Inorganic Arsenic Intake Research Articles

Inorganic arsenic: Evaluation of risks to health from environmental exposure in Canada

Abstract In this assessment of arsenic as a Priority Substance under the Canadian Environmental Protection Act, available data were critically evaluated to determine if levels of arsenic present in the Canadian environment pose a risk to health. Average daily intakes of inorganic arsenic from drinking water, food, air and soil have been estimated for the general population, as well as for populations residing in the vicinity of point sources. Based on the sufficient weight of evidence in adequate epidemiological studies in several countries in which exposure to arsenic compounds via inhalation or ingestion has been associated with cancer, arsenic has been classified as “carcinogenic in humans”. Based on comparison of estimates of exposure in Canada to the estimated potency of inhaled and ingested arsenic to induce cancer, the priority for analysis of options to reduce exposure in the general environment is considered to be moderate to high compared to that of other substances assessed under CEPA.

Species differences in the metabolism of arsenic compounds

AbstractHumans are exposed via air, water and food to a number of different arsenic compounds, the physical, chemical, and toxicological properties of which may vary considerably. In people eating much fish and shellfish the intake of organic arsenic compounds, mainly arsenobetaine, may exceed 1000 μg As per day, while the average daily intake of inorganic arsenic is in the order of 10–20 μg in most countries. Arsenobetaine, and most other arsenic compounds in food of marine origin, e.g. arsenocholine, trimethylarsine oxide and methylarsenic acids, are rapidly excreted in the urine and there seem to be only minor differences in metabolism between animal species. Trivalent inorganic arsenic (AsIII) is the main form of arsenic interacting with tissue constituents, due to its strong affinity for sulfhydryl groups. However, a substantial part of the absorbed AsIII is methylated in the body to less reactive metabolities, methylarsonic acid (MMA) and dimethylarsinic acid (DMA), which are rapidly excreted in the urine. All the different steps in the arsenic biotransformation in mammals have not yet been elucidated, but it seems likely that the methylation takes place mainly in the liver by transfer of methyl groups from S‐adenosylmethionine to arsenic in its trivalent oxidation state. A substantial part of absorbed arsenate (AsV) is reduced to AsIII before being methylated in the liver. There are marked species differences in the methylation of inorganic arsenic. In most animal species DMA is the main metabolite. Compared with human subjects, very little MMA is produced. The marmoset monkey is the only species which has been shown unable to methylate inorganic arsenic. In contrast to other species, the rat shows a marked binding of DMA to the hemoglobin, which results in a low rate of urinary excretion of arsenic.

Atmospheric deposition of trace elements around point sources and human health risk assessment. II: Uptake of arsenic and chromium by vegetables grown near a wood preservation factory

Kale, lettuce, carrots and potatoes were grown in 20 experimental plots sorrounding a wood preservation factory, to investigate the amount and pathways for plant uptake of arsenic and chromium. Arsenate used in the wood preservation process is converted to the more toxic arsenite by incineration of waste wood and is emitted into the atmosphere. Elevated concentrations of inorganic arsenic and chromium were found both in the test plants and in the soil around the factory. Multivariate statistical analysis of the results indicated that the dominating pathway of arsenic and chromium from the factory to the leafy vegetables grown nearby was by direct atmospheric deposition, while arsenic in the root crops originated from both the soil and the atmosphere. Consumption of vegetables grown near the source would result in an increased intake of inorganic arsenic, but the intake via the total diet was estimated to be below the provisional tolerable daily intake for inorganic arsenic established by FAO/WHO.

