Metabolism Of Arsenic Species Research Articles

Salivary and Gut Microbiomes Play a Significant Role in in Vitro Oral Bioaccessibility, Biotransformation, and Intestinal Absorption of Arsenic from Food.

The release of a toxicant from a food matrix during the gastrointestinal digestion is a crucial determinant of the toxicant’s oral bioavailability. We present a modified setup of the human simulator of the gut microbial ecosystem (SHIME), with four sequential gastrointestinal reactors (oral, stomach, small intestine, and colon), including the salivary and colonic microbiomes. Naturally arsenic-containing rice, mussels, and nori seaweed were digested in the presence of microorganisms and in vitro oral bioaccessibility, bioavailability, and metabolism of arsenic species were evaluated following analysis by using HPLC/mass spectrometry. When food matrices were digested with salivary bacteria, the soluble arsenic in the gastric digestion stage increased for mussel and nori samples, but no coincidence impact was found in the small intestinal and colonic digestion stages. However, the simulated small intestinal absorption of arsenic was increased in all food matrices (1.2–2.7 fold higher) following digestion with salivary microorganisms. No significant transformation of the arsenic species occurred except for the arsenosugars present in mussels and nori. In those samples, conversions between the oxo arsenosugars were observed in the small intestinal digestion stage whereupon the thioxo analogs became major metabolites. These results expand our knowledge on the likely metabolism and oral bioavailabiltiy of arsenic during human digestion, and provide valuable information for future risk assessments of dietary arsenic.

Enzyme-assisted extraction of arsenic species from plant material

Investigations regarding the transfer and metabolism of arsenic species in plants require mild extraction conditions to conserve the original composition of arsenic species. Beside the use of water or water/methanol for extraction of arsenic species from plant samples, enzymes can assist this procedure by digestion of cellulose and other constituents of cell walls, resulting in a faster, more efficient extraction technique which preserves the arsenic species. The investigations presented here were focused on the stability of certain arsenic species in enzymatic solutions, optimal conditions for their chromatographic separation and detection namely by means of ion chromatography–inductively coupled plasma mass spectrometry and improvements with respect to extraction efficiency. With commercially available enzymes and enzyme mixtures, the digestion rate of soluble starch as model cellulose was determined using high-performance anion exchange chromatography–pulsed amperometric detection analysis of glucose as the major digestion product. The most effective digestion rate (80% within 4 h) was obtained with Viscozyme®. This enzyme mixture was applied to extracted arsenic species from algae and terrestrial plant materials. Qualitative and quantitative differences in the results between enzyme-assisted and water extractions were obtained and discussed. The results show that the application of enzymes in mild extraction protocols should be evaluated as an additional step for the identification of As-metabolics in organisms. Careful selection of suitable enzyme mixtures can overcome the disadvantage that extraction efficiency is very organism-specific.

Pattern of Excretion of Arsenic Compounds [Arsenite, Arsenate, MMA(V), DMA(V)] in Urine of Children Compared to Adults from an Arsenic Exposed Area in Bangladesh

Urinary arsenic is generally considered as the most reliable indicator of recent exposure to inorganic arsenic and is used as the main bio-marker of exposure. However, due to the different toxicity of arsenic compounds, speciation of arsenic in urine is generally considered to be more convenient for health risk assessment than measuring total arsenic concentration. Additionally, it can give valuable information about the metabolism of arsenic species within the body. In our study, for exposed group—42 urine samples were collected from Datterhat (South) village of Madaripur district, Bangladesh and an average arsenic concentration in their drinking water was 376 µg/L (range 118 to 620 µg/L). For control group, 27 urine samples were collected from a non-affected district, Badhadamil village of Medinipur district, West Bengal, India, where arsenic concentration in their drinking water is below 3 µg/L. The arsenic species in the urine were separated and quantified by using HPLC-ICP-MS. The sum of inorganic arsenic and its metabolites was also determined by FI-HG-AAS. Results indicate that average total urinary arsenic metabolites in children's urine is higher than adults and total arsenic excretion per kg body weight is also higher for children than adults. For arsenic species between adults and children, it has been observed that inorganic arsenic (In-As) in average is 2.36% and MMA is 6.55% lower for children than adults while DMA is 8.91% (average) higher in children than adults. The efficiency of the methylation process is also assessed by the ratio between urinary concentration of putative product and putative substrate of the arsenic metabolic pathway. Higher values mean higher methylation capacity. Results show the values of the MMA/In-As ratio for adults and children are 0.93 and 0.74 respectively. These results indicate that first reaction of the metabolic pathway is more active in adults than children. But a significant increase in the values of the DMA/MMA ratio in children than adults of exposed group (8.15 vs. 4.11 respectively) indicates 2nd methylation step is more active in children than adults. It has also been shown that the distribution of the values of DMA/MMA ratio to exposed group decrease with increasing age (2nd methylation process). Thus from these results we may infer that children retain less arsenic in their body than adults. This may also explain why children do not show skin lesions compared to adults when both are drinking same contaminated water.