. The smears were stained with Giemsa stain, and a quantitative analysis of blood cells (erythrocytes, leukocytes, and monocytes) was obtained with an optical microscope at 100 ×. The parasites recovered from each fish were fixed and identified, and the infection parameters were calculated. Through generalized additive model analysis (GAMLSS), we observed that the infection intensity of puffer fish influenced changes in hematological parameters, principally in erythrocytes, neutrophils, thrombocytes, the total fish length, and the condition factor of the fish. In conclusion, this is the first study that provides baseline data on the hematological parameter variations in uninfected and infected L. laevigatus, the tropical wild puffer fish, as well as the possible effects on fish health. It is necessary to establish reference hematological patterns in wild populations for diagnosis and timely management with emphasis on aquaculture fish.
Similar content being viewed by others
Avoid common mistakes on your manuscript.
Introduction
Parasitic infections are thought to be a serious underrecognized health problem in wild aquatic organisms because infection levels can lead to disease and sometimes mortality, resulting in a serious impact on ecological interactions in ecosystems. For economically important fish, these factors can affect food safety with economic and public health consequences (Giari et al. 2022). Likewise, parasitic infections can alter the health conditions of wild and farmed fish (Guidelli et al. 2011). Physiological alterations, such as anemia, in host fish are characterized by a reduced hemoglobin concentration, hematocrit level, and erythrocyte number (Witeska 2015), and this is reflected in the condition factor of fish (Ryberg et al. 2020). Hematological parameters change in infected fish due to factors such as the consumption of blood by a parasite as it feeds (Clauss et al. 2008) and activation of host defense cells (Alvarez-Pellitero 2008). For example, hematocrit reduction observed in Hemigymnus melapterus (Labridae) Bloch, 1791 is related to the presence of ectoparasites such as isopods (Gnathia sp.), which take periodic large blood meals before leaving the host to mate (Jones and Grutter 2005). Additionally, the increase in eosinophil counts in the zebrafish Danio rerio (Cyprinidae) Hamilton, 1822 infected with the nematode Pseudocapillaria tomentosa suggests an inflammatory response to the parasitic infection (Balla et al. 2010). Changes in hematological parameters have also been observed in Cyprinus carpio infected with Philometra pellucida (Kumar 2023).
Hematological disorders in fish occur under natural and aquaculture conditions, and they can be diagnosed in a timely manner by the measurement of blood cell parameters. One suitable, noninvasive, and feasible diagnostic method used to help define alterations and test health status in fish is hematologic analysis (Clauss et al. 2008; Fazio 2019; Witeska et al. 2022). Although some authors consider this method to be controversial because the counts in some species seem to have a wide range of variation (Blaxhall 1972; Blaxhall and Daisley 1973), it is commonly used to assess the welfare of some economically important aquaculture species and in veterinary practice and scientific research (Clauss et al. 2008; Fazio 2019; Witeska et al. 2022). However, while the total amount of available information on fish diversity is high, references addressing fish health and their hematological disorders are limited. Therefore, it is often difficult to identify and determine possible alterations in the hematological parameters of wild fish with aquaculture potential, especially those affected by parasitic infections during management.
The morphology and defense system of the puffer fish (Tetraodontiformes, Tetraodontidae) include inflation and the presence of tetrodotoxin (neurotoxin), which is highly toxic to humans (Isbister et al. 2002). Despite the toxic risk to humans, puffer fish are biologically and economically important in many regions, especially in Asia, where the meat is considered a delicacy (NMFS 1989, Stump et al. 2018).
Puffer fish are also considered an economically important resource in the southern Gulf of México and Pacific regions, and those with the potential for aquaculture (Chávez-Sánchez et al. 2008) include S. annulatus from the Pacific and L. laevigatus and Sphoeroides spp. from the Gulf of México, particularly from the Campeche Coast. Notwithstanding this potential, knowledge of the hematological parameters of puffer fish is scarce, including a lack of information about the blood cell parameter imbalance associated with parasitic infections.
Fajer-Ávila et al. (2011) suggested that the infection levels with the copepod Pseudochondrcanthus diceraus can be associated with changes in the hematological parameters of the puffer fish Sphoeroides annulatus from the Mexican Pacific. Usually, fish harbor more than one species of parasite (Bush et al. 1997). Therefore, it is important to consider and evaluate these interactions together with the variability in hematological parameters to establish an information base. This allows for precise diagnoses, treatment or preventive measures in wild and cultured fishes.
Consequently, the aim of this study was to assess the parasite levels in infected Lagocephalus laevigatus, a wild tropical puffer fish of the coastal zone of Campeche, Mexico, and the associated changes in blood parameters.
Materials and methods
A total of 99 L. laevigatus were collected from Seybaplaya, Campeche (19°42.580'N, 90°44.155'W) during the months of November 2020 (27 fish), January 2021 (30 fish), April 2021 (12 fish) and September 2021 (30 fish) using a line and hook. After capturing a fish, 20 µl of blood was collected from the caudal vein using a hypodermic syringe without anticoagulant and applied to glass slides to perform blood smears in triplicate for at least 3,000 erythrocytes per fish; at the same time, leukocyte and thrombocyte numbers were determined in the fields (Murray 1983; Schultz et al. 1993, Ek-Huchim et al. 2022). The smears were air dried and fixed in absolute methanol for 10 min (Al-Sabti and Metcalfe 1995). Subsequently, for blood collection, the fish were first euthanized through a brain puncture and kept on ice for a maximum of 8 h (Vidal- Martínez et al. 1998; Ek-Huchim et al. 2022). The smears and fish were transported to the Laboratory of Aquatic Parasitology of EPOMEX (Instituto de Ecología, Pesquerías y Oceanografía del Golfo de México), Universidad Autónoma de Campeche (UAC). In the laboratory, the total length (TL) in cm and weight (W) in g of each fish were measured. Next, the fish were examined under a compound stereomicroscope (Leica EZ4) to determine the presence of any parasites on the body surface. Then, all organs were removed (gills, intestines, liver, bladder, and kidney), placed in bowls with 4% formaldehyde solution, and examined under a stereomicroscope.
