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Zoologia (Curitiba)

Print version ISSN 1984-4670

Zoologia (Curitiba, Impr.) vol.27 no.6 Curitiba  2010

http://dx.doi.org/10.1590/S1984-46702010000600017 

MORPHOLOGY AND PHYSIOLOGY

 

Genotoxic effects of the diesel water-soluble fraction on the seahorse Hippocampus reidi (Teleostei: Syngnathidae) during acute exposure

 

 

Celina Alcoforado Santos; Larissa Simões Novaes; Levy Carvalho Gomes*

Laboratório de Ecotoxicologia Aquática, Centro Universitário Vila Velha. Rua Comissário José Dantas de Melo 21, Boa Vista, 29102-770 Vila Velha, ES, Brazil

 

 


ABSTRACT

The high toxicity of diesel components makes oil spills a threat to the biota in coastal marine environments. The genotoxic effect of the diesel water-soluble fraction (DWSF) on Hippocampus reidi (Ginsburg, 1933) was assessed. Fish were exposed to three different DWSF dilutions for up to 96 hours, and genotoxicity was analyzed using the micronuclei test and the comet assay. The micronuclei test revealed no significant differences between any of the DWSF dilutions and the control in the 24-hours period; however, micronuclei increased in fish exposed to 1:500 and 1:100 DWSF dilutions for 96 hours. For all dilutions, there was an increase in micronuclei in fish exposed for 96 hours when compared to those exposed for 24 hours. The tested dilutions increased frequencies of cell classes 2 (medium damage) and 3 (large damage) in the comet assay after 24 and 96 hours. Fish exposed to DWSF 1:100 exhibited a higher frequency of class 4 (apoptosis) cells in the 96-hours period. All dilutions increased the comet score when compared to the control at 24 and 96 hours. The micronuclei and comet tests were efficient in detecting DWSF genotoxic effects in H. reidi.

Key words: Comet assay; diesel; marine fish; micronuclei; toxicity.


 

 

Diesel spills are a very important source of marine and coastal pollution (ZHANG et al. 2004, KING et al. 2005, ALBAIGÉS et al. 2006, SIMONATO et al. 2008). They are mainly caused by ships, sailing along the main maritime routes or anchored in harbors or tied up in berths (GONZÁLES et al. 2006, SILVA et al. 2009).

The diesel water-soluble fraction (DWSF) contains polar compounds and hydrocarbons of two toxicologically relevant groups: monoaromatic hydrocarbons (benzene, toluene and xylene) and low molecular weight polyaromatic hydrocarbons (PAHs) such as naphthalene, fluorene, and phenanthrene (SIMONATO et al. 2008). Among the diesel oil components, the PAHs raise the greatest environmental concerns due to their biotoxicity (LEE & ANDERSON 2005, FERREIRA et al. 2006). VANZELLA et al. (2007) suggested that the PAHs present in the DWSF form electrophilic compounds that react with DNA molecules and cause serious damage.

The micronuclei test and the comet assay are among the most efficient methods to evaluate DNA damage caused by diesel oil toxicity in fish (BUSCHINI et al. 2004, MARTÍNEZ-GOMEZ et al. 2006, VANZELLA et al. 2007). These two tests are simple, rapid and highly sensitive to several kinds of DNA damage (HARTMAN et al. 2003).

The seahorse Hippocampus reidi (Ginsburg, 1933) is a potential bioindicator of environmental disturbance caused by toxic compounds in coastal waters due to its wide geographic distribution (FOSTER & VINCENT 2004) and sensitivity to contaminants. This study aimed to assess the genotoxic effect of the DWSF on H. reidi and to evaluate the efficiency of the micronuclei test and the comet assay to detect genotoxic effects of the DWSF in this species.

