Exposure to Hg2+ and Pb2+ changes NTPDase and ecto-5′-nucleotidase activities in central nervous system of zebrafish (Danio rerio)
Introduction
Heavy metals, such as mercury and lead are important environmental contaminants, which can reach aquatic systems derived from effluents of industrial, urban and mining sources. These substances present severe risk to the aquatic biota and humans, even at sublethal concentrations (Baatrup, 1991, Jarup, 2003). Animals exposed to Hg2+ and Pb2+ have adverse developmental, reproductive, neurological and behavioral effects. Many cellular processes are affected by exposure to Hg2+ and Pb2+ and the correct function of central nervous system can be impaired by neurochemical changes (Aguilar and Kostrzewa, 2004). Synaptic transmission can be altered after exposure to these heavy metals. Changes in the release, extracellular metabolism and/or uptake and expression of components of neurotransmitter systems have been related to toxic effects observed in heavy metals-exposed animals (Cooper and Manalis, 1983).
ATP is a primitive signaling molecule that has been retained as a cotransmitter in every nerve type in both peripheral and central nervous system (Burnstock, 2004). This molecule is released to the synaptic cleft in a calcium-dependent manner, where it can act as a fast neurotransmitter or as a modulator, regulating the activity of other transmitter substances (Cunha and Ribeiro, 2000). ATP exerts its effects through purinoceptors, divided in two major classes, ionotropic P2X and metabotropic P2Y receptors (Ralevic and Burnstock, 1998). At the synapse, ATP can be metabolized by a group of enzymes called ecto-nucleotidases, which includes NTPDase family (nucleoside triphosphate diphosphohydrolase) and ecto-5′-nucleotidase. The final product of this enzyme cascade is the nucleoside adenosine, an important neuromodulator that acts on G-protein-coupled receptors, named A1, A2A, A2B and A3 (Ribeiro et al., 2003).
Ecto-nucleotidases are ubiquitous enzymes with a broad phylogenetic distribution, occurring in many vertebrate tissues. NTPDases present the ability to hydrolyze triphosphate and diphosphate nucleotides. Mammalian NTPDases1–3 and 8 are extracellular enzymes that can be classified according the ATP/ADP preference (Zimmermann, 2001, Bigonesse et al., 2004). NTPDase1 (CD39) hydrolyzes ATP and ADP almost equally well. NTPDase2 (CD39L1) has a large preference for ATP over ADP. NTPDase3 (CD39L3 or HB6) and NTPDase8 slightly prefer ATP over ADP by a ratio of about 3 and 2, respectively. The nucleotide AMP, which is the final product of ATP and ADP hydrolysis promoted by NTPDases, can be hydrolyzed by the action of an ecto-5′-nucleotidase, producing the neuromodulator adenosine. Ecto-5′-nucleotidase has a pivotal role together with the NTPDases in regulating the concentration of extracellular nucleotides and nucleosides to the purinoceptors (Zimmermann, 2001).
There are few studies demonstrating the effect of heavy metals on ecto-nucleotidases. Oliveira et al. (1994) investigated the in vitro and in vivo effect of HgCl2 on synaptosomal ATP diphosphohydrolase from cerebral cortex of developing rats. These authors observed contrasting results, whereas ATP and ADP hydrolysis were inhibited in vitro, exposure in vivo did not affect the nucleotide hydrolysis. Furthermore, Moretto et al. (2004) verified the subchronic (0.1 mg/kg; 30 doses/30 days) effect of HgCl2 on NTPDase and 5′-nucleotidase activity of adult rats, showing a significant increase on NTPDase activity, but not on 5′-nucleotidase activity.
Zebrafish is a consolidated model system in neuroscience and toxicological studies (Linney et al., 2004, Senger et al., 2005). The zebrafish genome project has demonstrated regions of syntenic relationship with human genome (Barbazuk et al., 2000). Purinoceptors were already identified in this teleost (Kucenas et al., 2003) and we characterized the presence of a NTPDase and an ecto-5′-nucleotidase activities in brain membranes of zebrafish (Rico et al., 2003, Senger et al., 2004). These enzymes were cation-dependent, with a maximal rate for nucleotide hydrolysis in a pH range of 7.5–8.0 in the presence of Ca2+ for NTPDase and Mg2+ for ecto-5′-nucleotidase (Rico et al., 2003, Senger et al., 2004).
Considering that mercury and lead are important environmental contaminants and previous studies have demonstrated the presence of purinergic receptors and enzyme activities involved in extracellular catabolism of nucleotides in zebrafish brain, the aim of present study was to investigate the effect of mercury chloride and lead acetate on NTPDase and ecto-5′-nucleotidase activities and expression in central nervous system of zebrafish.
Section snippets
Animals
Adult zebrafish were obtained from commercial suppliers and maintained at least for 2 weeks in a 50-L aquarium before the experiments. The fish of both sexes were kept at 25 ± 2 °C under a natural light–dark photoperiod. Animals feeding and maintenance of fishes were done according to Westerfield (2000). All procedures for the use of animals were according to the National Institute of Health Guide for Care and Use of Laboratory.
Chemicals
Mercury chloride (HgCl2, CAS Number 7487-94-7) and lead acetate [Pb(CH3
Results
The in vitro effects of mercury chloride and lead acetate on NTPDase and 5′-nucleotidase activities were evaluated in brain membranes of zebrafish. There was a significant decrease in ATP hydrolysis in all concentrations of mercury chloride tested (at the range 0.05–1 mM) and the inhibitory effect varied from 31 to 85%, respectively (Fig. 1). Mercury chloride also had an inhibitory effect in the concentrations of 0.25–1 mM for ADP (25–72%) and AMP hydrolysis (30–63%), respectively (Fig. 1). Lead
Discussion
This study reveals that in vitro and in vivo of exposure to HgCl2 and Pb(CH3COO)2 promoted significant changes on nucleotide hydrolysis in zebrafish brain membranes. During acute and chronic treatments, no changes on swimming patterns and mortality were observed between control and treated groups at the concentration tested. Our results are consistent with Gonzalez et al. (2005) that reported no changes on behavior and mortality of zebrafish exposed to low doses dietary methylmercury (MeHg)
Acknowledgements
This work was supported by Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES), Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq), Fundação de Amparo à Pesquisa do Rio Grande do Sul (FAPERGS) and Third World Academy of Sciences (TWAS). M.R.S. was recipient of fellowship from CAPES. E.P.R. and M.B.A. were recipient of fellowship from CNPq. The authors would like to thank the Instituto de Pesquisas Biomédicas (IPB-PUCRS) for technical support and D.B. Rosemberg
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