Changes of thyroid hormone levels and related gene expression in Chinese rare minnow (Gobiocypris rarus) during 3-amino-1,2,4-triazole exposure and recovery
Introduction
The thyroid hormones (THs) triiodothyronine (T3) and thyroxine (T4) have a wide range of biological effects in physiological processes of vertebrates (Power et al., 2001, Yen, 2001). T3 is derived from outer ring deiodination of T4 mediated by deiodinase enzyme (D1 and D2) resulting in an increased binding to TH receptors (Marchand et al., 2001, Orozco and Valverde, 2005) and exert its full biological activity (Orozco and Valverde, 2005). Transthyretin (TTR) is a specific TH transport protein in fish, and is a major carrier to transfer the hormones into the target cells (Morgado et al., 2007b). There is growing evidence that thyroid hormone synthesis, metabolism, and distribution may be targets for the interference by endocrine disruption chemicals (Cocco, 2002, Arukwe and Jenssen, 2005).
Many environment pollutants including aromatic hydrocarbons, halogenated aromatic hydrocarbons (dioxin, PCBs), organochlorine, organophosphorus, carbamate pesticides, chlorinated paraffins, cyanide compounds, methyl bromide, phenol, ammonia, metals (aluminum, arsenic, cadmium, lead and mercury), environmental steroids, and a variety of pharmaceutical agents are ubiquitous in the aquatic environment (Lans et al., 1993, Brouwer et al., 1998, Brouwer et al., 1999, Arukwe and Jenssen, 2005, Beck et al., 2006). Some ecotoxicological studies have indicated they could cause disturbances of thyroid hormone homeostasis, hypothyroidism and thyroid gland abnormalities in fish and humans (Langer et al., 2005, Langer et al., 2007, Zoeller, 2005).
The use of pesticides on agricultural land has resulted in contamination of adjacent surface waters (Guo et al., 2008, Singh and Singh, 2008). One of these pesticides, 3-amino-1,2,4-triazole (amitrole) has been shown to interfere normal function of thyroid system, which has a potential risk to aquatic organisms because of its relatively high water solubility (Zen et al., 2000). Measurable concentrations of amitrole in ground water were 1.1 μg/l (Bobeldijk et al., 2001). Previous studies confirmed that the primary target for the toxicity of amitrole is on the thyroid peroxidase with subsequent inhibitory actions on thyroid hormone synthesis (Strum and Karnovsky, 1971), but the impacts of amitrole contamination in aquatic ecosystems and, in particular, the effects on fish and potential thyroid axis disrupting capabilities remain to be elucidated.
Rare minnow (Gobiocypris rarus) is considered to be an appropriate species for the assessment of endocrine disrupting chemicals due to its small size, ease of culture, short life cycle and prolific egg production with high fertilization and hatching rates (Zha et al., 2007, Zha et al., 2008). Rare minnow is an ideal model fish in the laboratory. We have previously published the effects of environmental pollutants on expression of the vitellogenin and estrogen receptor genes in Chinese rare minnow (Zhang et al., 2008).
The changes of TH-related genes of fish have not been throughout investigated so far. The objectives of this study were as follows: to clone partial cDNA sequences of ttr, d1, d2, and trα in the rare minnow and quantify transcription rates using real-time polymerase chain reactions (PCR); to determine the regulation of mRNA transcription levels of these genes from liver and brain in adult rare minnow exposed to amitrole; to examine plasma T3 and T4 levels and to discuss the possible molecular mechanisms underlying toxic response.
Section snippets
Chemicals
Amitrole (purity >99%) was purchased from Sigma (Chemical Co., USA). Stock solutions of amitrole was prepared in distill water. To obtain the final concentration for exposure, the appropriate amount of the stock solution of amitrole was added to the aquarium water via polytetrafluorethylene (PFTE) and isoversinic tubes (Abimed, Langenfeld, Germany).
Test fish and culture conditions
The brood stock of rare minnow was raised in a flow-through system with dechlorinated tap water (pH 7.2–7.6; hardness 44.0–61.0 mg CaCO3/l) at a
Nucleotide and predicted amino acid sequences analysis
The ttr, d1, d2, and trα partial cDNAs were isolated and cloned from rare minnow. Cloned cDNAs were sequenced and compared to sequences available by BLAST in GenBank. The isolated nucleotide sequence of rare minnow d2 (88 bp) including 70 bp of 5′-untranslated region (UTR) and 18 bp of coding region showed high homology to the d2 (NM_212789) of zebrafish (Danio rerio) (97%). Phylogenetic analysis revealed TTR, D1, and TRα putative proteins in rare minnow had high amino acid similarities with those
Discussion
THs have been implicated as being important regulators of fish in differentiation, growth, metabolism, and salinity adaptation (Liu and Chan, 2002, Orozco et al., 2002, Crane et al., 2004). Previous studies indicate that if such processes are disturbed by endocrine disrupting compounds, this could have a dramatic impact on the thyroid endocrine system and reproduction (Mukhi and Patino, 2007). The development of bioassays that measure changes in gene expression provide molecular strategies and
Acknowledgements
This work was supported by National Basic Research Program of China (2009CB421605) and the National Natural Science Foundation of China (20737003 and 20877089).
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