Natural weathering and erosion cause certain minerals in rocks to release iAs into the soil, where it dissolves into groundwater and surface water. Although geology is the cause of most As contamination in drinking water, human activities—such as coal burning, mining, and smelting—can also contribute.[7]Drinking water is the most common source of human exposure to iAs.[3] Some people worldwide—in Bangladesh, India, Argentina, the United States, and elsewhere—regularly drink water with iAs concentrations exceeding the World Health Organization guideline of .[3,14] Infants are at particular risk when formula is mixed with iAs-contaminated water.[15]Rice and seafood are also significant sources of As exposure.[5,10] Rice is a staple food for people,[5] and fish is an important source of animal protein for more than 3 billion people.[4] Rice, which is typically grown in flooded paddies,[16] is what is known as a hyperaccumulator; the plants readily take up iAs from the soil or irrigation water.[17] The metal then concentrates in the outer layer of the grain.[18]Seafood, especially shellfish, is known to contain organic arsenicals.[10] Although generally considered less toxic than iAs, some oAs compounds and metabolites have demonstrated cytotoxic effects in vitro.[19,20,21] Margaret Karagas, a professor of epidemiology at the Dartmouth Geisel School of Medicine, believes more detailed studies are needed on the prevalence and toxicity of oAs compounds in both seafood[10] and rice.[22] “In parts of the world where arsenic levels in drinking water are not elevated, food is the main exposure source, especially for babies and children who regularly consume rice cereal or rice,” says Karagas. “Relative to body weight, arsenic levels in young children can be three times higher than in adults.”[23]iAs is a Group 1 carcinogen causally linked to skin, bladder, and lung cancer, with probable or possible links to several other cancers.[24] It has also been associated with type 2 diabetes and diseases of the cardiovascular, nervous, respiratory, and immune systems.[3] iAs and its metabolites can cross the placenta,[25] and fetal exposure has been associated with lower birth weight[26] and adverse neurodevelopmental effects.[27,28,29]
Mercury Sources and Toxicity
In contrast to As, the majority of Hg contamination occurs as a result of human activities, especially fossil fuel combustion.[30] Hg emissions can travel far from the original source before being deposited, on soil and water. Aquatic bacteria convert deposited Hg to MeHg, which marine creatures readily absorb. MeHg biomagnifies from the bottom to the top of the marine and freshwater food webs[30]; levels in the tissue of predatory ocean fish and mammals can be more than a million times higher than in the surrounding water.[31] This means that populations with high seafood consumption rates, such as coastal Indigenous peoples with strong cultural ties to the sea[4,32] may experience chronic high exposures to MeHg.Bacteria in flooded rice paddies produce MeHg that can reach the grain.[16] Although rice typically contains a lower proportion of MeHg than seafood, exposure levels can be substantial in populations that consume rice several times a day.[33] As with iAs, this exposure is a concern for infants who regularly eat rice cereal and other rice-derived foods.[1] Some studies suggest that the consumption of several daily rice meals during pregnancy may be more harmful to the fetus than a MeHg-rich seafood diet, which offers nutritional benefits that somewhat offset the compound’s toxicity.[34,35]Large-scale exposure events led to a strong research focus on the neurotoxicity of MeHg,[36] which readily crosses the placenta and blood–brain barrier.[37] MeHg biomagnifies from mother to fetus,[38,39] so neurological damage from high exposure during pregnancy is typically greater in the fetus than in the mother.[38,39]Beyond its neurotoxic effects, MeHg has been associated with cardiovascular[40,41,42,43,44] and immune system[45] disorders. Potential cancer links have also been reported[46] but are much less established than for iAs. In a study of young children, Karagas et al. reported associations between early-life Hg exposures (as estimated by toenail and urine samples) and increased blood pressure, which is an important risk factor for hypertension in adulthood.[44] “Capturing these [exposure-related] changes early gives us the opportunity to intervene and positively impact lifelong health,” says Karagas.In still another associated outcome, Matthew Rand, an associate professor of environmental medicine at the University of Rochester, studies the role of MeHg in skeletal muscle disorders.[47] “These conditions have traditionally been attributed to central nervous system disruptions,” says Rand. “But skeletal muscle abnormalities may also cause motor symptoms, which has been explored much less.”