The methods used for fixing, staining, and clearing the parasite specimens for identification were as follows: Trematoda were stained with Gomori’s trichrome stain and Nematoda, Copepoda and Crustacea were cleared with glycerin at different concentrations (1:10, 1:5, 1:2) (Vidal-Martínez et al. 2002; May-Tec et al. 2022). The parasites were identified according to the keys of Anderson (2004), Palm (2004), Jones and Bray (2005), Ho and Lin (2004) and Lin and Ho (2006) using an Olympus microscope (DM 2500). The prevalence, mean abundance, infection intensity and mean infection intensity were determined based on methods proposed by Bush et al. (1997).
To assess the condition factor of wild L. laevigatus, the length-weight relationship (LWR) of the puffer fish was estimated using the Equation W = αSLβ (Ricker 1975), where W = total weight (g), SL = standard length (cm), α = ordinate to the origin, and β = the intercept, also known as the allometry coefficient. Based on the estimation of the LWR, the condition factor of the puffer fish was calculated according to the formula proposed by Bagenal and Tesch (1978) (K = 100 * W/SLβ).
Morphological and morphometric analysis of blood cells
The blood smears were stained with Giemsa 10% for 12 min. After being air dried, they were observed under a microscope (Olympus BX51) at 100 × magnification using immersion oil (Baršiene et al. 2004). Descriptive data were obtained by observing the shape of the cell and its nucleus, the lobulation of the nucleus, and the color of the cytoplasm, as well as the color and density of the cytoplasmic granules. Quantitative cell analysis included measurements of erythrocytes, leukocytes (lymphocytes, neutrophils, eosinophils, basophils, and monocytes), and thrombocytes, also called platelets. The parameters measured involved the long axis (LA) of each blood cell. At least 3,000 erythrocytes were analyzed per fish and were used for differential (percent) determination of leukocytes. The morphological identification of blood cells was based on the work of Conroy and Conroy (2007) and Fajer-Ávila et al. (2011).
Statistical analysis
Kruskal–Wallis (K) analysis was applied to the data to determine the existence of any meaningful difference in the mean intensity of the parasite species and size of the fish.
The statistical relationship between the infection intensity (dependent variable) and hematological parameters (independent variables) in L. laevigatus was determined using generalized additive models of location, scale, and shape (GAMLSS). These models considered the statistical distribution of each variable (e.g., exponential, Gaussian, linear, distribution, etc.) (Rigby and Stasinopoulos 2005). The multicollinearity of the independent variables was evaluated through a variance inflation factor (VIF < 4) index and Spearman’s correlation (rs > 0.70) (R Core Team 2018). The selection of the best statistical distribution was made using the Akaike information criterion (AIC) (Burnham and Anderson 2002), where the best-fitted distribution had the lowest AIC value. The best statistical model was selected using the stepGAIC function in the GAMLSS package (Rigby and Stasinopoulos 2005) in R programming language (R Core Team 2018). In addition, the power of the fit of each model was evaluated through the explained deviance (ED), expressed as a percentage (Rigby and Stasinopoulos 2005).
Results
Fish status and parasitism
We collected 99 specimens of L. laevigatus with TLs from 18.9‒48.5 cm (29.18 ± 6.53) and Ws from 87‒1562 g (449.50 ± 305.73). The highest frequency of size was observed in the class of 27‒36.9 cm (Fig. 1a). The LWR values showed a negative allometric growth of L. laevigatus (β = 2.97), and the condition factor values of L. laevigatus oscillated between 0.65 and 2.09 (1.02 ± 0.23).
A total of 554 individual parasite specimens were found on L. laevigatus, which included 19 parasite species, of which 16 spp. were endoparasites and 3 spp. were ectoparasites, with a range of infection intensities of 0‒53 individual parasites per fish. The cestode (Tetraphyllidea) had the highest prevalence at 41.17%, followed by the copepod Caligus haemulonis (Caligidae), with a prevalence of 38.23% (Table 1). The number of parasites infecting L. laevigatus were categorized into four levels: uninfected (0 parasites), 1 (1‒5 parasites), 2 (6‒14 parasites), and 3 (15‒53 parasites).
The highest infection intensity was 53 parasites per fish, and the puffer fish were 38.9 ± 7.31 cm long, and weighed 861.54 ± 400.23 g. The length of uninfected fishes was 28.58 ± 5.84 cm, and the weight was 380.75 ± 215.82 g. The infection intensity values were significantly different among different sizes of L. laevigatus (K-W (2,99) = 17.31, P< 0.05) (Fig. 1b).
Blood cell morphology
The blood cell morphologies of the puffer fish (L. laevigatus) are presented in Figure 2. Erythrocytes with a blue cytoplasm were round with compact and oval nuclei and centrally positioned, and their LA was 7.97 ± 0.75 µm in diameter (Fig. 2a). The differential count of erythrocytes was 97.46% ± 2.38% (90.50%–99.96%).
Five leukocyte types were identified in the peripheral blood of puffer fish. The lymphocytes were smaller in size and round with a 5 ± 4.57 µm diameter, and a round, purple nucleus with dense chromatin that occupied almost all of the cytoplasm was observed (Fig. 2b). The differential count was 83% ± 16.74% (7.89%–100%).
