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Int. J. Mol. Sci. 2011, 12(4), 2351-2382; doi:10.3390/ijms12042351

Individual Variations in Inorganic Arsenic Metabolism Associated with AS3MT Genetic Polymorphisms
Tetsuro Agusa 1,2, Junko Fujihara 1, Haruo Takeshita 1 and Hisato Iwata 2,*
Department of Legal Medicine, Faculty of Medicine, Shimane University, Enya 89–1, Izumo 693–8501, Japan
Center for Marine Environmental Studies (CMES), Ehime University, Bunkyo-cho 2–5, Matsuyama 790–8577, Japan
Author to whom correspondence should be addressed; Tel.: +81-89-927-8172; Fax: +81-89-927-8172.
Received: 9 February 2011; in revised form: 9 March 2011 / Accepted: 18 March 2011 / Published: 4 April 2011


: Individual variations in inorganic arsenic metabolism may influence the toxic effects. Arsenic (+3 oxidation state) methyltransferase (AS3MT) that can catalyze the transfer of a methyl group from S-adenosyl-l-methionine (AdoMet) to trivalent arsenical, may play a role in arsenic metabolism in humans. Since the genetic polymorphisms of AS3MT gene may be associated with the susceptibility to inorganic arsenic toxicity, relationships of several single nucleotide polymorphisms (SNPs) in AS3MT with inorganic arsenic metabolism have been investigated. Here, we summarize our recent findings and other previous studies on the inorganic arsenic metabolism and AS3MT genetic polymorphisms in humans. Results of genotype dependent differences in arsenic metabolism for most of SNPs in AS3MT were Inconsistent throughout the studies. Nevertheless, two SNPs, AS3MT 12390 (rs3740393) and 14458 (rs11191439) were consistently related to arsenic methylation regardless of the populations examined for the analysis. Thus, these SNPs may be useful indicators to predict the arsenic metabolism via methylation pathways.
arsenic; AS3MT; genetic polymorphism

1. Introduction

Groundwater pollution by inorganic arsenic (IA) derived from natural origin is a serious issue of public health in the world, especially in developing countries where clean and safe surface water is not available in many places. In these areas, high arsenic concentrations exceeding the WHO guideline (10 μg/L) for drinking [1] have been reported in the groundwater [24]. It is well known that IA is one of the carcinogenic chemicals for the human. Chronic arsenic exposure causes skin pigmentation, hyperkeratosis, and cancers in the skin, lung, bladder, liver, and kidney resulting in high mortalities [1,5,6].

In general, humans can metabolize ingested IA to monomethylated arsenic (MMA) and then dimethylated arsenic (DMA), through arsenic (+3 oxidation state) methyltransferase (AS3MT). The pathways are discussed in detail in a later section of this review. Urinary arsenical profile has been used to assess arsenic exposure and its metabolism in individuals. In general, concentration ratios of MMA/IA and DMA/MMA in the urine indicate first and second methylation capacity, respectively. The metabolic action of AS3MT is considered to have an association with accumulation profile of various arsenic compounds in the body and consequently with susceptibility to toxic effects of arsenic. Several previous epidemiological studies showed that people who had high percentage of DMA (%DMA) in the urine could excrete more arsenic from the body because of high arsenic methylation capacity [7,8]. In other epidemiological studies, high concentration or percentage of MMA in the urine of populations with arsenic-related diseases were reported when compared with that of healthy people [912].

Vahter [13] showed that relative distributions of IA, MMA, and DMA in the urine of various populations are generally 10–30%, 10–20%, and 60–70%, respectively. On the other hand, there are large variations in the arsenic metabolism at individual and population levels [7]. It is known that biological and environmental factors including age, sex, pregnancy, arsenic exposure level, smoking habits, nutritional status and diet, potentially relate to the inter-individual variation (reviewed by Tseng [14]). With regard to ethnic related variation, it was shown that Andes women in arsenic contaminated area had only a low percentage of MMA[V] (0–11%) in the urine [15], whereas residents ingesting arsenic through drinking water in the northeast Taiwan had an extraordinarily high %MMA[V] (26.9%) in the urine [16]. These results indicate that genetic polymorphisms of certain enzymes that can metabolize arsenic through methylation pathways may be one of factors associated with the variation of arsenic profiles.

Genetic analyses of SNPs in the enzymes that may be involved in arsenic metabolism have been recently developed to evaluate the variation in the metabolism or toxic impacts of arsenic at individual or population level. We have also reported the association of arsenic metabolism-SNPs in AS3MT in Vietnamese [1721]. However, a limited number of publications regarding the association of SNPs in AS3MT with arsenic methlyation are available. Moreover, the published results are based on fragmentary investigations and thus consistent conclusions have not yet been drawn. Hernandez and Marcos [22] have recently reviewed the role of genetic polymorphisms in enzymes related to arsenic metabolism including AS3MT. Thereafter, the number of publications regarding genetic polymorphisms dependent metabolism and toxicity of arsenic is increasing.

In this short-review, we address the following three topics: (1) enzymatic processes of arsenic methylation by AS3MT; (2) associations of genetic polymorphisms in AS3MT with variation in arsenic methylation; (3) frequency distributions of genetic polymorphisms in AS3MT at population levels. Based on the summarized data, we suggest which SNPs in AS3MT gene play an important role in arsenic methylation. In addition, we discuss future issues to be solved.

2. Arsenic Methylation by Human AS3MT

Two distinct pathways of IA methylation (oxidative and reductive) have been proposed (Figure 1). A model of oxidative methylation of IA was proposed by Challenger [23] and Cullen and Reimer [24]. By the combination of oxidative methylation and other pathways, arsenate (As[V]) is transformed to dimethylarsinous acid (DMA[III]); arsenate (As[V]) → arsenite (As[III]) → monomethylarsonic acid (MMA[V]) → monomethylarsonous acid (MMA[III]) → dimethylarsinic acid (DMA[V]) → dimethylarsinous acid (DMA[III]) (Figure 1). However, this sequential pathway does not fully explain the reason why the intermediate species, DMA[V] is detected as a major arsenical in the urine of humans. Methylation has been considered as a detoxification process of IA, because toxicities of MMA[V] and DMA[V] are much lower than that of IA. On the other hand, later studies revealed that MMA[III] or DMA[III] are more cytotoxic and genotoxic than IA [25,26], suggesting that oxidative methylation of IA is a bioactivation process.

On the contrary, Hayakawa et al. [27] reported a reductive methylation model for the metabolism of arsenic compounds. In this model, trivalent arsenicals are conjugated with glutathione (GSH) and then are methylated; As[III] → arsenotriglutathione (As[III](GS)3) → monomethylarsenodiglutathione (MMA[III](GS)2) → dimethylarsenoglutathione (DMA[III](GS)) (Figure 1). MMA[III](GS)2 and DMA[III](GS) are then oxidized to MMA[V] and DMA[V], respectively. Naranmadura et al. [28] investigated hepatic and renal metabolites of arsenic after an intravenous injection of As[III] (0.5 mg As/kg body weight) in rats. The authors proposed that trivalent arsenic species can bind to thiol groups in proteins. The protein-bound arsenicals are released from the proteins by conjugation with GSH to form As[III](GS)3 or MMA[III](GS)2 or DMA[III](GS) [28]. Hence, in the reductive methylation, MMA[V] and DMA[V] could be the end products. This hypothesis is consistent with the results that DMA[V] is found as a major arsenical in the urine. This sequential reaction is considered to be a detoxification process of IA, because of the low toxicities of MMA[V] and DMA[V].

Through both oxidative and reductive metabolic pathways, AS3MT plays an important role on arsenic methylation (Figure 1). Lin et al. [29] succeeded in purifying arsenic (III) methyltransferase (previously called as Cyt19) from the liver cytosol of adult male Fischer 344 rats. AS3MT is an S-adenosyl-L-methionine dependent enzyme and could methylate trivalent arsenicals [29,30]. Human AS3MT gene is composed of 32-kb with 11 exons [30]. Variety of genetic polymorphisms including SNPs and variable number of tandem repeats (VNTRs) have been identified in this gene [30,31]. This indicates that these genotypes may influence the methylation capacity of arsenic compounds and subsequently the arsenic toxicity. Recently, Kojima et al. [32] reported that methylation of IA by AS3MT induces oxidative DNA damage and increase their carcinogenicity in vitro. In the following section, we summarize in vitro and epidemiological studies on the AS3MT genetic polymorphism-dependent metabolism of arsenic compounds.

3. Association of Arsenic Methylation with Genotypes in Human AS3MT

Notation of SNPs in human AS3MT is individually defined among studies. In this review, we use the notation by SNP ID which indicates the polymorphism identification number relative to the location in the consensus sequence (AY817668) with the first base of the consensus number 1 and dbSNP rs# cluster id which is available on Search for SNP on NCBI Reference Assembly [33]. Chromosome positions of genetic polymorphisms in AS3MT are indicated in Figure 2.