Arsenic intake and excretion by Japanese adults: A 7-day duplicate diet study

The amount of arsenic in the urine, faeces and in duplicate diets of two couples who had eaten customary Japanese meals were monitored for 7 days by arsine-generator atomic absorption spectrophotometry. For the four volunteers, the mean daily intake of arsenic from their diets was 182 μg (range 27 to 376 μg). The dietary arsenic was composed of 5.7% inorganic arsenic, 3.6% methylarsonic acid, 27.4% dimethylarsinic acid and 47.9% trimethylarsenic compounds. The mean amounts of arsenic eliminated daily in urine and faeces were 148 μg (50–416 μg) and 46 μg (0–138 μg), respectively. The urinary arsenic was composed of 1.4% inorganic arsenic, 3.5% methylarsonic acid, 33.6% dimethylarsinic acid and 61.4% trimethylarsenic compounds. The daily intake of arsenic influenced the total amount of arsenic excreted in the urine ( r = 0.7302, P <0.01) and the amount eliminated in the faeces ( r = 0.5900, P <0.01) the next day. Specifically, there was also a significant correlation between the daily intakes of trimethylarsenic compounds and dimethylarsinic acid and the amounts of these compounds found in the urine the following day ( r = 0.6833, P <0.01 and r = 0.6630, P <0.01, respectively). Considering the amounts of arsenic compounds present in seafood and in other components of the diet together with the urinary elimination patterns of arsenic compounds, it seemed probable that the trimethylarsenic compounds in the urine originated largely from fish and shellfish, which contain mainly arsenobetaine. Trimethylarsenic compounds in the urine should therefore be the preferred indicator of arsenic arising from the ingestion of seafood, especially fish and shellfish. In this study, the mean daily intake of inorganic arsenic from the diet (0.18 μg/kg) did not exceed the FAO/WHO JECFA Tolerable Daily Intake of 2 μg inorganic arsenic/kg.

Speciation of arsenic in Dutch total diets: methodology and results.

In the last decade 311 duplicate portions of the 24-h diet of Dutch citizens were collected and lyophilized. All samples were assayed for total arsenic and, in addition, the 20 samples which ranked highest in total arsenic were selected for arsenic speciation i.e., the separate determination of organic-bound arsenic and inorganic arsenic. For the determination of total arsenic, the test portion is wet-digested and the digest reduced with KI/SnCl2/Zn to give AsH3 which is measured by molecular absorption spectrometry. Inorganic arsenic is also measured as AsH3 after acid extraction of the test portion and subsequent NaBH4 reduction of the extract. The residue of the acid extraction and the NaBH4-reduced extract are combined, wet-digested and the digest reduced with NaBH4 to give AsH3 originating from organic-bound arsenic. Samples spiked at different levels with inorganic and organic-bound arsenic were analysed and gave recoveries for inorganic arsenic of 94% to 122% (n = 6) and for organic-bound arsenic of 87% to 104% (n = 6). On average, the inorganic fraction is 30% of the total arsenic intake; range 3% to 50% (n = 14). The inorganic arsenic fraction decreases with increasing level of total arsenic intake. The highest oral inorganic arsenic intake was 60 micrograms; the tolerable daily intake (TDI) for a 60-kg individual is 120 micrograms inorganic arsenic. Organic and inorganic arsenic measured were summed and compared with the results of the total arsenic determination; differences were less than 15%. (Since inorganic arsenic is a contaminant and not an additive, the abbreviation TDI is preferred here over ADI (acceptable daily intake) which is retained for additives.)

Urinary arsenic concentrations and speciation in Cornwall residents

Inorganic arsenic and its methylated metabolites were determined in urine from adults and children in Cornwall and from corresponding control groups in Glasgow. In the mineralised south-west of England, where it has been suggested that the highly enriched soil arsenic concentrations may at least be a cofactor in the increased incidence of skin cancer, urinary arsenic levels were, in general, only slightly elevated. The potential for increased intake of inorganic arsenic in Cornwall was, however, reflected in the more frequent occurrence of trivalent inorganic arsenic and monomethylarsonic acid in urine and, of especial significance, in two comparatively highly elevated sum of arsenic species concentrations of 48.7 and 20.8 μg g(-1) creatinine recorded for two pre-school children. These findings are discussed with reference to recommended limits and pathways of exposure to inorganic arsenic.