Comparative Biochemistry and Physiology Part C: Toxicology & Pharmacology
Genes involved in cysteine metabolism of Chironomus tepperi are regulated differently by copper and by cadmium
Introduction
Gene expression patterns are being increasingly used to identify exposure to stressful environmental conditions. In aquatic environments, they are used to examine how organisms respond to toxicants and are favored because they have the potential to identify sublethal stress that can lead to environmental degradation (Adams et al., 1989, Galay-Burgos et al., 2003). As a result, the US EPA now accepts gene expression data as part of a weight-of-evidence approach for environmental assessment (Van Aggelen et al., 2010). Several studies have investigated transcriptomic responses to pollution in freshwater biota (e.g. Hook et al., 2008, Marinkovic et al., 2012) and for these data to be fully interpreted the underlying mechanisms causing changes in the transcriptome of studied species need to be understood.
Cysteine metabolism plays a central role in detoxification against environmental stressors (Jones et al., 2004, Sugiura et al., 2005) (Fig. 1). Demethylation and remethylation of methionine are essential to cellular repair and function (James et al., 2002, Chen et al., 2010). Cysteine can only be produced via the transsulfuration pathway and is required for proteins, including metallothionein (MT), that protect cells directly from metal stress. Cysteine is also a precursor for glutathione (GSH) and is involved in several antioxidant responses (Hughes et al., 2009). Several genes regulate cysteine metabolism and its intermediates, the transcription of these genes can report on dynamics of the cysteine metabolic pathway, which in turn can inform how an organism responds to stressors.
The Chironomidae (Diptera), particularly species from the genus Chironomus, are commonly used in toxicological testing as several species can be cultured in the laboratory (for example: Dawson et al., 2000, Martin et al., 2008, Stevens, 1993, Watts and Pascoe, 2000). Furthermore, Chironomus larvae tend to live on or in the sediments and are exposed to hydrophobic toxicants in sediment (Burton, 1991). Chironomus riparius (Chironomidae) is a standard test organism (US-EPA, 1996, OECD, 2004) and Chironomus tentans is widely used in toxicity testing (Martinez et al., 2003, Rakotondravelo et al., 2006, Lee and Choi, 2009). The transcriptome of C. riparius was recently investigated (Marinkovic et al., 2012), although only the responses of a few genes to different pollutants have been described in these species (Lee et al., 2006, Park and Kwak, 2008, Park et al., 2009, Planello et al., 2010). Neither of these species occurs in Australia, however Chironomus tepperi (Skuse) is widespread in the Australian mainland, can be easily cultured in the laboratory, and occurs in metal-contaminated habitats. While C. tepperi is used in toxicological testing, there is little sequence information and no gene expression data yet available for this species.
In this study, we isolate eight genes involved in the cysteine metabolism of C. tepperi using sequence alignments of conserved genes from other chironomid and dipteran species. The genes investigated encode enzymes involved in the remethylation cycle (S-adenosylmethionine synthetase; SAM and S-adenosylhomocysteine hydrolase; SAH), the transsulfuration pathway (cystathionine-γ-lyase; CγL, cystathionine-β-synthase; CβS, γ-glutamylcysteine synthase; GCS, and glutathione synthetase; GS) and two representing resulting stress response proteins (glutathione S-transferase delta 1; GSTd1 and metallothionein; Mtn). The transcriptional responses of these genes were characterized after 24 h exposures to two sublethal concentrations of copper (Cu: 0.05 mg/L and 0.5 mg/L) and cadmium (Cd: 0.25 mg/L and 0.5 mg/L). We show that these metals induce different changes in gene expression regulating for cysteine metabolism intermediates and products.