3.1. In Vitro Studies

Drobna et al. [34] reported the association of genotypes in AS3MT with arsenic methylation in human hepatocytes. They treated primary hepatocytes from eight human donors with graded concentrations of As[III] (0.330 nmol/mg protein) for 24 h to evaluate the variation in arsenic metabolism. One of eight donor’s cells showed a higher methylation rate than other cells at a high exposure level (30 nmol/mg protein). The methylation rate was consistent with heterozygote of Met287Thr at amino acid base (14458 at nucleotide base, rs11191439) mutation of AS3MT, suggesting a linkage of this genotype with arsenic methylation.

In vitro functional analysis of human AS3MT was performed by Wood et al. [30]. The authors initially sequenced DNA samples from African-American (n = 60) and Caucasian-American (n = 60), and identified 26 SNPs and one VNTR. Among the SNPs, three SNPs, Arg173Trp, Met287Thr, and Thr306Ile in the exon region were non-synonymous. In the AS3MT-expressed COS-1 cells, which was treated with 12.5 nM As[III], the enzyme activity and immunoreactive protein expression of 287Thr variant of AS3MT were significantly higher than those of the wild type, whereas 173Trp and 306Ile variants showed opposite trends. Reporter gene assays using reporter constructs containing different length 5′-UTR VNTR sequences of AS3MT gene demonstrated that the transcriptional expression of this gene depends on the number of the repeat sequence. Given these results, the authors suggested genetic polymorphisms in AS3MT may contribute to individual differences in the expression and function of AS3MT, and, consequently, to variation in the risk of arsenic-dependent carcinogenesis.

3.2. Human Case Studies

3.2.1. Mexico

Case studies on human populations regarding the AS3MT polymorphism have recently started. Genetic association of AS3MT with urinary arsenic metabolite levels in residents (n = 135) ingesting arsenic (5.5–43.3 μg/L) through drinking water from the Yaqui Valley of Sonora, Mexico, was reported by Meza et al. [35]. The authors found that three unexonic SNPs (2393 at ATG offset position (SNP ID; AS3MT 7395, rs#; rs12767543), 7388 (AS3MT 12390, rs3740393), and 30585 (AS3MT 35587, rs11191453)) in AS3MT were significantly associated with DMA[V]/MMA[V] in the urine of the entire population. Subsequent analysis showed that these relationships were observed only in children (7–11 years), but not for adults (18–79 years); DMA[V]/MMA[V] for AS3MT 7395 (rs12767543) AG + AA, 12390 (rs3740393) CG + CC, and 35587 (rs11191453) CT + CC were higher than that for AS3MT 7395 (rs12767543) GG, 12390 (rs3740393) GG, and 35587 (rs11191453) TT, respectively. The linkage disequilibrium (LD) analysis revealed that these SNPs have significant LD, with r2 = 0.56 for AS3MT 7395 (rs12767543) and 35587 (rs11191453), and r2 = 0.94 for AS3MT 12390 (rs3740393) and 35587 (rs11191453). In addition, AS3MT 35587 (rs11191453) CT + CC had significantly higher As[III]/MMA[V] than AS3MT 35587 (rs11191453) TT for children.

Following the above initial study, the same group [36] found a clear association of percentage of (%) MMA[V] with genetic polymorphism in AS3MT 35587 (rs11191453) only for children. However, given that the participant selection may be biased; children of the above study belong to more indigenous American ancestry than adults [33,34], these age-dependent associations of genetic polymorphisms in AS3MT with arsenic metabolism need reconsideration.

According to Valenzuela et al. [37], AS3MT polymorphisms may influence skin lesions caused by arsenic exposure through drinking water. This group investigated three SNPs, AS3MT 4602 (rs7085104), 14458 (rs11191439, Met287Thr), and 35587 (rs11191453) in 71 individuals with skin lesions and 51 controls without the lesions from Zimapan, Hidalgo in Mexico. In this study area, medians of arsenic concentrations in wells and human urine samples were 84 μg/L and 109 μg/g creatinine, respectively. No significant association of AS3MT 35587 (rs11191439) was found with arsenic metabolism and skin disease. Among the subjects, AS3MT 4602 (rs7085104) GG carriers had lower %MMA[III + V], but higher %DMA[III + V] and DMA[III + V]/MMA[III + V] than 4602 (rs7085104) AA + AG carriers. The percentages of IA[V] and MMA[III + V] in AS3MT 14458 (rs11191439) CT + CC carriers were significantly higher than those in AS3MT 14458 (rs11191439) TT carriers. This suggests that AS3MT 14458 (rs11191439) CT + CC carriers may have a poor methylation capacity. Interestingly, the frequency of this SNP carriers in the skin lesion group was marginally (p = 0.055) higher than the control subjects, suggesting that AS3MT 14458 (rs11191439) CT + CC may be involved in skin lesions. Although the way in which genetic polymorphism of AS3MT 14458 (rs11191439) affects skin lesions is not clear, it can be presumed that the skin disease may be related to the metabolic pathway of IA.

Recently, from a large sample size (n = 405), Gomez-Rubio et al. [38] found significant associations of unexonic AS3MT 7395 (rs12767543), 12390 (rs12767543), 14215 (rs3740390), 30312 (rs10883795), 35587 (rs11191453), 35739 (rs11191454), and 37219 (rs1046778), with urinary DMA[V]/MMA[V], also showing strong LD. For example, DMA[V]/MMA[V] was higher in CC genotype of AS3MT 30312 (rs10883795), followed by TC and TT genotypes. On the contrary, exonic AS3MT 14458 (rs11191439) showed no significant association with arsenic methylation, probably due to the small number of variants for this SNP. As described earlier, a previous study by this group revealed a children specific association of AS3MT genotypes with arsenic metabolism [35,36], but the association was also observed in adults when analyses were performed using a large number of subjects [38].

Sampayo-Reyes et al. [39] evaluated DNA damages by a comet assay in residents who were exposed to IA from drinking water (1–187 μg/L) in Torreon, Coahuila, Mexico. The results revealed a significant positive correlation between DNA damages and urinary arsenic concentrations, suggesting that this population is under threat by exposure to arsenic. Furthermore, AS3MT 14458 (rs11191439, Met287Thr) influenced DNA damages in children; DNA damages of subjects having AS3MT 14458 (rs11191439, Met287Thr) C allele were higher than those having T allele (p = 0.034). Hence, the authors suggested that the arsenic exposure through drinking water induces DNA damage and this effect may become more profound by AS3MT 14458 (rs11191439, Met287Thr).

3.2.2. Argentina

Significant relationships between genetic polymorphisms in AS3MT and arsenic metabolism in Argentina were reported by Schläwicke Engström et al. [40]. This group analyzed arsenic compounds in the urine, whole blood, and buccal cells and polymorphisms in AS3MT of 147 indigenous women from a village in the northern Argentinean Andes. The residents have been exposed to high levels (about 200 μg/L) of arsenic through drinking water. For AS3MT, nine polymorphisms (AS3MT 5019 (rs17880342), 5194 (rs3740400), 8788 (rs17881367), 12390 (rs3740393), 12590 (rs3740392), 14215 (rs3740390), 14458 (rs11191439), and 35991 (rs10748835)) were identified. Among these SNPs, intronic AS3MT 12390 (rs3740393), 14215 (rs3740390), and 35991 (rs10748835), which had a strong LD with each other (r2 = 0.74–0.95), were significantly associated with the secondary methylation step of arsenic. For example, AA type of AS3MT 35991 (rs10748835) had a lower %MMA[V] and higher %DMA[V] and DMA[V]/MMA[V] ratios in the urine than the GG and GA types. They also found that the genotype frequencies in three SNPs in AS3MT, which had correlations with the secondary methylation of arsenic in a population of Argentina, were higher than those in other populations. This may be due to a positive selection of AS3MT genetic polymorphisms that can efficiently metabolize arsenic for detoxification, because these populations have suffered from arsenic toxicity for thousands of years [41,42].

Recently, Schläwicke Engström et al. [43] genotyped another two SNPs, AS3MT 4602 (rs7085104) in 5′ terminal and AS3MT 5194 (rs3740400) in intron 1, and evaluated the influences on arsenic metabolism in the same subjects as in the previous cases. These SNPs comprised a strong LD (r2 = 0.97) with each other and also with AS3MT 12390 (rs3740393), 14215 (rs3740390), and 35991 (rs10748835) which were reported in the previous study [40]. This LD cluster was found only in this Argentinean population, but not in other HapMap populations. The SNPs, AS3MT 4602 (rs7085104) and 5194 (rs3740400) were clearly associated with %MMA[V] and %DMA[V].