Neutrophils were the most common granulocytes found in the peripheral blood of puffer fish. Unlike the other leukocytes, the neutrophils were ovoid to rounded with a diameter of 10.5 ± 1.50 µm; the nucleus was stained purple; and the cytoplasm had a pale blue color (Fig. 2c). The differential count of neutrophils was 6.68% ± 9.16% (0%–42.85%). Eosinophils were ovoid to rounded with a diameter of 8.59 ± 0.74 µm, and unsegmented peripheral purple nuclei, and a cytoplasm with numerous reddish-orange granules were observed (Fig. 2d). The differential count of eosinophils was 3.97% ± 12.37% (0–92.10). The last type of granulocyte was basophils; these cells were ovoid with a diameter of 9.04 ± 0.92 µm, and the cytoplasm was filled with deep blue–purple stained granules with an eccentric nucleus (Fig. 2e). The differential basophil percentage was 4.24% ± 7.05% (0%‒ 36%).
Monocytes were recognized by their ovoid to rounded shape with a diameter of 11.05 ± 0.82 µm. Their cytoplasm was stained clear blue with vacuoles and a bluish-purple eccentric nucleus (Fig. 2f). The differential count of monocytes was 1.95% ± 4.33% (0% ‒ 20%).
Thrombocytes were observed as purple fragments in the blood (Fig. 2g) and commonly formed small clusters. The differential thrombocyte counts was 0.96% ± 0.71% (0%‒3.15%).
Association of blood cell parameters and infection intensity of parasites on Lagocephalus laevigatus
Infection intensities from 0 to 53 parasites per fish resulted in a significant reduction in the percentage of erythrocytes and an increase in leukocytes. There was a significant difference between the infection intensity and erythrocyte count (K-W3,68 = 30.26; P < 0.05), leucocyte count (K-W3,82= 34.26; P < 0.05), lymphocyte count (K-W3,68 = 27.04; P < 0.05), neutrophil count (K-W3,68 = 14.83; P < 0.05), eosinophil count (K-W3,68 = 17.73; P < 0.05), monocyte count (K-W3,68 = 9.4; P < 0.05), and thrombocyte count (K-W 3,68 = 23.30; P < 0.05); however, no significant difference was observed for the basophil count.
The statistical associations between the hematological parameters changed, and the infective parasite intensity of L. laevigatus was assessed through three generalized additive models for location scale and shape (GAMLSS) (Table 2). The first GAMLSS model showed that the number of individual parasites per fish was correlated with the number of erythrocytes, neutrophils, and thrombocytes, TL, and the condition factor, and this correlation had a 60% overall contribution to the explained deviance (ED). The second GAMLSS model showed that the number of individual ectoparasites per fish was correlated with the number of erythrocytes and thrombocytes, the total length, and the condition factor, which had a 57% contribution to the ED (Table 2). The last model showed that the number of individual endoparasites per fish was correlated with the neutrophil count and the total length, which had a 46% contribution to the ED (Table 2).
Discussion
The host-parasite interaction triggers the activation of different blood cells as lines of defense (Holzer et al. 2021). The variability in fish blood cell parameters (i.e., variation in the cell type composition) is an efficient and sensitive tool for assessing the health of wild and cultured fishes, providing key insights regarding their physiological status reflected by the condition factor as well the damage by parasitic infections (Omar et al. 2021). Our findings indicate that variation in the blood cell parameters of the wild puffer fish L. laevigatus of the Campeche Coast was associated with infective parasite levels, i.e., blood cell parameters of uninfected and infected puffer fish were significantly different. However, authors such as Marcogliese (2002), Lafferty et al. (2006), and Dunne et al. (2013) have mentioned that parasitized wild fish represent a healthy ecosystem in which a proper host-parasite interaction of the food web occurs. High levels of infection can cause important diseases in both wild (Barzegar and Jalali 2009) and farmed fish (Jithila and Prasadan 2019; Buchmann 2022; Nguyen et al. 2021). Our work is the first study on the hematological values of L. laevigatus and their parasites, and this study revealed that there is considerable variation in blood cell parameters associated with infective parasite levels in a natural environment.
The larval cestode Tetraphyllidea and the copepod Caligus haemulonis were the dominant species infecting L. laevigatus. These endoparasites (cestode) and ectoparasites (copepod) might have biological and morphological traits relevant to the variability in blood parameters of the puffer fish. The cestode Tetraphyllidea is an absorber parasite, and the copepod C. haemulonis is characterized as a depredator (Vidal-Martínez et al. 2022). Both groups of parasites damage the tissues of their hosts, and they are associated with hematological changes (Sharp et al. 1992; Jones and Grutter 2005). For example, the anemia and inflammatory response of fish have been observed in hosts infected with copepods such as Caligus rogercresseyi and cestodes Cyathocephalus truncates and Bothriocephalus acheilognathi, respectively (Sopinska 1985; Martins et al. 2004; Alvarez-Pellitero et al. 2008; Peña-Rehbein et al. 2013). Therefore, the present study suggests that the high infection intensity of cestodes and copepods could most likely affect the health of L. laevigatus.
In this puffer fish, the erythrocyte characteristics (oval nuclei and centrally positioned) were consistent with teleost fish (Palíková et al. 1999; Rough et al. 2005; Pavlidis et al. 2007; Fajer-Ávila et al. 2011; Grant 2015). However, the erythrocyte size of L. laevigatus (6–10 µm) differed from that suggested by Fänge (1992) for teleost fish with a tendency to live in brackish waters (8–15 µm) and as reported by Fajer-Ávila et al. (2011) for the puffer fish Sphoeroides annulatus (7.61 ± 0.66 µm) from the Pacific Coast. Larsson et al. (1976) and Glazova (1977) noted that erythrocytes are slightly smaller in active species than in nonactive species due to oxygen demands. The dissimilarity in the erythrocyte size of S. annulatus and L. laevigatus is likely due to their habitat. S. annulatus prefers shallow waters (<1–60 m) and represents the category of puffer fish that are slow swimmers, while L. laevigatus is an active species in marine waters (10–180 m) (Nader et al. 2012).
