The polymorphism is located in the promoter region and cultured human kidney cells transfected Wee1 inhibitor with the rs28366003 G/G genotype responded with lower transcription efficiency to Cd exposure compared to cells transfected with the A/A genotype. While there are a number of polymorphisms in MT1A and MT2A, the minor allele frequency of the majority is low or unknown (http://www.ncbi.nlm.nih.gov/snp/). Variation of MT1A is described by three tagging SNPs, one of them is rs11076161, carrying information about variation in a larger genomic region (http://hapmap.ncbi.nlm.nih.gov/index.html.en).

In MT2A, only rs10636 and rs28366003 have minor allele frequency above 5%, which is suitable for gene–environment interaction analysis of medium size. However, it is not yet clear if these SNPs may modify Cd metabolism

and Cd-induced excretion of low molecular weight proteins in vivo. Our aim was to elucidate how variations in MT genes affect the metabolism of Cd and Cd-induced excretion of low molecular weight proteins. Therefore, inhabitants from areas to a varying extent polluted by Cd in South-Eastern China were genotyped for SNPs in MT1A (rs11076161) and MT2A (rs10636 and rs28366003). A cross-sectional study was performed in South-Eastern China in 2006 among persons with a history of Cd exposure through contaminated rice which is the main food consumed in this region (Jin et al., 1999 and Jin et al., 2002). The subjects included lived in either a Cd-polluted http://www.selleckchem.com/products/frax597.html area near a non-ferrous metal smelter or in a control area at 40 km from the smelter. Cd levels in rice in the contaminated areas, i.e. Methamphetamine Jiaoweibao (highly polluted) were 3.7 mg Cd/kg in rice on average, in Nanbaixiang (moderately polluted) 0.5 mg Cd/kg in rice, and these levels were higher than the State Hygienic Standard (0.2 mg Cd/kg). Yantuo (control area) demonstrated 0.072 mg Cd/kg in rice on average. In 1996, the residents of the Cd-contaminated areas were asked to stop

producing rice in their own fields and to eat commercial rice from non-polluted areas (0.03 mg Cd/kg). Based on registry information available from the local authorities, the characteristics of the populations (such as age, sex distribution and birth rate) were available for the three areas (highly polluted, moderately and control area). Data from nutrition surveys performed in the period after 1960 were collected and present nutritional status was assessed by means of a targeted interview of 10 families in each area. Participants were selected based on this information to ensure that living conditions, social and economic conditions, and lifestyles were similar in all areas. Only persons born in the respective areas who had lived there and consumed locally grown rice throughout their entire lifetime (apart from the years when the local rice was banned) were included in the present study.