3.2.3. Chile

Hernández et al. [44] investigated 50 workers who have been occupationally exposed to high levels of arsenic in a copper smelting plant in Chuquicamata, Chile. Mean values of exposure periods and total arsenic concentration in the urine of the workers were 15.55 years and 152.8 ppb, respectively. In this study, nine polymorphisms were found from the sequencing of exons and flanking regions of AS3MT gene. Three polymorphisms, AS3MT 4965 (rs17881215), exon 1: 5′-UTR (inside VNTR), and 14458 (rs11191439) in AS3MT, which comprised one LD cluster, were significantly associated with the variation in %MMA[V].

To confirm the genetic polymorphism-dependent metabolism of arsenic, Hernández et al. [45] re-investigated the relationships of the arsenic profile and AS3MT SNPs in larger population (n = 207), in which the urine had 91.26 ppb of the arsenic level on average. The results revealed that exonic AS3MT 14458 (rs11191439) TC + CC showed higher %MMA[V] in the urine than the wild type as observed in the previous study [44]. In summary, the authors concluded that AS3MT 14458 (rs11191439) TC + CC genotypes increase the methylation capacity from IA to MMA.

3.2.4. Central Europe

Lindberg et al. [46] investigated the association between the genetic polymorphism in AS3MT and arsenic metabolism in populations from Hungary, Romania and Slovakia (n = 415) that have been exposed to low arsenic levels. This investigation is distinct from others, and is meaningful because variation of the arsenic metabolism depending on the exposure could be negligible. Even though the median urinary arsenic concentration of the individuals was low (8.0 μg/L), percentages of arsenic compounds in the urine varied widely. Through the multivariate analysis, they found that AS3MT 14458 (rs11191439) in exon was one of the major factors that can influence arsenic metabolism; the TC + CC type had higher %MMA[V] and lower %DMA[V] than the TT type. This trend was much more pronounced in men than in women.

3.2.5. India

West Bengal in India is one of the most severe arsenic endemic areas in the world. It has been estimated that about 6,000,000 people are exposed to arsenic through the consumption of groundwater [3]. However, only 300,000 individuals (5% of total exposed population) within this population had arsenic-related disease [47]. De Chaudhuri et al. [48] hypothesized that low occurrence of the disease may be related to the genetic variability. Hence, the association of exonic genetic polymorphisms in AS3MT with the occurrence of arsenic-induced skin lesions was investigated. They first analyzed 13 genotypes in AS3MT in 25 cases with skin lesions and 25 controls from North 24 Parganas, Nadia, and Murshidabad Districts in West Bengal, and identified eight common genotypes. Mean concentrations of arsenic in drinking water and human urine were 163.16 μg/L and 301.17 μg/L, respectively, in the cases with skin lesions, and 161.71 μg/L and 283.28 μg/L, respectively, in controls. For these samples, there were no significant differences in the arsenic concentrations between case and control groups. On the other hand, arsenic concentrations in nail and hair of case subjects (5.39 μg/g dry wt and 3.13 μg/g dry wt, respectively) were significantly higher than those of control group (2.39 μg/g dry wt and 1.61 μg/g dry wt, respectively). The authors did not carry out urinary arsenic speciation and thus they did not mention arsenic methylation. Among the identified eight genotypes, AS3MT 14458 (rs11191439) was genotyped in 229 cases and 199 controls, and the distribution of genotype frequencies was compared between cases and controls. However, no significant difference was detected between the two groups, and thus the exonic genetic polymorphisms in AS3MT may not be linked to the occurrence of arsenic-induced skin lesions.

3.2.6. Taiwan

Chung et al. [49] attempted to evaluate the impact of AS3MT 12390 (rs3740393) in intron 6 on the cancer prevalence in arsenic-endemic areas of Taiwan. The authors conducted a 15 years follow-up study (1988–2004) in Homei, Funshin, and Hsinming villages in Putai Township of Chiayi County, where the highest prevalence of Black Footed Disease has been observed. During these 15 years, total arsenic concentration, %IA, and %MMA[V] significantly decreased, while contrasting results were observed for %DMA[V], (MMA[V] + DMA[V])/total arsenic, and DMA[V]/MMA[V]. Individuals with higher %MMA[V] in 1988 and with little change in %MMA[V] during these 15 years had higher cancer risk, but its significance level was low (p < 0.1). These results imply that %MMA[V] is a potential predictor of the cancer risk. Seventeen cases with cancers identified by the National Cancer Registry Systems and 191 controls were investigated, but AS3MT 12390 (rs3740393) showed no significant effect on the cancer risk. On the other hand, a general linear model (GLM), which was adjusted for age, sex, and education level, revealed that AS3MT 12390 (rs3740393) GC genotype had lower %MMA[V] and higher %DMA[V] and DMA[V]/MMA[V] than the GG genotype. This suggests that the GC carrier may have a higher methylation capacity from MMA to DMA and this SNP may be an indicator of individual cancer susceptibility in relation to MMA%.

3.2.7. Vietnam

Arsenic pollution in groundwater in Vietnam was reported by Berg et al [50]. The authors detected more than 3,000 μg/L of As concentration in groundwater from around Hanoi. Following this initial attempt, many studies have reported the concentration and distribution patterns of As in groundwater and sediment samples in northern and southern Vietnam [5156].

While intensive studies have focused on the levels of arsenic in environmental samples, there is little information on arsenic exposure to, and toxic impacts on, local residents [18,53,5761]. Furthermore, frequency distribution of AS3MT polymorphisms and the association with arsenic methylation ability have not yet been clarified. Hence, our group has investigated arsenic exposure, methylation capacity, and SNPs in AS3MT in Vietnamese [1721].

To clarify the relationship between arsenic methylation and SNPs in AS3MT, we collected groundwater as well as human hair, urine, and blood samples from Hoa Hau and Liem Thuan in Ha Nam Province, which are located in the Red River Delta. For the human samples, each arsenic compound was quantified and 17 SNPs in AS3MT were genotyped [17,18,20]. The arsenic level in filtered water that some families consumed in Hoa Hau drastically (around 93%) decreased when compared with that in raw groundwater. Geometric means (GMs) of arsenic concentration in drinking water (50.1 μg/L) and human hair (0.351 μg/g dry wt) from Hoa Hau were significantly higher than those from Liem Thuan (1.7 μg/L in the water and 0.232 μg/g dry wt in the hair). On the other hand, there was no significant difference in urinary arsenic level and composition of arsenicals between Hoa Hau (GM, 92.6 μg/g creatinine) and Liem Thuan (GM, 97.9 μg/g creatinine), suggesting that the residents in Hoa Hau have not recently been exposed to arsenic through drinking water and/or there are arsenic sources other than drinking water in Liem Thuan. Among the 17 SNPs in AS3MT investigated, 14 unexonic SNPs were categorized into four LD clusters; AS3MT 3963 (rs7098825), 6144 (rs17878846), 12390 (rs3740393), 14215 (rs3740390), 35587 (rs11191453), and 37950 (rs17879819) as cluster 1, AS3MT 4602 (rs7085104), 35991 (rs10748835), and 37853 (rs11191459) as cluster 2, AS3MT 4740 (rs12416687) and 12590 (rs3740392) as cluster 3, and AS3MT 5913 (rs4917986), 9749 (rs17881367), and 27215 (rs11191446) as cluster 4. We also found that sex, age, and body mass index (BMI) are correlated with urinary arsenic profile in this Vietnamese population. Thus, to understand the SNP-dependent association with arsenic metabolism without co-effects, we further conducted an analysis that was adjusted for sex, age, and BMI and detected significant associations for 12 SNPs. In cluster 1, homozygotes in AS3MT 12390 (rs3740393) GG and 35587 (rs11191453) CC had lower DMA[V]/MMA[V] in the urine, suggesting low methylation capacity from MMA to DMA for homo types of these SNPs. All homozygotes for AS3MT 4602 (rs7085104) GG, 35991 (rs10748835) AA, and 37853 (rs11191459) AA in cluster 2 had lower %DMA[V] in the urine, when compared with other genotypes in the corresponding SNP. For AS3MT 37853 (rs11191459), %MMA[V] in AA homozygote was lower than in GG type. LD cluster 3 (AS3MT 4740 (rs12416687) and 12590 (rs3740392)) showed significant associations with urinary %DMA[V]. For AS3MT 12590 (rs3740392), the TT type had a higher DMA[V]/MMA[V] ratio in urine than other genotypes, suggesting the prompted second methylation capacity. The LD group including AS3MT 5913 (rs4917986), 9749 (rs17881367), and 27215 (rs11191446) (cluster 4) had a correlation with %MMA[V]. For AS3MT 5913 (rs4917986), TC type had a higher MMA[V]/IAs than TT type, suggesting that the SNP may be related to the first methylation process of As. AS3MT 27215 (rs11191446) AA had a higher DMA[V]/MMA[V] and a lower MMA[V]/IA than SNP27215 (rs11191446) AG. Apart from LD clusters, AS3MT 8979 (rs7920657) AA showed a low %DMA[V] compared with other genotypes. Heterozygote for exonic AS3MT 14458 (rs11191439, Met287Thr) TC had a higher MMA[V]/IAs in urine than TT homozygote, indicating that the heterozygote may have a stronger methylation ability of IAs.