Although variation in leukocyte classification between fish species was observed (Barber et al. 1981; Tierney et al. 2004), the white cells of L. laevigatus were consistent with the general classification suggested by Fänge (1992) for teleost fishes. In L. laevigatus, lymphocytes were the most abundant, accounting for 83% of leukocytes. These results support early studies by Fänge (1992) and Fajer-Ávila et al. (2011) concerning teleost fish (50%–80%) and S. annulatus (84%–86%), respectively. The lymphocytes of L. laevigatus (6–10 µm) are apparently larger than those of S. annulatus (5.06 ± 0.52 µm) and teleost fish (4.5–8.2 µm). The lymphocytes constituted the basis of the immune response of fish, and some authors mentioned a size variation (small, medium, and large lymphocytes) between species of fish (Rough et al. 2005). Granulocytes were the second most frequently observed (14%) leukocyte of L. laevigatus, measuring between 7 and 14 µm. These values differ from the low values for S. annulatus (12.34%), with cell measurements of 8.38 ± 0.80 μm, while high values (18%) and cell measurements of 9–12 µm have been reported for teleost fish. This inconsistency can be attributed to the fact that granulocytes are active cells with properties such as phagocytosis, so they can vary in size between different groups of fish (Buchmann 2022). In granulocytic cells, neutrophils were the most abundant (6.6%), followed by basophils (4.2%) and eosinophils (3.9%). In contrast, neutrophils account for less than 5% of leukocytes, while basophils and eosinophils are scarce cells in teleost fish (Fänge 1992). Neutrophils are involved in host protection against pathogens and the inflammatory process (Havixbeck and Barreda 2015; Buchmann 2022). Therefore, the presence and abundance of neutrophils in L. laevigatus suggest an active host immune response most likely attributed to the presence of parasitic infections.
In this research, the additive model analysis showed that the infective parasite intensity (ectoparasites and endoparasites) of L. laevigatus was associated with concurrent changes in erythrocyte, neutrophil, and thrombocyte values, such as with the length and condition factor (k) of this puffer fish. Several studies have demonstrated that parasitism causes impaired condition factors in fish (Guidelli et al. 2011; Özer et al. 2016; Ryberg et al. 2020). This result suggested that the infection levels of wild puffer fish most likely affected their health status and metabolism due to energy consumption to maintain fish homeostasis (Sadauskas-Henrique et al. 2011; Ryberg et al. 2020). Several studies have recorded alterations in erythrocyte values in a wide variety of fish species infected with parasites (Martins et al. 2004; Montero et al. 2004; Belo et al. 2013; Restiannasab et al. 2014; Souza-Rocha et al. 2018). These alterations are related to anemia and attributed to the consumption of blood as a form of parasite feeding; in some cases, those with anemia cannot recover fully, leading to a fatal outcome (Witeska 2015). However, with the variation in erythrocytes found in L. laevigatus, we cannot indicate the presence of anemia because of the lack of parameters of normal erythrocytes established in this puffer fish. Then, the tendency of infected fish to have decreased erythrocytes is a determining factor in the physiology of the organism.
Likewise, the variation in neutrophil values with respect to infective parasite intensity can be attributed to the fish immune response and inflammation processes, as suggested by Buchmann (2022). It is known that parasites are host stressors and that neutrophil numbers are normally lower in uninfected fish than in infected fish (Havixbeck and Barreda 2015; Souza-Rocha et al. 2018). The variation in thrombocyte values is associated with the activation of the coagulation system of fish, and this can be influenced by infective parasite damage. Studies have suggested that this damage occurs during ectoparasite infection, as monogeneans and copepods cause mechanical damage, resulting in hemorrhages (Ferguson 2006; Tavares-Dias and Oliveira 2009; Belo et al. 2013; Becker and Baldisserotto 2014; Fernandes and Moron 2014). Therefore, the condition factor, together with hematological parameters, is an important variable for monitoring the health status and infective parasite intensity of L. laevigatus.
Regarding ectoparasite infection, the second model suggested that their variation influenced the number of erythrocytes and thrombocytes in puffer fish (Table 2). The copepod Caligus haemulonis was the second dominant species of L. laevigatus. It is known that copepods damage the tissues of their hosts; thus the increase in thrombocytes can be attributed to avoiding blood loss. These results are observed in some species of fish infected with copepods (Paperna and Zwerner 1982; Roubal 1989; Ferguson 2006). However, Fajer-Ávila et al. (2011) did not find an association between the blood parameters and the infection intensity of the copepod Pseudochondracanthus diceraus on S. annulatus. This difference can most likely be attributed to infection levels (i.e., n = 17 parasites on S. annulatus vs. n = 53 parasites in L. laevigatus). High levels of infective parasites promote a stress reaction in the host, with the presence of physiological responses (Urbinati et al. 2015; Holzer et al. 2021). Our results indicate that the health conditions of wild puffer fish can be especially affected by ectoparasites. This is in accordance with Guidelli (2011), who found a negative effect of the abundance of ectoparasites on the condition factor of wild fish. Therefore, our results suggest that erythrocyte variation is due to the loss of blood, and thrombocyte variability is a function of blood clot formation that occurs when the vasculature is damaged by these parasites.
Our third model suggested that the number of endoparasites is related to neutrophil variability. The aggregation of parasites can promote neutrophil cell variation as an immune response. We observed an aggregation of the larval cestode Tetraphyllidea and nematode larvae in the intestine of L. laevigatus. Buchmann (2022) indicated that this cell line of defense is stimulated by parasites such as monogeneans, cestodes, trematodes, and ciliates. Several studies mention that helminthic infection causes inflammation, impaired nutrient absorption, damage to the intestinal tract, and, in several cases, host mortality (Ogawa et al. 2007; Scholz et al. 2012; Wise et al. 2013; Jithila and Prasadan 2019; Nguyen et al. 2021). We consider that neutrophils are an immunological response of puffer fish to this parasitic aggregation in the intestine of L. laevigatus.