 

MATERIAL AND METHODS

Fifty-six specimens of H. reidi (1.94 ± 0.47 g and 8.47 ± 0.68 cm) were obtained from a private breeder in the municipality of Serra, state of Espírito Santo (ES), Brazil, and transported to the laboratory (commute lasting approximately 1 hour) in plastic bags with pressurized oxygen. Acclimation and experiments were conducted using sea water collected at the Itapuã Beach, Vila Velha, state of Espírito Santo, Brazil (20°21'13"S, 40°17'02"W).

In the laboratory, fish were transferred to two 30-L aquaria containing 25 L filtered water, where they were keptfor 30 days. Fish were fed twice a day on live Artemia sp. There was no mortality during this period. During acclimation, physicochemical water parameters were measured every three days using a multiparameter YSI 85 instrument and a digital pH meter. The measurements obtained were as follows (mean ± SD): temperature = 22.1 ± 0.4ºC; conductivity = 39.9 ± 0.9 mS/cm; dissolved oxygen = 6.6 ± 0.7 mg/L; pH = 7.5 ± 0.2; salinity = 30.1 ± 0.01.

Commercial diesel oil (type B2) was purchased from a commercial gas station. The density of the oil was 0.849 g/cm3. The container used to transport the diesel oil was lined with a black plastic bag and sealed to prevent alteration in composition.

The DWSF was prepared in strict accordance with the methodology described by SINGER et al. (2000). A 5-g aliquot of the oil was weighed and transferred to a 1-L volumetric flask, and sea water was added to bring the final volume to 1 L. The oil + water mixture was placed in an amber container and shaken at 250 rpm for 24 hours without vortex formation. The procedure allowed the DWSF to be obtained. The DWSF was collected using a pipette, and the upper insoluble phase was discarded. The DWSF composition was analyzed by gas chromatography (Perkin-Elmer, Clarus 500). The following parameters were assessed: total PAH (4.8% v/v); benzene (0.11% v/v); toluene (0.59% v/v); m+o+p xylene (2.1% v/v); naphthalene (4.8 mg/L); phenanthrene (0.47 mg/L) and fluorene (0.36 mg/L).

After acclimation, the fish were transferred to 56 aquaria, each containing 1 L of sea water under constant aeration. One animal was placed in each aquarium. Four treatments (seven replicates for each sampling time) were defined according to DWSF dilutions: 1:1000, 1:500, 1:100 and control (without DWSF). These dilutions were based on a previous study by SOLÉ et al. (2008). The experiment lasted a total of 96 hours and sampling was conducted in two distinct periods: after 24 hours and after 96 hours. Half of the water volume in each aquarium used to expose fish for 96 hours was replaced after a 48-hours exposure with the same DWSF concentration that had been originally used.

After exposure (24 or 96 hours), fish were anesthetized with benzocaine 1:10 diluted in 95% alcohol. Their blood was collected by caudal vein punction. This procedure was conducted in accordance with the guidelines for the use of fish in research by the American Fisheries Society (NICKUM et al. 2004).

Physicochemical parameters of the water were measured at the beginning and at the end of the experiment, using a multiparameter YSI 85 instrument. The parameters obtained were (mean ± SD): temperature = 23.2 ± 0.2ºC; conductivity = 41.3 ± 0.5 mS/cm; dissolved oxygen = 6.9 ± 0.5 mg/L; and salinity = 30 ± 0.01.

Peripheral blood samples were smeared on clean slides. Slides were left to dry in the laboratory environment overnight, and then the smears were fixed in methanol PA for 15 minutes and stained for 20 minutes with 5% (w/v) Giemsa, washed with distilled water and left to dry in the laboratory environment. After drying, 2,000 erythrocytes per fish (1,000 from each duplicate slide) were blind analyzed for the presence of micronuclei at 400x magnification under a light microscope (AL-SABATI & METCALFE 1995).