4. Allele Frequency of SNPs in AS3MT

As we have mentioned above, several SNPs in AS3MT may influence arsenic metabolism. However, only limited information on frequencies of genetic polymorphisms in AS3MT was available for the number of the SNPs and the association with ethnicity. We have reported distribution of SNPs in AS3MT in some Asian [Japanese (JP), South Koreans (SKR), Chinese (CH), Mongolians (MN), Tibetans (TIB), Nepalese (NP), Vietnamese (VN), Sri Lanka-Tamils (SLT), Sri Lanka-Sinhalese (SLS)] and African [Ovambos (OVA) and Ghanaians (GH)] populations since 2007 [18,20,6265].

The summarized results are shown in Table 1. The genotype frequencies followed the Hardy–Weinberg Principle except for 4602 (rs7085104) in MN, 6144 (rs17878846) in CH and TIB, 7395 (rs12767543) in SKR and VN, 9749 (rs17881367) in MN, 12390 (rs3740393) in JP, 12590 (rs3740392) in JP, 14215 (rs3740390) in JP, SKR, MN, and GH, 26790 (rs11191445) in JP, 35587 (rs11191453) in JP, SKR, MN, TIB, and VN, 37616 (rs4568943) in JP, CH, Mongolians, and OVA, and 37950 (rs17879819) in OVA. Because no genotyping error was observed in duplicate analysis, the reason that some genotype frequencies did not follow the Hardy–Weinberg Principle may probably be due to the small sample size. The allele frequencies of SNPs of Japanese in Tokyo, Japan (JPT (J)), Han Chinese in Beijing, China (CHB (H)), Chinese in Metropolitan Denver, Colorado (CHD (D)), Luhya in Webuye, Kenya (LWK (L)), Maasai in Kinyawa, Kenya (MKK (K)), Yoruban in Ibadan, Nigeria (YRI (Y)), African ancestry in Southwest USA (ASW (A)), Tuscan in Italy (TSI (T)), Utah residents with Northern and Western European ancestries from the CEPH collection (CEU (C)), Gujarati Indians in Houston, Texas (GIH (G)), and Mexican ancestry in Los Angeles, California (MEX (M)) that are available in the International HapMap Project [31], were compared with our studies (Figure 3). While the distribution patterns of AS3MT 4602 (rs7085104), 9749 (rs17881367), 12390 (rs3740393), 12590 (rs3740392), and 27215 (rs11191446) polymorphisms were not drastically different among the populations, notable variations were found for other SNPs. For AS3MT 3963 (rs7098825), C alleles were low in SLT, SLS, OVA, GH, YRI (Y) and CEU (C), particularly in MN. NP has no C allele of AS3MT 4740 (rs12416687). Relatively high frequencies of AS3MT 7395 (rs12767543) A allele and 8979 (rs72920657) A allele were found in CH and VN, respectively. AS3MT 6144 (rs17878846) A allele, AS3MT 37616 (rs4568943) A allele, and AS3MT 37950 (rs17879819) C allele frequencies in OVA and GHA populations were higher than Asians, but comparable with those in MN. Frequencies of AS3MT 10209 (rs3740394) A allele, AS3MT 26790 (rs11191445) C allele, and AS3MT 35991 (rs10748835) A allele in Asians (except for AS3MT 35991 (rs10748835) A allele in OVA) were higher than those in other ethnic groups, while the opposite trend was observed for AS3MT (rs11191439) T allele. For AS3MT 14215 (rs3740390), the allele distribution was different even within Chinese (CH vs CHB(H) and CHD(D)) and African groups (OVA and GH vs LWK(L), MKK(K), YRI(Y), and ASW(A)). TIB also showed a different pattern of AS3MT 14215 (rs3740390) allele from other Asian populations. Relatively lower C allele frequency of AS3MT 25986 (rs7085854) was detected in JP, JPT, SKR, and MN. TIB showed different allele distribution of AS3MT 35587 (rs11191446). To understand these variations, further research is necessary.

5. Conclusions and Future Perspectives

In this review, we summarized recent results on association of AS3MT genetic polymorphism with arsenic methylation. Although there are some inconsistencies between the genotypes and metabolism in human case studies, we found consistent results on two SNPs, AS3MT 12390 (rs3740393) in intron and 14458 (rs11191439, Met287Thr) in exon, in all the nations (Figure 4 and Table 2). This indicates that these SNPs may be ethnically independent polymorphisms, but may affect arsenic methylation.

AS3MT 12390 (rs3740393) is an intronic polymorphism, but the genotype with C allele in this SNP may have a higher second methylation capacity as predicted from the consistent results of high DMA[V]/MMA[V] in Mexicans, Argentines, Taiwanese, and Vietnamese (Table 2). Although AS3MT 12390 (rs3740393) belongs to a LD cluster in these populations, other SNPs within the cluster are different among populations (Table 2). Therefore, AS3MT 12390 (rs3740393) may be involved in an independent reaction from other SNPs in the same LD on a worldwide population basis. The frequency of AS3MT 12390 (rs3740393) CC or CG types was much higher than the GG type in Argentina’s population; the allele frequencies of C and G were 72% and 28%, respectively [40]. This allele frequency distribution was drastically different from other populations (Table 1 and Figure 3). This unique distribution may contribute to the results indicating that Argentina’s population has a higher %DMA and a lower %MMA in the urine, when compared with yet another study [15]. It is noteworthy to study whether this specific genotype distribution of AS3MT 12390 (rs3740393) is observed only in this group (Argentinean Andes) and how this unique SNP selection took place.

AS3MT 14458 (rs11191439), locates in the exon region, is synonymous substitution (Met to Thr substitution) at the amino acid base 287, and its functional difference has been investigated in some studies. By reviewing the in vitro [30,34] and human case studies [1721,3540,4349], we found that C allele containing genotype in this SNP consistently showed a higher first methylation capacity than the T allele carrier. Interestingly, the effect of this SNP has been observed even in subjects exposed to low levels of arsenic [46]. Hence, it seems that the association of AS3MT 14458 polymorphism with arsenic methylation may occur irrespective of arsenic exposure status. This allele frequency was relatively low in Asian populations (Table 1 and Figure 3), indicating that among different global populations, Asians may be genetically less sensitive to arsenic methylation.

Increased %MMA in the urine linked to cancer risk has been suggested in previous epidemiological studies [912]. Thus, AS3MT 14458 (rs11191439) C allele carriers, who have a higher methylation capacity from IA to MMA, may be at higher risk of arsenic related cancers. The association of this SNP with human health effect was investigated in Mexicans [37] and Indians [48]. According to the study by De Chaudhuri et al. [48], there was no significant interaction between this SNP and skin lesions. On the other hand, Valenzuela et al. [37] found higher frequency of C allele type of AS3MT 14458 (rs11191439) TC + CC in people with cancers, although the level of significance was not high (p = 0.055). Hence, at present, no rigid evidence has been provided to link the AS3MT 14458 (rs11191439) dependent variation in arsenic methylation to arsenic-induced carcinogenesis. Apart from an evidence of cancer, Sampayo-Reyes et al. [39] found that AS3MT 14458 (rs11191439) is linked with DNA damages among children living in arsenic contaminated sites in Mexico (p = 0.034). Although these authors did not analyze arsenic compounds in urine and thus did not take into consideration the methylation capacity, they suggested that increased production of MMA[III] during methylation processes in AS3MT 14458 (rs11191439, Met287Thr) C allele carrier might induce genotoxicity.

Up to now, it still remains unknown how AS3MT 12390 (rs3740393) and 14458 (rs11191439) can influence the structure and function of this enzyme. Also, several results of AS3MT genotype-dependent arsenic methylation are interesting, because some non-exonic (intron, UTR, or 5′ and 3′ gene) SNPs may play important roles during methylation. The study on splicing variants of AS3MT gene and their function is one such issue to be pursued.

There are several tasks for future study regarding the role of AS3MT polymorphisms on arsenic methylation. As shown in this review, most studies encompassed only a small number of subjects and SNPs in AS3MT and thus, they merely provide fragmental and weak significant results at particular level(s). As shown in Table 2, results on the genotype association of AS3MT 4602 (rs7085104), 5194 (rs3740400), 7395 (rs12767543), 12590 (rs3740393), 14215 (rs3740390), 35587 (rs11191453), and 35991 (rs10748835) with arsenic metabolism were not consistent among different country groups. Larger scale studies would be required to gain enough statistical power and strengthen currently proposed assumptions on the linkages of AS3MT SNPs with arsenic methylation and cancer risk.

SNPs in AS3MT can provide useful information on the medical treatment of some diseases or risk assessment. For example, arsenic trioxide has been used for the treatment of acute promyelocytic leukemia, although the systematic mechanism is not fully understood [66]. The information on gene-arsenic interactions presented here can be applied to a personalized medicine for leukemia or other cancers. To better understand the variations in arsenic metabolism and to assess the potential susceptibility to its toxic and carcinogenic effects at individual and population levels, more comprehensive studies would be necessary.