The size of L. laevigatus was an important factor for parasite infection in the three models due to larger puffer fish having the highest infection intensities. The influence of host size on infection intensity variability is a pattern documented in marine and freshwater fish (Poulin 2000; Luque and Alves 2001; Oniye et al. 2004; Barzegar and Jalali 2009). Some authors have mentioned that larger fish provide more internal and external areas for parasite establishment, and the highest infection intensity occurs because they eat more parasitized small hosts and have a longer contact time for the transmission of parasites (Rolbiecki 2006; Poulin 2000; May-Tec et al. 2020).
In conclusion, our results indicate that parasitism is reflected in the variation in the blood cells of L. laevigatus, which is related to the health status of the fish (condition factor). In addition, the present results contribute to the baseline knowledge of blood cell parameters in this puffer fish and could be useful for further fish hematology research, such as establishing diagnostic applications in the wild and in aquaculture. To establish a range of blood cell parameters in this species, it is essential to carry out bioassays comparing healthy fish and infected fish under controlled conditions. This interaction promotes understanding an identifying the variability in natural infections, such as the possible effects of some ecological disturbances (contaminants) on fish health in natural populations.
Data availability
All data generated or analyzed during this study are included in this published article.
References
Al-Sabti K, Metcalfe CD (1995) Fish Micronuclei for Assessing Genotoxicity in Water. Mutat Res Genet Toxicol Environ Mutagen 343:121–135. https://doi.org/10.1016/0165-1218(95)90078-0
Alvarez-Pellitero P (2008) Fish immunity and parasite infections: from innate immunity to immunoprophylactic prospects. Vet Immunol Immunopathol 126:171–198. https://doi.org/10.1016/j.vetimm.2008.07.013
Anderson RC (2004) Nematode parasites of vertebrates: Their development and transmission. Department of Zoology, University of Guelph, Edit CABI
Bagenal TB, Tesch FW (1978) Age and growth. In: Bagenal T (ed) Methods for assessment of fish production in freshwater waters, 3rd edn. Blackwell Scientific Publication, Oxford, pp 101–136
Balla KM, Lugo-Villarino G, Spitsbergen JM, Stachura DL, Hu Y, Bañuelos K, Traver D (2010) Eosinophils in the zebrafish: Prospective isolation, characterization, and eosinophilia induction by helminth determinants. Blood 116:3944–3954. https://doi.org/10.1182/blood-2010-03-267419
Barber DL, Mills Westermann JE, White MG (1981) The blood of the Antarctic icefish Chaenocephalus aceratus Lonnberg: light and electron microscopic observations. J Fish Biol 19:11–28
Baršiene J, Lazutka J, Šyvokiene J et al (2004) Analysis of micronuclei in blue mussels and fish from the Baltic and North Seas. Environ Toxicol 19:365–371. https://doi.org/10.1002/tox.20031
Barzegar M, Jalali B (2009) Crustacean Parasites of Fresh and Brackish (Caspian Sea) Water Fishes of Iran. J Agric Sci Technol 11:161–171
Becker AG, Baldisserotto B (2014) Regulação osmótica e iônica. In: Baldisserotto B, Cyrino JEP, Urbinati EC (eds) Biologia e Fisiologia de Peixes Neotropicais de Água Doce, 1st edn. Fundação de Apoio a Pesquisa, Ensino e Extensão (Funep), Jaboticabal, São Paulo, pp 253–264
Belo MAA, Souza DGF, Faria VP et al (2013) Haematological response of curimbas Prochilodus lineatus, naturally infected with Neoechinorhynchus curemai. J Fish Biol 82:1403–1410. https://doi.org/10.1111/jfb.12060.PMid:23557315
Blaxhall PC (1972) The haematological assessment of the health of freshwater fish: a review of selected literature. J. Fish Biol. 4:593–604
Blaxhall PC, Daisley KW (1973) Routine haematological methods for use with fish blood. J. Fish Biol 5:771–781
Buchmann K (2022) Neutrophils and aquatic pathogens. Parasite Immunol 44:1–11. https://doi.org/10.1111/pim.12915
Burnham KP, Anderson DR (2002) Model Selection and Multimodel Inference: A Practical Information-theoretic Approach, 2nd edn. Springer, New York
Bush AO, Lafferty KD, Lotz JM et al (1997) Parasitology meet ecology in its own terms: margolis revisited. J Parasitol 83:575–583
Chávez-Sánchez MC, Álvarez-Lajonchère L, Abdo De La Parra MI et al (2008) Advances in the culture of the Mexican bullseye puffer fish Sphoeroides annulatus, Jenyns (1842). Aquac Res 39:718–730. https://doi.org/10.1111/j.1365-2109.2008.01924.x
Clauss TM, Dove ADM, Arnold JE (2008) Hematologic Disorders of Fish. Vet Clin North Am Exot Anim Pract 11:445–462. https://doi.org/10.1016/j.cvex.2008.03.007
Conroy DA, Conroy G (2007) Basic atlas of normal and abnormal blood cells in farmed tilapias. Patterson Peddie Consulting Ltd, Northern Ireland,UK
Dunne JA, Lafferty KD, Dobson AP et al (2013) Parasites Affect Food Web Structure Primarily through Increased Diversity and Complexity. PLoS Biol 11:e1001579. https://doi.org/10.1371/journal.pbio.1001579