Section snippets
Organism
C. tepperi was cultured from a stock originating from Yanco Agricultural Institute in New South Wales as described previously in Townsend et al. (2012). Briefly, larvae were maintained in culture medium similar to Martin's solution (Martin et al., 1980) which contained reverse osmosis water with 0.12 mM NaHCO3, 0.068 mM CaCl2, 0.083 mM MgSO4, 0.86 mM NaCl, 0.015 mM KH2PO4, 0.089 mM MgCl2 and 0.1% (w/v) iron chelate at 21 °C ± 1 °C and a 16:8 h light:dark photoperiod. Ethanol-rinsed tissue paper was used
Gene sequence identification
All gene sequences identified with the exception of Mtn showed homology to target proteins when subjected to a BLASTx search against the Drosophila melanogaster annotated protein database (www.ncbi.nim.nih.gov). Amino acid alignments are displayed in Supplementary file 4. The SAH sequence top hit was CG9977 (GenBank accession no. NP647746) responsible for adenosylhomocysteine hydrolase activity, with 88% identity and an expect value (E) of 61e− 62. The fragment included the AdoHcyase domain (E =
Discussion
Here we have successfully isolated and characterized gene sequences involved in the cysteine metabolism of C. tepperi. The results suggest that cysteine metabolism is regulated differentially under copper and cadmium exposure. These changes in regulation often correlate with changes in protein or enzyme levels. In animals, the methionine/transsulfuration pathway is the only route for the production of cysteine (Rao et al., 1990, Sugiura et al., 2005). Furthermore, cysteine is an essential
Acknowledgments
We thank Steve Marshall, Rebecca Reid and Lee Engelstad for their technical support. This study was funded primarily by the Australian Research Council (Linkage and Fellowship schemes) and in part, by foundation funding granted to The Centre of Aquatic Pollution Identification and Management by The Victorian Science Agenda Investment.
Fund managed by the Department of Business and Innovation with partner funding contributed from Melbourne Water, Department of Primary Industries (Victoria), and
References (33)
- et al.
The use of biomarkers for assessing the effects of pollutant stress on fish
Mar. Environ. Res.
(1989) - et al.
Elevation in S-adenosylhomocysteine and DNA hypomethylation: potential epigenetic mechanism for homocysteine-related pathology
J. Nutr.
(2002) - et al.
Multi-level ecotoxicity assay on the aquatic midge, Chironomus tentans (Diptera, Chironomidae) exposed to octachlorostyrene
Environ. Toxicol. Pharmacol.
(2009) - et al.
Expression of heat shock protein and hemoglobin genes in Chironomus tentans (Diptera, Chironomidae) larvae exposed to various environmental pollutants: a potential biomarker of freshwater monitoring
Chemosphere
(2006) - et al.
Identification and characterization of eleven glutathione S-transferase genes from the aquatic midge Chironomus tentans (Diptera: Chironomidae)
Insect Biochem. Mol. Biol.
(2009) - et al.
Morphological abnormalities in Chironomus tentans exposed to cadmium- and copper-spiked sediments
Ecotoxicol. Environ. Saf.
(2003) - et al.
Characterization and expression during development and under environmental stress of the genes encoding ribosomal proteins L11 and L13 in Chironomus riparius
Comp. Biochem. Physiol. B Biochem. Mol. Biol.
(2007) - et al.
Expression of Chironomus riparius serine-type endopeptidase gene under di-(2-ethylhexyl)-phthalate (DEHP) exposure
Comp. Biochem. Physiol. B Biochem. Mol. Biol.
(2008) - et al.
Ecotoxicological multilevel-evaluation of the effects of fenbendazole exposure to Chironomus riparius larvae
Chemosphere
(2009) - et al.
Effect of acute exposure to cadmium on the expression of heat-shock and hormone-nuclear receptor genes in the aquatic midge Chironomus riparius
Sci. Total Environ.
(2010)
Role of the transsulfuration pathway and of gamma-cystathionase activity in the formation of cysteine and sulfate from methionine in rat hepatocytes
J. Nutr.
Food limitation in Chironomus tepperi: effects on survival, sex ratios and development across two generations
Ecotoxicol. Environ. Saf.
Induction profile of HSP70-cognate genes by environmental pollutants in Chironomidae
Environ. Toxicol. Pharmacol.
Assessing the toxicity of fresh-water sediments
Environ. Toxicol. Chem.
Regulation of homocysteine metabolism and methylation in human and mouse tissues
FASEB J.
Laboratory culture of Chironomus tentans for use in toxicity testing: optimum initial egg-stocking densities
Hydrobiologia
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