Microbial influences on human toxicity go beyond the direct metabolism of iAs. Because both metals have historically been used as antimicrobial agents,[77,78] it is plausible that they may reduce the diversity of microbes in the gut. “This is especially worrisome for infants and young children,” says Juliette Madan, a neonatal perinatologist and professor of epidemiology at the Dartmouth Geisel School of Medicine. “[Exposure to metals may change] the developmental trajectory of their gut microbiome during a critical period when their immune system is being trained and their body is learning to metabolize food.”Analyzing data from the New Hampshire Birth Cohort Study, Madan and Karagas found that higher urine As concentrations in babies were associated with a reduced frequency in stool of multiple microbial genera involved in immune system development.[79] A later analysis, which used toenail clippings to assess exposure to a variety of trace elements, associated higher As levels with reduced gut microbial diversity in all the infants. The same association was observed with higher Hg levels in a subset of babies.[80] Higher MeHg concentrations in stool were also associated with lower microbial diversity in a small study of pregnant women.[81]Curtis Huttenhower, a professor of computational biology and bioinformatics at the Harvard T.H. Chan School of Public Health, notes that studies of exposure effects on microbial diversity require special care because chronic health conditions, the therapeutics used to treat them, and many dietary and environmental exposures all affect microbiome composition in similar ways. This means that quality control methods for laboratory and statistical analyses of microbiome samples are critical to avoid spurious associations.[82,83]The known microbial influences on the human toxicity of iAs and MeHg may only be the tip of the iceberg.[84,85] In natural environments, for example, the As defense systems of soil and aquatic bacteria regulate an exceptionally wide range of cellular processes beyond iAs methylation, including sugar transport, copper tolerance, and iron homeostasis.[84] Walk says this fact—along with recent rodent findings[86]—suggests that microbes in the human gut may transform iAs in additional ways that indirectly influence toxicity, perhaps by producing arsenicals that more easily cross cell membranes. “We think the total microbial influence on arsenic biochemistry is larger than the host’s and likely involves many different types of biotransformation,” adds Walk. “Methylation is just one of these.”Similarly, says Sarah Rothenberg, an associate professor of environmental health at Oregon State University, microbial influences on MeHg toxicity may not be restricted to demethylation. “It is quite possible that gut microbes may help regulate neurotransmitters through the gut–brain axis, as some studies[87,88] have suggested,” she explains. In other words, the microbiome may contribute to the notorious neurotoxic effects of MeHg through a variety of mechanisms. Further study could clarify the full range of bidirectional interactions between iAs, MeHg, and the gut microbiome.
Authors: Sarah E Rothenberg; Sharon Keiser; Nadim J Ajami; Matthew C Wong; Jonathan Gesell; Joseph F Petrosino; Alexander Johs Journal: Toxicol Lett Date: 2015-11-25 Impact factor: 4.372
Authors: Beatriz Valera; Gina Muckle; Paul Poirier; Sandra W Jacobson; Joseph L Jacobson; Eric Dewailly Journal: Neurotoxicology Date: 2012-10 Impact factor: 4.294
Authors: Sarah E Rothenberg; Merle Anders; Nadim J Ajami; Joseph F Petrosino; Erika Balogh Journal: Sci Total Environ Date: 2016-07-20 Impact factor: 7.963
Authors: Tom Van de Wiele; Christina M Gallawa; Kevin M Kubachka; John T Creed; Nicholas Basta; Elizabeth A Dayton; Shane Whitacre; Gijs Du Laing; Karen Bradham Journal: Environ Health Perspect Date: 2010-03-26 Impact factor: 9.031
Authors: Antonio J Signes-Pastor; Jayne V Woodside; Paul McMullan; Karen Mullan; Manus Carey; Margaret R Karagas; Andrew A Meharg Journal: PLoS One Date: 2017-05-04 Impact factor: 3.240
Authors: Beverly H Koller; John N Snouwaert; Christelle Douillet; Leigh A Jania; Hisham El-Masri; David J Thomas; Miroslav Stýblo Journal: Environ Health Perspect Date: 2020-08-11 Impact factor: 9.031