We are grateful to A. Subramanian, CMES, Ehime University for critical reading of the manuscript. This study was mainly supported by Global COE Programs from the Ministry of Education, Culture, Sports, Science, and Technology (MEXT), Japan and Japan Society for the Promotion of Science (JSPS), Japan. The award of the JSPS Post Doctoral Fellowship for Researchers in Japan to T. Agusa (No. 207871) is also acknowledged.


  1. Guidelines for Drinking Water Quality, 3rd ed; World Health Organization: Geneva, Switzerland, 2004.
  2. Mandal, BK; Suzuki, KT. Arsenic round the world: A review. Talanta 2002, 58, 201–235. [Google Scholar]
  3. Nordstrom, DK. Public health. Worldwide occurrences of arsenic in ground water. Science 2002, 296, 2143–2145. [Google Scholar]
  4. Smedley, PL; Kinniburgh, DG. A review of the source, behavior and distribution of arsenic in natural waters. Appl. Geochem 2002, 17, 517–568. [Google Scholar]
  5. Wu, MM; Kuo, TL; Hwang, YH; Chen, CJ. Dose-response relation between arsenic concentration in well water and mortality from cancers and vascular diseases. Am. J. Epidemiol 1989, 130, 1123–1132. [Google Scholar]
  6. Tondel, M; Rahman, M; Magnuson, A; Chowdhury, IA; Faruquee, MH; Ahmad, SA. The relationship of arsenic levels in drinking water and the prevalence rate of skin lesions in Bangladesh. Environ. Health Perspect 1999, 107, 727–729. [Google Scholar]
  7. Vahter, M. Variation in human metabolism of arsenic. In Arsenic Exposure and Health Effects; Chappell, WR, Abernathy, CO, Calderon, RL, Eds.; Elsevier Science, Ltd: Oxford, UK, 1999; pp. 267–279. [Google Scholar]
  8. Concha, G; Nermell, B; Vahter, MV. Metabolism of inorganic arsenic in children with chronic high arsenic exposure in northern Argentina. Environ. Health Perspect 1998, 106, 355–359. [Google Scholar]
  9. Del Razo, LM; Garcia-Vargas, GG; Vargas, H; Albores, A; Gonsebatt, ME; Montero, R; Ostrosky-Wegman, P; Kelsh, M; Cebrian, ME. Altered profile of urinary arsenic metabolites in adults with chronic arsenicism. A pilot study. Arch. Toxicol 1997, 71, 211–217. [Google Scholar]
  10. Valenzuela, OL; Borja-Aburto, VH; Garcia-Vargas, GG; Cruz-Gonzalez, MB; Garcia-Montalvo, EA; Calderon-Aranda, ES; Del Razo, LM. Urinary trivalent methylated arsenic species in a population chronically exposed to inorganic arsenic. Environ. Health Perspect 2005, 113, 250–254. [Google Scholar]
  11. Steinmaus, C; Bates, MN; Yuan, Y; Kalman, D; Atallah, R; Rey, OA; Biggs, ML; Hopenhayn, C; Moore, LE; Hoang, BK; Smith, AH. Arsenic methylation and bladder cancer risk in case-control studies in Argentina and the United States. J. Occup. Environ. Med 2006, 48, 478–488. [Google Scholar]
  12. Tseng, CH. Arsenic methylation, urinary arsenic metabolites and human diseases: Current perspective. J. Environ. Sci. Health C 2007, 25, 1–22. [Google Scholar]
  13. Vahter, M. Methylation of inorganic arsenic in different mammalian species and population groups. Sci. Progr. London 1999, 82, 69–88. [Google Scholar]
  14. Tseng, CH. A review on environmental factors regulating arsenic methylation in humans. Toxicol. Appl. Pharmacol 2009, 235, 338–350. [Google Scholar]
  15. Vahter, M; Concha, G; Nermell, B; Nilsson, R; Dulout, F; Natarajan, AT. A unique metabolism of inorganic arsenic in native Andean women. Eur. J. Pharmacol 1995, 293, 455–462. [Google Scholar]
  16. Chiou, HY; Hsueh, YM; Hsieh, LL; Hsu, LI; Yi-Hsiang, H; Hsieh, FI; Wei, ML; Chen, HC; Yang, HT; Leu, LC; et al. Arsenic methylation capacity, body retention, and null genotypes of glutathione S-transferase M1 and T1 among current arsenic-exposed residents in Taiwan. Mutat. Res 1997, 386, 197–207. [Google Scholar]
  17. Agusa, T; Fujihara, J; Takeshita, H; Iwata, H; Minh, TB; Trang, PTK; Viet, PH; Tanabe, S. Relationship between genetic polymorphism of arsenic (+3 oxidation state) methyltransferase (AS3MT) and profiles of urinary arsenic compounds in Vietnamese. Biomed. Res. Trace Elem 2009, 19, 265–267. [Google Scholar]
  18. Agusa, T; Iwata, H; Fujihara, J; Kunito, T; Takeshita, H; Minh, TB; Trang, PTK; Viet, PH; Tanabe, S. Genetic polymorphisms in AS3MT and arsenic metabolism in residents of the Red River Delta, Vietnam. Toxicol. Appl. Pharmacol 2009, 236, 131–141. [Google Scholar]
  19. Agusa, T; Iwata, H; Fujihara, J; Kunito, T; Takeshita, H; Tu, BM; Pham, TKT; Pham, HV; Tanabe, S. Genetic polymorphisms in glutathione S-transferase (GST) superfamily and arsenic metabolism in residents of the Red River Delta, Vietnam. Toxicol. Appl. Pharmacol 2010, 242, 352–362. [Google Scholar]
  20. Agusa, T; Iwata, H; Fujihara, J; Kunito, T; Takeshita, H; Minh, TB; Trang, PTK; Viet, PH; Tanabe, S. Interindividual variation in arsenic metabolism in a Vietnamese population: Association with 17 single nucleotide polymorphisms in AS3MT. In Interdisciplinary Studies on Environmental Chemistry Vol 3 Biological Responses to Chemical Contaminants: From Molecular to Community Level; Hamamura, N, Suzuki, S, Mendo, S, Barroso, CM, Iwata, H, Tanabe, S, Eds.; TERRAPUB: Tokyo, Japan, 2010; pp. 113–119. [Google Scholar]
  21. Agusa, T; Kunito, T; Kubota, R; Inoue, S; Fujihara, J; Minh, TB; Ha, NN; Tu, NPC; Trang, PTK; Chamnan, C; et al. Exposure, metabolism, and health effects of arsenic in residents from arsenic-contaminated groundwater areas of Vietnam and Cambodia: A review. Rev. Environ. Health 2010, 25, 193–220. [Google Scholar]
  22. Hernández, A; Marcos, R. Genetic variations associated with interindividual sensitivity in the response to arsenic exposure. Pharmacogenomics 2008, 9, 1113–1132. [Google Scholar]
  23. Challenger, F. Biological methylation. Chem. Rev 1945, 36, 315–361. [Google Scholar]
  24. Cullen, WR; Reimer, KJ. Arsenic speciation in the environment. Chem. Rev 1989, 89, 713–764. [Google Scholar]
  25. Petrick, JS; Ayala-Fierro, F; Cullen, WR; Carter, DE; Vasken Aposhian, H. Monomethylarsonous acid (MMAIII) is more toxic than arsenite in Chang human hepatocytes. Toxicol. Appl. Pharmacol 2000, 163, 203–207. [Google Scholar]
  26. Styblo, M; Del Razo, LM; Vega, L; Germolec, DR; LeCluyse, EL; Hamilton, GA; Reed, W; Wang, C; Cullen, WR; Thomas, DJ. Comparative toxicity of trivalent and pentavalent inorganic and methylated arsenicals in rat and human cells. Arch. Toxicol 2000, 74, 289–299. [Google Scholar]
  27. Hayakawa, T; Kobayashi, Y; Cui, X; Hirano, S. A new metabolic pathway of arsenite: Arsenic-glutathione complexes are substrates for human arsenic methyltransferase Cyt19. Arch. Toxicol 2005, 79, 183–191. [Google Scholar]
  28. Naranmandura, H; Suzuki, N; Suzuki, KT. Trivalent arsenicals are bound to proteins during reductive methylation. Chem. Res. Toxicol 2006, 19, 1010–1018. [Google Scholar]
  29. Lin, S; Shi, Q; Nix, FB; Styblo, M; Beck, MA; Herbin-Davist, KM; Hall, LL; Simeonsson, JB; Thomas, DJ. A novel S-adenosyl-L-methionine: Arsenic(III) methyltransferase from rat liver cytosol. J. Bio. Chem 2002, 277, 10795–10803. [Google Scholar]
  30. Wood, TC; Salavagionne, OE; Mukherjee, B; Wang, LW; Klumpp, AF; Thomae, BA; Eckloff, BW; Schaid, DJ; Wieben, ED; Weinshilboum, RM. Human arsenic methyltransferase (AS3MT) pharmacogenetics—Gene resequencing and functional genomics studies. J. Bio. Chem 2006, 281, 7364–7373. [Google Scholar]
  31. HapMap Public Release #28; National Center for Biotechnology Information: Bethesda, MD, USA, 2010. Available online: (accessed on 10 March 2011).