Ek-Huchim JP, Árcega-Cabrera F, May-Tec AL, Améndola-Pimenta M, Ceja-Moreno V, Rodríguez-Canul R (2022) Red Blood Cell Cytotoxicity Associated to Heavy Metals and Hydrocarbons Exposure in Flounder Fish from Two Regions of the Gulf of Mexico. Bull Environ Contam Toxicol 108(1):78–84. https://doi.org/10.1007/s00128-021-03176-w
Fajer-Ávila EJ, Guzman-Beltran L, Zárate-Rodríguez WC et al (2011) Patología causada por adultos de Pseudochondracanthus diceraus (Copepoda: Chondracanthidae) parásito del botete diana Sphoeroides annulatus. Rev Biol Mar Oceanogr 46:293–302. https://doi.org/10.4067/S0718-19572011000300001
Fänge R (1992) Fish blood cells. Fish Physiol 12:1–54. https://doi.org/10.1016/S1546-5098(08)60008-4
Fazio F (2019) Fish hematology analysis as an important tool of aquaculture: A review. Aquaculture 500:237–242. https://doi.org/10.1016/j.aquaculture.2018.10.030
Ferguson HW (2006) Systemic pathology of fish: a text and atlas of normal tissues in Teleosts and their responces in disease. Scotian Press
Fernandes MN, Moron SE (2014) Respiração e adaptações respiratórias. In: Baldisserotto B, Possebon Cyrino JE, Criscuolo Urbinati E (eds) Biologia e Fisiologia de Peixes Neotropicais de Água Doce, 1st edn. Fundação de Apoio a Pesquisa, Ensino e Extensão (Funep), Jaboticabal, São Paulo pp 203–232
Giari L, Castaldelli G, Timi J (2022) Ecology and effects of metazoan parasites of fish in transitional waters. Parasitology 149:1829–1841. https://doi.org/10.1017/S0031182022001068
Glazova TN (1977) Ichthyologia (Beograd) 9:65–73
Grant KR (2015) Fish hematology and associated disorders. Vet Clin: Exotic Animal Practice 18:83–103
Guidelli G, Tavechio WLG, Takemoto RM et al (2011) Relative condition factor and parasitism in anostomid fishes from the floodplain of the Upper Paraná River, Brazil. Vet Parasitol 177:145–151. https://doi.org/10.1016/j.vetpar.2010.11.035
Havixbeck JJ, Barreda DR (2015) Neutrophil development, migration, and function in teleost fish. Biology 4:715–734. https://doi.org/10.3390/biology4040715
Ho JS, Lin CL (2004) Sea Lice of Taiwan (Copepoda: Siphonostomatoida: Caligidae). The Sueichan Press, Keelung, Taiwan, p 388
Holzer AS, Piazzon MC, Barrett D et al (2021) To React or Not to React: The Dilemma of Fish Immune Systems Facing Myxozoan Infections. Front Immunol 12:1–22. https://doi.org/10.3389/fimmu.2021.734238
Isbister GK, Son J, Wang F et al (2002) Puffer fish poisoning: a potentially life- threatening condition. Med J Aust. 177:650–3. https://doi.org/10.5694/j.1326-5377.2002.tb04999.x
Jithila P, Prasadan P (2019) Histopathology and other aspects of the Clinostomum complanatum infection in the freshwater fish, Pseudosphromenus cupanus from the south western ghats. Pak J Parasitol 68:33–38
Jones A, Bray RA, Gibson DI (2005) Keys to the Trematoda, vol 2. CAB International and Natural History Museum, Wallingford, UK
Jones CM, Grutter AS (2005) Parasitic isopods (Gnathia sp.) reduce hematocrit in captive blackeye thicklip (Labridae) on theGreat Barrier Reef. J Fish Biol 66:860–4. https://doi.org/10.1111/j.0022-1112.2005.00640.x
Kumar A (2023) Biochemical and hematological responses of Cyprinus carpio fish to Philometra pellucida parasite infestation. Int J Adv Res Biol Sci 10:71–81. https://doi.org/10.22192/ijarbs.2023.10.07.008
Lafferty KD, Dobson AP, Kuris AM (2006) Parasites dominate food web links. Proc Natl Acad Sci U. S. A. 103:11211–6. https://doi.org/10.1073/pnas.0604755103
Larsson A, Johansson-Sjobeck M, Fange R (1976) Comparative study of some haematological and biochemical blood parameters in fishes from the Skagerrak. J Fish Biol 9:425–440
Lin CL, Ho JS (2006) Copepods of the genus Taeniacanthus Sumpf, 1871 (Poecilostomatoida: Taeniacanthidae) parasitic on marine fishes of Taiwan. Taiwan Shuichanxue Hui Kan 33:171–191. https://doi.org/10.29822/2fJFST.200606.0008
Luque JL, Alves DR (2001) Ecologia das comunidades de metazoarios parasites do xareu Caranx hippo (L.) e do xerelete Caranx latus Agassiz (Osteichthyes, Carangidae) do litoral do Estado do Rio de Janeiro. Brazil. Rev Bras Zool 18:399–41. https://doi.org/10.1590/S0101-81752001000200011
Marcogliese DJ (2002) Food webs and the transmission of parasites to marine fish. Parasitology 124:S83–S99. https://doi.org/10.1017/s003118200200149x
Martins ML, Tavares-Dias M, Fujimoto RY et al (2004) Haematological alterations of Leporinus macrocephalus (Osteichtyes: Anostomidae) naturally infected by Goezia leporini (Nematoda: Anisakidae) in fish pond. Arq Bras Med Vet e Zootec 56:640–646. https://doi.org/10.1590/s0102-09352004000500011
May-Tec AL, Herrera-Castillo NA, Vidal-Martínez VM et al (2020) Following the infection dynamics of the tropical trematode Oligogonotylus mayae in its intermediate and definitive hosts for 13 years. J. Helminthol 94:e208. https://doi.org/10.1017/S0022149X200008
May-Tec AL, Baños-Ojeda C, Mendoza-Franco EF (2022) Parasitic crustaceans (Branchiura and Copepoda) parasitizing the gills of puffer fish species (Tetraodontidae) from the coast of Campeche, Gulf of Mexico. ZooKeys 1089:73–92. https://doi.org/10.3897/zookeys.1089.79999