The blood samples were diluted to 1:120 (v/v) with RPMI 1640 medium and used immediately. The alkaline comet assay was performed as described by TICE et al. (2000). Briefly, 5 µL of each diluted blood sample was added to 95 µL of 0.75% (w/v) molten low melting point agarose, and a portion of the mixture was spread on a microscope slide pre-coated with 1.5% (w/v) normal melting point agarose and topped with a coverslip. After the agarose solidified, coverslips were removed, and the slides were immersed in a lysis solution (2.5 M NaCl, 100 mM EDTA and 10 mM Tris, pH 10.0-10.5) containing 1% Triton X-100 and 10% DMSO. The slides were kept frozen in lysis solution (4°C) and protected from light for at least 2-3 hours at most subsequently, slides were incubated in freshly prepared alkaline buffer (300 mM NaOH and 1 mM EDTA, pH > 13, which was experimentally determined) for 20 minutes for DNA unwinding. Electrophoresis (15 minutes at 300 mA and 25 V [0.8 V/cm]) was performed in the same buffer. Every step was carried out under indirect yellow light. After electrophoresis, slides were neutralized in Tris 400 mM (pH 7.5), rinsed three times in distilled water and left to dry overnight at room temperature. Slides were then fixed for 10 minutes in trichloroacetic acid 15% w/v, zinc sulfate 5% w/v, and glycerol 5% v/v, rinsed three times in distilled water, and dried for two hours at 37°C. The dry slides were re-hydrated for five minutes in distilled water and then stained (sodium carbonate 5% w/v, ammonium nitrate 0.1% w/v, silver nitrate 0.1% w/v, tungstosilicic acid 0.25%, formaldehyde 0.15% w/v, freshly prepared in the dark) and constantly shaken for 35 minutes. The stained slides were rinsed twice with distilled water and then submerged in the stop solution (acetic acid 1%), rinsed again, and immediately coded for analysis. To calculate image length, 200 cells from each fish were randomly chosen (100 from each duplicate slide) and analyzed under an optical microscope (400× magnification). Analysis of the slides involved 200 cells/animal, utilizing the visual classification based on the migration of DNA fragments from the nucleus: class 0 (no damage), class 1 (little damage - less than or equal to the diameter of one nucleus), class 2 (medium damage - less than or equal to diameters of two nuclei), class 3 (extensive damage - greater than two times the diameter of one nucleus) and class 4 (apoptosis) (COLLINS et al. 1995, KOBAYASHI et al. 1995). The data are presented as the frequency of cells per class of damage. The comet score (CS) for each fish was calculated as the sum of the number of nucleoids observed in each damage class multiplied by the value of the respective damage class (0, 1, 2, 3 or 4). Results are expressed as the comet score for each treatment group, where 0 represents the absence of damage and 400 indicates the highest damage score.

For all data, normality was tested by the Kolmogorov-Smirnov test. The comet score presented a parametric pattern, and comet assay and micronuclei results did not; therefore, non-parametric tests were used for those results.

For both the micronuclei test and the comet assay, the differences in frequencies obtained for the different dilutions (1:1000, 1:500 and 1:100) in comparison to the respective controls at one of the two measurement times (24 or 96 hours) were analyzed by the Kruskal-Wallis ANOVA and Dunnett's test (p < 0.05). The difference between results obtained for the same dilution for the two sampling times was determined using the t test (p < 0.05).

For the assessment of CS, the difference in results obtained with each DWSF dilution were compared to the results of respective controls at one of the two sampling times (24 or 96 hours) using the ANOVA and Dunnett's test (p < 0.05). The difference between results obtained for same treatment for the two sampling times was determined using the t test (p < 0.05).

 

RESULTS

No statistically significant differences were observed in micronuclei frequency with respect to the control in samples collected in the 24-h period for any of the dilutions tested. By contrast, there was a significant increase in the frequency of micronuclei in fish exposed to the 1:500 and 1:1000 DWSF for 96 h Tab. I).

 

 

No significant difference was observed in the class 1 cells between samples exposed to any of the DWSF dilutions for 24 hours and their controls. However, H. reidi exposed to all DWSF dilutions presented significantly greater numbers of damaged cell classes 2 and 3 in comparison with their controls. For class 4 cells, the median was zero for all DWSF dilutions, with no statistically significant difference (Tab. II). As for the fish exposed for 96 h to all DWSF dilutions, the number of class 0 cells was lower than that of the respective control. By contrast, the fish exposed to all DWSF dilutions presented higher numbers of cell classes 2 and 3 when compared with their controls. In addition, the fish exposed to the 1:100 DWSF dilution had more class 4 cells in comparison to the control.