  32. Kojima, C; Ramirez, DC; Tokar, EJ; Himeno, S; Drobná, Z; Stýblo, M; Mason, RP; Waalkes, MP. Requirement of arsenic biomethylation for oxidative DNA damage. J. Nat. Cancer Inst 2009, 101, 1670–1681. [Google Scholar]
  33. NCBI Reference Assembly; National Center for Biotechnology Information: Bethesda, MD, USA, 2010. Available online: (accessed on 10 March 2011).
  34. Drobna, Z; Waters, SB; Walton, FS; LeCluyse, EL; Thomas, DJ; Styblo, M. Interindividual variation in the metabolism of arsenic in cultured primary human hepatocytes. Toxicol. Appl. Pharmacol 2004, 201, 166–177. [Google Scholar]
  35. Meza, MM; Yu, LZ; Rodriguez, YY; Guild, M; Thompson, D; Gandolfi, AJ; Klimecki, WT. Developmentally restricted genetic determinants of human arsenic metabolism: Association between urinary methylated arsenic and CYT19 polymorphisms in children. Environ. Health Perspect 2005, 113, 775–781. [Google Scholar]
  36. Meza, M; Gandolfi, AJ; Klimecki, WT. Developmental and genetic modulation of arsenic biotransformation: A gene by environment interaction? Toxicol. Appl. Pharmacol 2007, 222, 381–387. [Google Scholar]
  37. Valenzuela, OL; Drobna, Z; Hernandez-Castellanos, E; Sanchez-Pena, LC; Garcia-Vargas, GG; Borja-Aburto, VH; Styblo, M; Del Razo, LM. Association of AS3MT polymorphisms and the risk of premalignant arsenic skin lesions. Toxicol. Appl. Pharmacol 2009, 239, 200–207. [Google Scholar]
  38. Gomez-Rubio, P; Meza-Montenegro, MM; Cantu-Soto, E; Klimecki, WT. Genetic association between intronic variants in AS3MT and arsenic methylation efficiency is focused on a large linkage disequilibrium cluster in chromosome 10. J. Appl. Toxicol 2010, 30, 260–270. [Google Scholar]
  39. Sampayo-Reyes, A; Hernández, A; El-Yamani, N; López-Campos, C; Mayet-Machado, E; Rincón-Castañeda, CB; Limones-Aguilar, ML; López-Campos, JE; de León, MB; González-Hernández, S; Hinojosa-Garza, D; Marcos, R. Arsenic induces DNA damage in environmentally exposed Mexican children and adults. Influence of GSTO1 and AS3MT Polymorphisms. Toxicol. Sci 2010, 117, 63–71. [Google Scholar]
  40. Schläwicke Engström, K; Broberg, K; Concha, G; Nermell, B; Warholm, M; Vahter, M. Genetic polymorphisms influencing arsenic metabolism: Evidence from Argentina. Environ. Health Perspect 2007, 115, 599–605. [Google Scholar]
  41. Núñez, ALN; Hill, HG; Martinez, AL. Guía Museo Arqueológico. In Universidad Católica del Norte Chile San Pedro de Atacama (II Regíon): Instituto de Investigaciones; Arqueológicas y Museo, RP, Gustavo Le Paige, SJ, Eds.; Universidad Católica del Norte Chile: Antofagasta, Chile, 1991. [Google Scholar]
  42. Figueroa, LT; Razmilic, BB; González, MU. Corporal distribution of arsenic in mummied bodies owned to an arsenical habitat. In International Seminar Proceedings: Arsenic in the Environment and Its Incidence on Health; Sancha, AM, Ed.; Universidad de Chile, Facultad de Ciencias Fisicas y Matematicas: Santiago, Chile, 1992; pp. 77–82. [Google Scholar]
  43. Schläwicke Engström, K; Nermell, B; Concha, G; Stromberg, U; Vahter, M; Broberg, K. Arsenic metabolism is influenced by polymorphisms in genes involved in one-carbon metabolism and reduction reactions. Mutat. Res 2009, 667, 4–14. [Google Scholar]
  44. Hernandez, A; Xamena, N; Surralles, J; Sekaran, C; Tokunaga, H; Quinteros, D; Creus, A; Marcos, R. Role of the Met(287)Thr polymorphism in the AS3MT gene on the metabolic arsenic profile. Mutat. Res 2008, 637, 80–92. [Google Scholar]
  45. Hernandez, A; Xamena, N; Sekaran, C; Tokunaga, H; Sampayo-Reyes, A; Quinteros, D; Creus, A; Marcos, R. High arsenic metabolic efficiency in AS3MT(287)Thr allele carriers. Pharmacogenet. Genomics 2008, 18, 349–355. [Google Scholar]
  46. Lindberg, AL; Kumar, R; Goessler, W; Thirumaran, R; Gurzau, E; Koppova, K; Rudnai, P; Leonardi, G; Fletcher, T; Vahter, M. Metabolism of low-dose inorganic arsenic in a Central Europena population: Influence of sex and genetic polymorphisms. Environ. Health Perspect 2007, 115, 1081–1086. [Google Scholar]
  47. Chakraborti, D; Rahman, MM; Paul, K; Chowdhury, UK; Sengupta, MK; Lodh, D; Chanda, CR; Saha, KC; Mukherjee, SC. Arsenic calamity in the Indian subcontinent: What lessons have been learned? Talanta 2002, 58, 3–22. [Google Scholar]
  48. De Chaudhuri, S; Ghosh, P; Sarma, N; Majumdar, P; Sau, TJ; Basu, S; Roychoudhury, S; Ray, K; Giri, AK. Genetic variants associated with arsenic susceptibility: Study of purine nucleoside phosphorylase, arsenic (+3) methyltransferase, and glutathione S-transferase omega genes. Environ. Health Perspect 2008, 116, 501–505. [Google Scholar]
  49. Chung, CJ; Hsueh, YM; Bai, CH; Huang, YK; Huang, YL; Yang, MH; Chen, CJ. Polymorphisms in arsenic metabolism genes, urinary arsenic methylation profile and cancer. Canc. Causes Contr 2009, 20, 1653–1661. [Google Scholar]
  50. Berg, M; Tran, HC; Nguyen, TC; Pham, HV; Schertenleib, R; Giger, W. Arsenic contamination of groundwater and drinking water in Vietnam: A human health threat. Environ. Sci. Technol 2001, 35, 2621–2626. [Google Scholar]
  51. Nga, TTV; Inoue, M; Khatiwada, NR; Takizawa, S. Heavy metal tracers for the analysis of groundwater contamination: Case study in Hanoi City, Vietnam. Water Sci. Tech. Water Sup 2003, 3, 343–350. [Google Scholar]
  52. Trang, PTK; Berg, M; Viet, PH; Van Mui, N; Van der Meer, JR. Bacterial bioassay for rapid and accurate analysis of arsenic in highly variable groundwater samples. Environ. Sci. Tech 2005, 39, 7625–7630. [Google Scholar]
  53. Berg, M; Luzi, S; Trang, PTK; Viet, PH; Giger, W; Stuben, D. Arsenic removal from groundwater by household sand filters: Comparative field study, model calculations, and health benefits. Environ. Sci. Tech 2006, 40, 5567–5573. [Google Scholar]
  54. Shinkai, Y; Van Truc, D; Sumi, D; Canh, D; Kumagai, Y. Arsenic and other metal contamination of groundwater in the Mekong River Delta, Vietnam. J. Health Sci 2007, 53, 344–346. [Google Scholar]
  55. Buschmann, J; Berg, M; Stengel, C; Winkel, L; Sampson, ML; Trang, PTK; Viet, PH. Contamination of drinking water resources in the Mekong delta floodplains: Arsenic and other trace metals pose serious health risks to population. Environ. Int 2008, 34, 756–764. [Google Scholar]
  56. Norrman, J; Sparrenbom, CJ; Berg, M; Nhan, DD; Nhan, PQ; Rosqvist, H; Jacks, G; Sigvardsson, E; Baric, D; Moreskog, J; Harms-Ringdahl, P; Van Hoan, N. Arsenic mobilisation in a new well field for drinking water production along the Red River, Nam Du, Hanoi. Appl. Geochem 2008, 23, 3127–3142. [Google Scholar]
  57. Agusa, T; Kunito, T; Fujihara, J; Kubota, R; Minh, TB; Trang, PTK; Iwata, H; Subramanian, A; Viet, PH; Tanabe, S. Contamination by arsenic and other trace elements in tube-well water and its risk assessment to humans in Hanoi, Vietnam. Environ. Pollut 2006, 139, 95–106. [Google Scholar]
  58. Agusa, T; Inoue, S; Kunito, T; Minh, TB; Ha, NN; Tu, NPC; Trang, PTK; Iwata, H; Viet, PH; Tuyen, BC; Tanabe, S. Human exposure to arsenic from groundwater in the Red River and the Mekong River Deltas in Vietnam. Int. J. Environ. Stud 2009, 66, 49–57. [Google Scholar]
  59. Agusa, T; Kunito, T; Minh, TB; Trang, PTK; Iwata, H; Viet, PH; Tanabe, S. Relationship of urinary arsenic metabolites to intake estimates in residents of the Red River Delta, Vietnam. Environ. Pollut 2009, 157, 396–403. [Google Scholar]
  60. Agusa, T; Kunito, T; Kubota, R; Inoue, S; Fujihara, J; Minh, TB; Ha, NN; Tu, NPC; Trang, PTK; Chamnan, C; et al. Exposure, metabolism, and health effects of arsenic in residents from arsenic-contaminated groundwater areas of Vietnam and Cambodia: A review. Rev. Environ. Health 2010, 25, 193–220. [Google Scholar]