Montero FE, Crespo S, Padrós F et al (2004) Effects of the gill parasite Zeuxapta seriolae (Monogenea: Heteraxinidae) on the amberjack Seriola dumerili Risso (Teleostei: Carangidae). Aquaculture 232:153–163. https://doi.org/10.1016/S0044-8486(03)00536-2
Murray SA (1983). Thermal effects of bluegill hematology. Environmental Protection Agency, Washington DC
Nader M, Indary S, Boustany L (2012) The Puffer Fish Lagocephalus Sceleratus (Gmelin, 1789) in the Eastern Mediterranean. FAO East Med Tech Doc
Nguyen TH, Dorny P, Nguyen TTG et al (2021) Helminth infections in fish in Vietnam: A systematic review. Int J Parasitol Parasites Wildl 14:13–32. https://doi.org/10.1016/j.ijppaw.2020.12.001
NMFS (1989) Japan’s “fugu” or puffer fish market. Mar Fish Rev 51:60e62
Ogawa K, Nagano T, Akai N et al (2007) Blood fluke infection of cultured tiger puffer Takifugu rubripes imported from China to Japan. Fish Pathol 42:91–99
Omar RH, Hagras AA, El-Naggar MA et al (2021) Ecological, hematological and parasitological studies on Oreochromis niloticus linnaeus 1757 in the nile delta region Egypt. Egypt J Aquat Biol Fish 25:795–819. https://doi.org/10.21608/EJABF.2021.150883
Oniye SJ, Adebote DA, Ayanda OI (2004) Helminth parasites of Clarias gariepinus in Zaria. Nigeria J Aquat Sci 2:71–76
Özer A, Çankaya E, Yılmaz Kırca D (2016) Health assessment of grey mullet Mugil cephalus based on interrelationship between parasite co-infections and relative condition factor. J Zool 300:186–196. https://doi.org/10.1111/jzo.12371
Palíková M, Mares J, Jirásek J (1999) Characteristics of leukocytes and thrombocytes of selected sturgeon species from intensive breeding. Acta Vet Brunensis 68:259–264
Palm HW (2004) The Trypanorhyncha Diesing, 1863. PK SPL-IPB Press, Bogor, p 710
Paperna I, Zwerner DE (1982) Host-parasite relationship of Ergasilus labracis Krøyer (Cyclopidea, Ergasilidae) and the striped bass, Morone saxatilis (Walbaum) from the lower Chesapeake Bay. Ann Parasitol 57:393–405
Pavlidis M, Futter WC, Katharios P et al (2007) Blood cell profile of six mediterranean mariculture fish species. J Appl Ichthyol 23:70–7. https://doi.org/10.1111/j.1439-0426.2006.00771.x
Peña-Rehbein P, De los Ríos-Escalante RC, Navarrete C (2013) Use of a negative binomial distribution to describe the presence of Sphyrion laevigatum in Genypterus blacodes. Rev Brasil Parasitol Veter 22:602–604. https://doi.org/10.1590/S1984-29612013000400024
Poulin R (2000) Variation in the intraspecific relationship between fish length and intensity of parasitic infection: Biological and statistical causes. J Fish Biol 56:123–137. https://doi.org/10.1006/jfbi.1999.1146
R Core Team (2018) A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. http://www.R-project.org/. Accessed 1 Oct 2022
Restiannasab A, Hemmatzadeh M, Khara H et al (2014) Changes of haematological indices of grass carp, Ceteopharyngodon idella exposed to monogenean parasites, Gyrodactylus spp. and Dactylogyrus spp. J Parasit Dis 40:627–629. https://doi.org/10.1007/s12639-014-0547-y
Ricker WE (1975) Computation and interpretation of biological statistics of fish populations. Bull Fish Res Bd Can 191:1–382
Rigby RA, Stasinopoulos DM (2005) Generalized additive models for location, scale and shape. J R Stat Soc Ser C Appl Stat 54:507–54
Rolbiecki L (2006) Correlation between the occurrence of parasites and body length of roach, carp bream, European perch, zander, and ruffe in the Vistula Wetland estuary. Oceanol Hydrobiol Stud 3:257–267
Roubal FR (1989) Comparative pathology of some monogenean and copepod ectoparasites on the gills of on Acanthopagrus australis (family: Sparidae). J Fish Biol 34:503–514
Rough KM, Nowak BF, Reuter RE (2005) Haematology and leucocyte morphology of wild caught Thunnus maccoyii. J Fish Biol 66:1649–1659. https://doi.org/10.1111/j.0022-1112.2005.00710.x
Ryberg MP, Skov PV, Vendramin N, Buchmann K, Nielsen A, Behrens JW (2020) Physiological condition of Eastern Baltic cod, Gadus morhua, infected with the parasitic nematode Contracaecum osculatum. Conserv Physiol 8:1–14. https://doi.org/10.1093/conphys/coaa093
Sadauskas-Henrique H, Sakuragui MM, Paulino MG et al (2011) Using condition factor and blood variable biomarkers in fish to assess water quality. Environ Monit Assess 181:29–42. https://doi.org/10.1007/s10661-010-1810-z
Scholz T, Kuchta R, Williams C (2012) Bothriocephalus acheilognathi. In: Woo PTK, Buchmann K (eds) Fish Parasites: Pathobiology and Protection. CABI, Wallingford, United Kingdom, pp 282–297
Schultz N, Norrgren L, Grawé J, Johannisson A, Medhage Ö (1993) Micronuclei frequency in circulating erythrocytes from rainbow trout (Oncorhynchus mykiss) subjected to radiation, an image analysis and flow cytometric study. Comp Biochem Physiol Part C: Comp Pharma 5:207–211. https://doi.org/10.1016/0742-8413(93)90196-R