 

 

The fish exposed to the 1:1000, 1:500 and 1:100 DWSF dilutions presented higher comet scores when compared with the control groups in the two exposure periods (24 and 96 hours) (Fig. 1). There was no significant difference in comet score between the two exposure periods of fish within the same dilution (Control: p = 0.368 and T = 0.934; 1:1000 dilution: p = 0.659 and T = 0.452; 1:500 dilution: p = 0.722 and T = 0.364; 1:100 dilution: p = 0.161 and T = -1.994).

 

 

DISCUSSION

The DWSF was a determining factor in the induction of micronuclei in H. reidi. From the cellular perspective, micronuclei are formed by chromosome fragments or by chromosomes that, during anaphase, fail to be incorporated into the new nucleus (FENECH 2000). The appearance of micronuclei during cell division results from chromosome breakages, which in turn result from poor lesion repair or improper chromosome segregation during mitosis (IARMACOVAI et al. 2008). These errors may be induced by gene defects in the cell cycle, oxidative stress and/or exposure to contaminants (IARMACOVAI et al. 2008), as observed in the present study.

HOSHINA et al. (2008) have suggested the tilapia, Oreochromis niloticus (Linnaeus, 1758) as an appropriate test organism to assess genetic damage caused by oil because in this organism the exposure to [even low] oil concentrations induces the formation of micronuclei, and triggers cell death. In the tilapia, micronuclei frequency varied from 1 to 3 - values well under those reported here for H. reidi in the 96-hours exposure period, which varied between 2 and 6. The micronuclei test proved to be efficient in detecting the magnitude of the genotoxic effects of the DWSF in H. reidi because increased micronuclei frequencies were observed for increasing concentrations and longer exposure periods.

VANZELLA et al. (2007) assessed the effects of acute exposure to DWSF on the fish Prochilodus lineatus (Valenciennes, 1837). They observed that relative frequencies of erythrocytes were higher in fish exposed to the xenobiotic for over 96 hours. In the present study, the damage induced to H. reidi erythrocytes was also more evident when fish had been exposed to DWSF dilutions for 96-hours. It is possible that the 24-hours exposure period is not long enough to observe erythrocyte damage because by the end of this period the cell division process under the effect of the DWSF is only beginning. The comet assay allows one to distinguish and quantify cells with different DNA damage rates. Therefore, the analysis of the mean DNA damage index for each group is important because it can shed more light on the damage caused by xenobiotics (VANZELLA et al. 2007). The control fish exhibited a prevalence of class 0 and 1 cells, whereas class 2 and 3 cells were most frequent in samples collected from fish exposed to all dilutions (1:1000, 1:500, and 1:100) over both exposure periods (24 and 96 h) in comparison with the respective controls. Apoptosis, which corresponds to class 4 cells, was observed only in samples collected from individuals of H. reidi exposed to 1:100 dilutions of DWSF for 96 hours, though at a rather low frequency (median 2.5%). The results of the comet assay in H. reidi exposed to the DWSF appear sufficient to detect environmental genotoxicity. Our results are similar to those reported by AKCHA et al. (2003), who studied the effects of PAHs in Limanda limanda (Linnaeus, 1758) and demonstrated that the comet assay was sensitive enough to detect the effects caused by xenobiotics. An increased CS was observed with the increase in the DWSF concentrations, though this damage was not related to exposure time because no difference was observed in CS in relation to exposure time for any of the dilutions tested.

Hippocampus reidi is sensitive to genotoxic effects of the DWSF. The micronuclei test and the comet assay are efficient biomarkers of contamination by diesel oil in costal environments for this species.