  61. Nguyen, VA; Bang, S; Viet, PH; Kim, KW. Contamination of groundwater and risk assessment for arsenic exposure in Ha Nam province, Vietnam. Environ. Int 2009, 35, 466–472. [Google Scholar]
  62. Fujihara, J; Kunito, T; Agusa, T; Yasuda, T; Iida, R; Fujii, Y; Takeshita, H. Population differences in the human arsenic (+3 oxidation state) methyltransferase (AS3MT) gene polymorphism detected by using genotyping method. Toxicol. Appl. Pharmacol 2007, 225, 251–254. [Google Scholar]
  63. Fujihara, J; Soejima, M; Koda, Y; Kunito, T; Takeshita, H. Asian specific low mutation frequencies of the M287T polymorphism in the human arsenic (+3 oxidation state) methyltransferase (AS3MT) gene. Mutat. Res.-Genet. Toxicol. E. M 2008, 654, 158–161. [Google Scholar]
  64. Fujihara, J; Fujii, Y; Agusa, T; Kunito, T; Yasuda, T; Moritani, T; Takeshita, H. Ethnic differences in five intronic polymorphisms associated with arsenic metabolism within human arsenic (+3 oxidation state) methyltransferase (AS3MT) gene. Toxicol. Appl. Pharmacol 2009, 234, 41–46. [Google Scholar]
  65. Fujihara, J; Soejima, M; Yasuda, T; Koda, Y; Agusa, T; Kunito, T; Tongu, M; Yamada, T; Takeshita, H. Global analysis of genetic variation in human arsenic (+3 oxidation state) methyltransferase (AS3MT). Toxicol. Appl. Pharmacol 2010, 243, 292–299. [Google Scholar]
  66. Zhu, J; Chen, Z; Lallemand-Breitenbach, V; De Thé, H. How acute promyclocytic leukaemia revived arsenic. Nat. Rev. Cancer 2002, 2, 705–713. [Google Scholar]
Figure 1. Proposed pathways of inorganic arsenic metabolism by oxidative and reductive methylation.
Figure 1. Proposed pathways of inorganic arsenic metabolism by oxidative and reductive methylation.
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Figure 2. Location of genetic polymorphisms in AS3MT. Dark blue rectangles represent exons. Chromosome positions are also indicated. Arrows show the locations of genetic polymorphisms.
Figure 2. Location of genetic polymorphisms in AS3MT. Dark blue rectangles represent exons. Chromosome positions are also indicated. Arrows show the locations of genetic polymorphisms.
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Figure 3. Frequencies of alleles in AS3MT in various populations reported in our studies [20,65] and the HapMap Project [31]. JP: Japanese, JPT (J): Japanese in Tokyo, Japan, SKR: South Koreans, CH: Chinese, CHB (H): Han Chinese in Beijing, China, CHD (D): Chinese in Metropolitan Denver, Colorado, MN: Mongolians, TIB: Tibetans, NP: Nepalese, VN: Vietnamese, SLT: Sri Lanka-Tamils, SLS: Sri Lanka-Sinhalese, OVA: Ovambos, GH: Ghanaians, LWK (L): Luhya in Webuye, Kenya, MKK (K): Maasai in Kinyawa, Kenya, YRI (Y): Yoruban in Ibadan, Nigeria, ASW (A): African ancestry in Southwest USA, TSI (T): Tuscan in Italy, CEU (C): Utah residents with Northern and Western European ancestry from the CEPH collection, GIH (G): Gujarati Indians in Houston, Texas, MEX (M): Mexican ancestry in Los Angeles, California. 1; Fujihara et al. [65], 2; Agusa et al. [20], 3; HapMap Project [31].
Figure 3. Frequencies of alleles in AS3MT in various populations reported in our studies [20,65] and the HapMap Project [31]. JP: Japanese, JPT (J): Japanese in Tokyo, Japan, SKR: South Koreans, CH: Chinese, CHB (H): Han Chinese in Beijing, China, CHD (D): Chinese in Metropolitan Denver, Colorado, MN: Mongolians, TIB: Tibetans, NP: Nepalese, VN: Vietnamese, SLT: Sri Lanka-Tamils, SLS: Sri Lanka-Sinhalese, OVA: Ovambos, GH: Ghanaians, LWK (L): Luhya in Webuye, Kenya, MKK (K): Maasai in Kinyawa, Kenya, YRI (Y): Yoruban in Ibadan, Nigeria, ASW (A): African ancestry in Southwest USA, TSI (T): Tuscan in Italy, CEU (C): Utah residents with Northern and Western European ancestry from the CEPH collection, GIH (G): Gujarati Indians in Houston, Texas, MEX (M): Mexican ancestry in Los Angeles, California. 1; Fujihara et al. [65], 2; Agusa et al. [20], 3; HapMap Project [31].
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Figure 4. Suspected universal AS3MT genotype-dependent methylation of arsenic. C carrier of AS3MT 14458 (rs11191439) may have higher first methylation capacity than the T carrier, while C carrier of AS3MT 12390 (rs3740393) may have higher second methylation capacity than the G carrier.
Figure 4. Suspected universal AS3MT genotype-dependent methylation of arsenic. C carrier of AS3MT 14458 (rs11191439) may have higher first methylation capacity than the T carrier, while C carrier of AS3MT 12390 (rs3740393) may have higher second methylation capacity than the G carrier.
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Table 1. Allele frequency of genotypes in AS3MTof various Asians and Africans [18,20,6265].
Table 1. Allele frequency of genotypes in AS3MTof various Asians and Africans [18,20,6265].
SNP IDrs #LocationNucleotide changeAncestralAlleleJapanese (n = 141)South Koreans (n = 230)Chinese (n = 54)Mongolians (n = 58)Tibetans (n = 65)Nepalese (n = 31)
3963rs70988255′ terminalC/TTC0.2660.2980.2410.0090.3310.355
4602rs70851045′ terminalA/GAA0.5670.5650.4360.672*0.4540.694
4740rs124166875′ terminalC/TTC0.0600.0670.1300.0610.0540.000
5913rs4917986Intron 3C/TTCNANANANANANA
6144rs17878846Intron 3A/TAA0.7340.7300.695*0.9310.708*0.678
7395rs12767543Intron 3A/GGA0.2870.274*0.4260.0690.1850.275
8979rs7920657Intron 5A/TTA0.0570.07600.0770.0690.000
9749rs17881367Intron 5A/GAA0.9440.9241.0000.922*0.9311.000
10209rs3740394Intron 6A/GTA0.9900.9851.0000.9830.9850.984
12390rs3740393Intron 6C/GCC0.373*0.2790.2780.4310.3380.339
12590rs3740392Intron 7C/TTC0.178*0.1720.2510.2150.1850.162
14215rs3740390Intron 8C/TCC0.483*0.587*0.3430.587*0.2620.645
144581rs11191439Exon 9C/TTC0.0040.00900.0260.0230.000
25986rs7085854Intron 8C/TTC0.0570.1220.2590.0520.1620.145
26790rs11191445Intron 10C/TCC0.990*0.9851.0000.9830.9770.968
27215rs11191446Intron 10A/GAA0.9260.9180.9720.9490.9000.952
35587rs11191453Intron 10C/TTC0.344*0.370*0.3330.155*0.516*0.404
35991rs10748835Intron 10A/GAA0.5430.5700.6020.5610.6540.597
37616rs45689433′ terminalA/CAA0.656*0.7350.519*0.906*0.6390.678
37853rs111914593′ terminalA/GGANANANANANANA
37950rs178798193′ terminalC/TCC0.7100.7130.6760.9230.6380.629
SNP IDrs #LocationNucleotide changeAncestralAlleleVietnamese (n = 100)Sri Lanka-Tamils (n = 29)Sri Lanka-Sinhalese (n = 30)Ovambos (n = 102)Ghanaians (n = 87)
3963rs70988255′ terminalC/TTCNA0.0860.1170.0540.121
4602rs70851045′ terminalA/GAA0.4200.8450.8170.5250.598
4740rs124166875′ terminalC/TTC00.0170.0170.1330.104
5913rs4917986Intron 3C/TTC0.080NANANANA
6144rs17878846Intron 3A/TAA0.7500.8450.8671.0001.000
7395rs12767543Intron 3A/GGA0.335*0.1210.1670.1130.304
8979rs7920657Intron 5A/TTA00.0350.0170.1420.075
9749rs17881367Intron 5A/GAANA0.9660.9840.8580.926
10209rs3740394Intron 6A/GTANA0.9830.9840.8680.920
12390rs3740393Intron 6C/GCC0.2250.1890.2510.5400.299
12590rs3740392Intron 7C/TTC0.3600.1550.0840.2210.189
14215rs3740390Intron 8C/TCC0.7550.8100.8670.5540.414*
144581rs11191439Exon 9C/TTC000.0170.0930.075
25986rs7085854Intron 8C/TTCNA0.1720.2500.2990.316
26790rs11191445Intron 10C/TCCNA0.9830.9840.8140.966
27215rs11191446Intron 10A/GAANA0.9660.9840.8730.920
35587rs11191453Intron 10C/TTC0.270*0.2070.1340.0450.063
35991rs10748835Intron 10A/GAA0.5850.5350.3670.7060.402
37616rs45689433′ terminalA/CAANA0.7940.8670.941*0.931
37853rs111914593′ terminalA/GGA0.495NANANANA
37950rs178798193′ terminalC/TCCNA0.7930.8670.961*0.937