Sharp GJE, Pike AW, Secombes CJ (1992) Sequential development of the immune response in rainbow trout [Oncorhynchus mykiss (Walbaum, 1792)] to experimental plerocercoid infections of Diphyllobothrium dendriticum (Nitzsch, 1824). Parasitology 104:169–178
Sopinska A (1985) Effects physiological factors, stress, and disease on hematologic paramerters of carp, with a particular reference to the leukocyte patterns. III. Changes in blood accompanyng branchionecrosis and bothriocephalosis. Acta Ichthyol Pisc 15:141–165
Souza-Rocha MJ, Jerônimo GT, da Costa Ferreira OT et al (2018) Changes in hematological and biochemical parameters of tambaqui (Colossoma macropomum) parasitized by metazoan species. Rev Bras Parasitol Vet 27:488–494. https://doi.org/10.1590/s1984-296120180073
Stump E, Ralph GM, Comeros-Raynal MT, Matsuura K, Carpenter KE (2018) Global conservation status of marine pufferfishes (Tetraodontiformes: Tetraodontidae). Glob Ecol Conserv 14:e00388. https://doi.org/10.1016/j.gecco.2018.e00388
Tavares-Dias M, Oliveira SR (2009) A review of the blood coagulation system in fish. Braz J Biosci 7:205–224
Tierney KB, Farrel AP, Kennedy CJ (2004) The differential leucocyte landscape of four teleosts: juvenile Oncorhynchus kisutch, Clupea pallasi, Culaea inconstans and Pimephales promelas. J Fish Biol 65:906–919
Urbinati EC, Zanuzzo FS, Serra M, Wolkers CPB, Sabioni RE (2015) Avanços da fisiologia do estresse e suas implicações em espécies nativas. In: Tavares-Dias M, Mariano WS (eds) Aquicultura no Brasil: novas perspectivas. Editora Pedro & João, São Carlos pp 381–416
Vidal-Martinez VM, Kennedy CR, Aguirre-Macedo ML (1998) The structuring process of the macroparasite community of an experimental population of Cichlasoma urophthalmus through time. J Helminthol 72:199–207. https://doi.org/10.1017/s0022149x00016448
Vidal-Martínez VM, Ocaña FA, Soler-Jiménez LC et al (2022) Functional Groups of Metazoan Parasites of the Dusky Flounder (Syacium papillosum) as Bioindicators of Environmental Health of the Yucatan Shelf. Bull Environ Contam Toxicol 108:24–29. https://doi.org/10.1007/s00128-021-03177-9
Vidal-Martínez VM, Aguirre Macedo ML, Scholz T, González-Solis D, Mendoza-Franco EF (2002) Atlas de los helmintos parásitos de cíclidos de México. Instituto Politécnico Nacional, México DF
Wise DJ, Li MH, Griffin MJ (2013) Impacts of Bolbophorus damnificus (Digenea: Bolbophoridae) on production characteristics of Channel catfish, Ictalurus punctatus, raised in experimental ponds. J World Aquacult Soc 44:557–564. https://doi.org/10.1111/jwas.12060
Witeska M (2015) Anemia in teleost fishes. Bull Eur Ass Fish Pathol 35:148–160
Witeska M, Kondera E, Ługowska K, Bojarski B (2022) Hematological methods in fish – Not only for beginners. Aquaculture 547. https://doi.org/10.1016/j.aquaculture.2021.737498
Acknowledgments
This research was financially supported by a postdoctoral grant (216405) from CONACyT, Mexico, to A.L.M.-T. We would like to thank Francisco Javier Gómez Criollo and Jaime Navarro Flores (EPOMEX) for helping us with fish identification, and Mariela del Carmen Rosado Tun (Aquatic Parasitology, EPOMEX) for her assistance during the laboratory work. We would also like to thank David González-Solis (ECOSUR, Quintana Roo, Mexico) for their support in the identification of nematodes. We would like to express our sincere thanks to the administrative and academic authorities of the Universidad Autónoma de Campeche (UAC-EPOMEX) for use of the facilities.
Funding
This research was supported financially by a postdoctoral grant (216405) from CONACyT, Mexico, of A.L.M.-T.
Author information
Authors and Affiliations
Contributions
All authors conceived the study. Ana Luisa May-Tec: conceptualization, methodology, formal analyses, visualization, writing (reviewing and editing). Juan Pablo Ek-Huchim: methodology and review. Abril Rodríguez-González: review, and editing. Edgar Fernando Mendoza-Franco: visualization, resources, review, and editing. The authors read and approved the final manuscript.
Corresponding author
Ethics declarations
Ethical approval
All applicable institutional, national, and international guidelines for the care of animals were followed.
Consent to participate, consent for publication
All the authors read and approved the final version of the manuscript. All persons involved in the study gave their oral consent for publication.
Competing interests
The authors declare no competing interests.
Additional information
Handling Editor: Una Ryan
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Rights and permissions
Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.
About this article
Cite this article
May-Tec, A.L., Ek-Huchim, J.P., Rodríguez-González, A. et al. Differential blood cells associated with parasitism in the wild puffer fish Lagocephalus laevigatus (Tetraodontiformes) of the Campeche Coast, southern Mexico. Parasitol Res 123, 24 (2024). https://doi.org/10.1007/s00436-023-08066-0
Received:
Accepted:
Published:
DOI: https://doi.org/10.1007/s00436-023-08066-0