 

ACKNOWLEDGMENTS

We are indebted to Bruno Ferreira and Frederico Delunardo for their help during fish sampling. This work was supported by a research grant from UVV/FUNDADESP # 09/2009. L.C. Gomes is a research fellowship recipient from CNPq/Brazil.

 

LITERATURE CITED

AKCHA, F.; F.V. HUBERT & A. PFHOL-LESZKOWICZ. 2003. Potential value of the comet assay and DNA adduct measurement in dab (Limanda limanda) for assessment of in situ exposure to genotoxic compounds. Mutation Research 534: 21-32.         [ Links ]

ALBAIGÉS, J.; B. MORALES-NIN & F. VILAS. 2006. The Prestige oil spill: a scientific response. Marine Pollution Bulletin 53: 205-207.         [ Links ]

AL-SABTI, K. & C.D. METCALFE. 1995. Fish micronuclei for assessing genotoxicity in water. Mutation Research 343: 121-135.         [ Links ]

BUSCHINI, A.; A. MARTINO; B. GUSTAVINO; M. MONFRINOTTI; P. POLI; C. ROSSI; M. SANTORO; A.J.M. DÖRR & M. RIZZONI. 2004. Comet assay and micronuclei test in circulating erythrocytes of Cyprinus carpio specimens exposed in situ to lake waters treated with disinfectants for potabilization. Mutation Research 557: 119-129.         [ Links ]

COLLINS, R.A.; M. AI-GUO & S.J. DUTHIE. 1995. The kinetics of repair of oxidative DNA damage (strand breaks and oxidised pyrimidines) in Human Cells. Mutation Research 336: 69-77.         [ Links ]

FENECH, M. 2000. The in vitro micronuclei technique. Mutation Research 455: 81-95.         [ Links ]

FERREIRA, M.; P. MORADAS-FERREIRA & M.A. REIS-HENRIQUES. 2006. The effect of longterm depuration on phase I and phase II biotransformation in mullets (Mugil cephalus) chronically exposed to pollutants in River Douro Estuary, Portugal. Marine Environmental Research 61: 326-338.         [ Links ]

FOSTER, S.J. & C.J. VINCENTJ. 2004. Live history and ecology of seahorses: implications for conservation and management. Journal of Fish Biology 65: 1-61.         [ Links ]

GONZÁLEZ, J.J.; L. VINAS; M.A. FRANCO; J. FUMEGA; J.A. SORIANO; G. GRUEIRO; S. MUNIATEGUI; P. LOPEZ-MAHIA; D. PRADA; J.M. BAYONA; R. ALZAGA & J. ALBAIGÉS. 2006. Spatial and temporal distribution of dissolved/dispersed aromatic hydrocarbons in seawater in the area affected by the Prestige oil spill. Marine Pollution Bulletin 53: 250-259.         [ Links ]

HARTMANN, A.; E. AGURELL; C. BEEVERS; S. BRENDLER-SCHWAAB; B. BURLINSON; P. CLAY; A. COLLINS; A. SMITH; G. SPEIT; V. THYBAUD & R.R. TICE. 2003. Recommendations for conducting the in vivo alkaline comet assay. Mutagenesis 18 (1): 45-51.         [ Links ]

HOSHINA, M.M.; D.F. ANGELIS. & M.A. MARIN-MORALES. 2008. Induction of micronuclei and nuclear alterations in fish (Oreochromis niloticus) by a petroleum refinery effluent. Mutation Research 656: 44-48.         [ Links ]

IARMACOVAI, G.; S. BONASSI; A. BOTTA; R.A. BAAN & T. ORSIÉRE. 2008. Genetic polymorphisms and micronuclei formation: A review of the literature. Mutation Research 658: 215-233.         [ Links ]

KING, S.C.; J.E. JOHNSON; M.L. HAASCH; D.A.J. RYAN; J.T. AHOKAS & K.A. BURNS. 2005. Summary results from a pilot study conducted around an oil production platform on the Northwest Shelf of Australia. Marine Pollution Bulletin 50: 1163-1172.         [ Links ]