NA: no available data.*:not followed Hardy–Weinberg Principle (p < 0.05).1:Met to Thr substitution at amino acid base on 287.

Table 2. Differences in the association of arsenic methylation and linkage disequilibrium (LD) for SNPs of AS3MT among nations.
Table 2. Differences in the association of arsenic methylation and linkage disequilibrium (LD) for SNPs of AS3MT among nations.
SNP IDrs #LocationNucleotide changeAncestralMexico (n = 144)Mexico (n = 122)Mexico (n = 405)Argentina (n = 147)
3963rs70988255′ terminalC/TT
4602rs70851045′ terminalA/GANS%MMA[III + V]: AA + AG > GG
%DMA[III + V]: GG > AA + AG
4740rs124166875′ terminalC/TTNS
4965rs17881215Exon 1: 5′ UTRC/GG
5019rs17880342Exon 1: 5′ UTRC/TCNA
5051rs17883409Intron 1*NAVNSNA
5194rs3740400Intron 1A/CCNA
5913rs4917986Intron 3C/TT
6144rs17878846Intron 3A/TA
7395rs12767543Intron 3A/GGDMA[V]/MMA[V]: AA + AG > GG2S
8788rs17881367Intron 5-/TTTNAVNA
8979rs7920657Intron 5A/TT
9749rs17881367Intron 5A/GA
10209rs3740394Intron 6C/TTNS
12390rs3740393Intron 6C/GCDMA[V]/MMA[V]: CC + CG > GG2S%MMA[V]: GG > CC, CG
%DMA[V]: CC, CG > GG
12590rs3740392Intron 7C/TTNSNA
13599rs10883797Intron 7C/GCNS
14215rs3740390Intron 8C/TCS%MMA[V]: CC > TT, CT
%DMA[V]: TT, CT > CC
144581rs11191439Exon 9C/TT%MMA[III + V]: CT + CC > TT
%As[V]: CT + CC > TT
25986rs7085854Intron 9C/TTNS
27215rs11191446Intron 10A/GA
30312rs1191453Intron 10C/TTDMA[V]/MMA[V]: CC > CT > TT
35587rs11191453Intron 10C/TTDMA[V]/MMA[V]: CC + CT > TT2
MMA[V]/As[III]: TT > CC + CT2
35739rs11191454Intron 10A/GAS
35991rs10748835Intron 10A/GA%MMA[V]: GG > AA, AG
%DMA[V]: AA, AG > GG
36209rs17879039Exon 11: 3′ UTRA/GG
37219rs1046778Exon 11: 3′ UTRC/TTS
37616rs45689433′ terminalA/CA
37853rs111914593′ terminalA/GG
37950rs178798193′ terminalC/TC
LD cluster
References[35, 36][37][38][40]
SNP IDrs #LocationNucleotide changeAncestralArgentina (n = 104)Chile (n = 50)Chile (n = 207)
3963rs70988255′ terminalC/TT
4602rs70851045′ terminalA/GA%MMA[V]: AA + AG > GG
%DMA[V]: GG > AG + AA
4740rs124166875′ terminalC/TT
4965rs17881215Exon 1: 5′ UTRC/GG%MMA: CG > GG
5019rs17880342Exon 1: 5′ UTRC/TC
5051rs17883409Intron 1*NAV
5194rs3740400Intron 1A/CC%MMA[V]: AA + AC > CC
%DMA[V]: CC > AC + AA
5913rs4917986Intron 3C/TT
6144rs17878846Intron 3A/TA
7395rs12767543Intron 3A/GG
8788rs17881367Intron 5-/TTTNAV
8979rs7920657Intron 5A/TT
9749rs17881367Intron 5A/GA
10209rs3740394Intron 6C/TT
12390rs3740393Intron 6C/GC
12590rs3740392Intron 7C/TT
13599rs10883797Intron 7C/GC
14215rs3740390Intron 8C/TC
144581rs11191439Exon 9C/TT%MMA: CT + CC > TT%MMA: CT + CC > TT
25986rs7085854Intron 9C/TT
27215rs11191446Intron 10A/GA
30312rs1191453Intron 10C/TT
35587rs11191453Intron 10C/TT
35739rs11191454Intron 10A/GA
35991rs10748835Intron 10A/GA
36209rs17879039Exon 11: 3′ UTRA/GGNS
37219rs1046778Exon 11: 3′ UTRC/TT
37616rs45689433′ terminalA/CA
37853rs111914593′ terminalA/GG
37950rs178798193′ terminalC/TC
LD cluster
SNP IDrs #LocationNucleotide changeAncestralCentral Europe4 (n = 415)Taiwan (n = 208)Vietnam (n = 100)
3963rs70988255′ terminalC/TTNS
4602rs70851045′ terminalA/GA%DMA[V]: AA, AG > GG
4740rs124166875′ terminalC/TT%DMA[V]: TT > CT, CC
4965rs17881215Exon 1: 5′ UTRC/GG
5019rs17880342Exon 1: 5′ UTRC/TC
5051rs17883409Intron 1*NAV
5194rs3740400Intron 1A/CC
5913rs4917986Intron 3C/TT%MMA[V]: CT > TT
6144rs17878846Intron 3A/TANS
7395rs12767543Intron 3A/GGNS
8788rs17881367Intron 5-/TTTNAV
8979rs7920657Intron 5A/TT%DMA[V]: AT, TT > AA
9749rs17881367Intron 5A/GA%MMA[V]: AG > AA
10209rs3740394Intron 6C/TT
12390rs3740393Intron 6C/GC%MMA[V]: GG > CG
%DMA[V]: CG > GG
%MMA[V]: GG > CC
12590rs3740392Intron 7C/TT%DMA[V]: TT > CC
13599rs10883797Intron 7C/GC
14215rs3740390Intron 8C/TCNS
144581rs11191439Exon 9C/TT%DMA[V]: TT > CT + CC
%MMA[V]: CT + CC > TT
25986rs7085854Intron 9C/TT
27215rs11191446Intron 10A/GA%MMA[V]: AG > AA
30312rs1191453Intron 10C/TT
35587rs11191453Intron 10C/TTDMA[V]/MMA[V]: CT > TT
35739rs11191454Intron 10A/GA
35991rs10748835Intron 10A/GA%DMA[V]: AG > AA
36209rs17879039Exon 11: 3′ UTRA/GG
37219rs1046778Exon 11: 3′ UTRC/TT
37616rs45689433′ terminalA/CA
37853rs111914593′ terminalA/GG%DMA[V]: GG, AG > AA
%MMA[V]: GG > AA
37950rs178798193′ terminalC/TCNS
LD cluster
References[46][49][18, 20]

NAV: not available.NS: not significant.NA: no statistical analysis due to the small genotype frequency.1:Met to Thr substitution at amino acid base on 287.2:Significant result was observed for only children but not for adults.3:Previous data of SNP is included.4:Hungarian, Romanian, and Slovak.*:-/CGCGCCCTGAGTCGCAGGCCGAGGAGACAGTGAGTGCS: Significant association with DMA[V]/MMA[V] was found but no information which genotype is associated with it.

Int. J. Mol. Sci. EISSN 1422-0067 Published by MDPI AG, Basel, Switzerland RSS E-Mail Table of Contents Alert
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