KOBAYASHI, H.; Y. SUGUYAMA; M. MORIKAWA; T. HAYASHI & A. SOFUNI. 1995. Comparison between manual microscopic analysis and computerized image analysis in the single cell gel electrophoresis. MMS Community 3: 103-115.         [ Links ]

LEE, R.F. & J.W. ANDERSON. 2005. Significance of cytochrome P450 system responses and levels of bile fluorescent aromatic compounds in marine wildlife following oil spills. Marine Pollution Bulletin 50: 705-723.         [ Links ]

MARTÍNEZ-GOMEZ, C.; J.A. CAMPILLO; J. BENEDICTO; B. FERNANDEZ; J. VALDES; I. GARCIA & F. SANCHEZ. 2006. Monitoring biomarkers in fish (Lepidorhombus boscii and Callionymus lyra) from the northern Iberian shelf after the Prestige oil spill. Marine Pollution Bulletin 53: 305-314.         [ Links ]

NICKUM, J.G.; H.L. BART; P.R. BOWSER; I.E. GREER; C. HUBBS; J.A. JENKINS; J.R. MACMILLAN; J.W. RACHLIN; J.D. ROSE; P.W. SORENSEN & J.R. TOMASSO 2004. Guidelines for the use of fishes in research. American Fisheries Society, Bethesda.         [ Links ]

SILVA, C.A.; C.A.O. RIBEIRO; A. KATSUMITI; M.L.P. ARAUJO; E.M. ZANDONÁ; G.P. COSTA SILVA; J. MASCHIO; H. ROCHE & H.C. SILVA DE ASSIS. 2009. Evaluation of waterborne exposure to oil spill 5 years after an accident in Southern Brazil. Ecotoxicology Environmental Safety 72: 400-409.         [ Links ]

SIMONATO, J.D.; C.L.B. GUEDES & C.B.R. MARTINEZ. 2008. Biochemical, physiological, and histological changes in the neotropical fish Prochilodus lineatus exposed to diesel oil. Ecotoxicology Environmental Safety 69: 112-120.         [ Links ]

SINGER, M.M.; D. AURAND; G.E. BRAGIN; J.R. CLARKS; G.M. COELHO; M. SOWBY & L. TJEERDEMA. 2000. Standardization of the Preparation and Quantitation of Water accommodated Fractions of Petroleum for Toxicity Testing. Marine Pollution Bulletin 40 (11): 1007-1016.         [ Links ]

SOLÉ, M.; D. LIMA; M.A. REIS-HENRIQUES & M.M. SANTOS. 2008. Stress biomarkers in Juvenile Senegal Sole, Solea senegalensis, exposed to the water-accommodated fraction of the "Prestige" Fuel Oil. Bulletin of Environmental Contamination and Toxicology 80: 19-23.         [ Links ]

TICE, R.R.; E. AGURELL; D. ANDERSON; B. BURLINSON; A. HARTMANN; H. KOBAYASHI; Y. MIYAMAE; E. ROJAS; J.C. RYU & Y.F. SASAKI. 2000. Single cell gel/comet assay: Guidelines for in vitro and in vivo genetic toxicology testing. Environmental Mutagenesis 35 (3): 206-221.         [ Links ]

VANZELLA, T.P.; C.B.R. MARTINEZ & M.S. CÓLUS. 2007. Genotoxic and mutagenic effects of diesel oil water soluble fraction on a neotropical fish species. Mutation Research 631: 36-43.         [ Links ]

ZHANG, J.F.; X.R. WANG; H.Y. GUO; J.C. WU & Y.Q. XUE. 2004. Effects of water-soluble fractions of diesel oil on the antioxidant defenses of the goldfish, Carassius auratus. Ecotoxicology Environmental Safety 58: 110-116.         [ Links ]

 

 

Submitted: 03.VIII.2010; Accepted: 21.X.2010.

 

 

Editorial responsibility: Antonio Ostrensky Neto
* Corresponding author: E-mail: levy.gomes@uvv.br

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