A method was developed for the determination of total arsenic in rice grain by microwave-assisted digestion inductively coupled plasma mass spectrometry. Standard calibration solutions were matrix-matched with respect to acid concentration and carbon content post-digest. The importance of eliminating the drying step during sample preparation procedures was investigated. The method was validated with spikes containing standard arsenate solutions into the rice matrix, and with certified reference material SRM1568a (rice flour) from NIST. The method was successfully applied to a commercially available rice sample. Four arsenic species [arsenate (As(V)), arsenite (As(III)), dimethylarsinic acid (DMA) and monomethylarsonic acid (MMA)] were extracted from rice grains by microwave-assisted extraction and separated with high performance liquid chromatography inductively coupled plasma mass spectrometry. The method includes a novel sample clean-up step involving a dialysis procedure to decrease the amount of large starch molecules in the injection solution, in order to minimize poor resolution of chromatographic peaks and maximize column life. The method was validated with spikes of standard arsenic solutions, added to the rice matrix before the extraction procedure. Literature reference values for arsenic species quantification in SRM1568a (rice flour) were also compared. This method was successfully applied to a commercially available rice sample. A study into improvements in reverse phase-HPLC separations of arsenic species was conducted. For the first time, a Sunfire C8 column from Waters (Milford, CT) was employed for the separation of arsenic species in rice extracts. This column was compared to a Symmetry C8 column with respect to total elution time, detection limits, interference effects, and column life, and evaluated with respect to peak resolution, shifts in retention times, and peak symmetry.

Groundwater arsenic contamination is currently a global problem, and also a concern at numerous former industrial sites, agricultural sites, landfill sites and mining operations in the U.S. This dissertation aims to develop improved strategies of remediating these arsenic contaminated aquifers. It focuses on two distinct approaches of remediation: (1) mobilizing arsenic from contaminated aquifer sediments to decrease the quantity of arsenic at the source of contamination; and (2) immobilizing arsenic in situ, to decrease the mobility and bioavailability of this arsenic. Optimal remediation may well involve combinations of these two approaches. Arsenic mobilization using oxalic acid is effective because oxalic acid dissolves arsenic host minerals and competes for sorption sites on those minerals. In this dissertation, oxalic acid treatment was tested using sediments with contrasting iron mineralogies and arsenic contents from the Dover Municipal Landfill and the Vineland Chemical Company Superfund sites. Oxalic acid mobilized arsenic from both sites and the residual sediment arsenic was less vulnerable to microbial reduction than before the treatment. Oxalic acid thus could improve the efficiency of widely used pump-and-treat remediation. Oxalic acid did not remove all of the reactive iron(III) minerals in Vineland sediment samples, and thus released significant quantities of arsenic into solution under reducing conditions than the Dover samples. Therefore, the efficacy of pump-and-treat must consider iron mineralogy when evaluating its overall potential for remediating groundwater arsenic. Arsenic immobilization occurs by changing the chemical state, or speciation, of arsenic and other elements in the system. Arsenic is often assumed to be immobile in sulfidic environments. In this dissertation, sulfate reduction was stimulated in sediments from the Vineland Superfund site and the Coeur d'Alene mining district. Sulfate reduction in the Coeur d'Alene sediments was more effective at removing arsenic from solution than the Vineland sediments. The Vineland sediments initially contained abundant reactive ferrihydrite, and underwent extensive sulfur cycling during incubation. As a result, arsenic in the Vineland sediments could not be effectively converted to immobile arsenic-bearing sulfides, but instead a part of the arsenic was probably converted to soluble thioarsenates. Therefore, coupling between the iron and sulfur redox cycles must be fully understood for arsenic immobilization by sulfate reduction to be successful. Arsenic can also be immobilized by retention on magnetite (Fe3O4). Magnetite is stable under a wide range of aquifer conditions including both oxic and iron(III)-reducing environments. In this dissertation, a series of experiments were performed with sediments from the Dover and Vineland Superfund sites, to examine the potential of magnetite for use in arsenic immobilization. Our data suggest that the formation of magnetite can be achieved by the microbial oxidation of ferrous iron with nitrate. Magnetite can incorporate arsenic into its structure during formation, forming a stable arsenic sink. Magnetite, once formed, can also immobilize arsenic by surface adsorption, and thus serve as a reactive filter when contaminated groundwater migrates through the treatment zone. Reactive transport modeling is used for investigating the magnetite based arsenic immobilization strategy and for scaling laboratory results to field environments. Such modeling suggests that the ratio between iron(II) and nitrate in the injectant regulates the formations of magnetite and ferrihydrite, and thus regulates the long-term evolution of the effectiveness of the strategy. The results from field-scale models favor scenarios that rely on the chromatographic mixing of iron(II) and nitrate after injection. The studies in this dissertation demonstrate that the environmental fate of arsenic depends on the biogeochemical cycling of arsenic, iron, and to a lesser extent, sulfur. The development of effective groundwater arsenic remediation strategies depends on a good understanding of each of the involved processes, and their combinations.

Dissertation submitted in partial compliance with the requirements of the Master's Degree in Technology: Homoeopathy, Durban University of Technology, 2010. / The therapeutic effects of homoeopathic Arsenicum album potencies were investigated in-vitro, using human cell cultures which were previously antagonised by arsenic trioxide (As2O3). Primary cell culture (peripheral blood mononuclear cells) and a continuous cell line (MT4) were treated with succussed and unsuccussed homoeopathic potencies, 6CH, 30CH and 200CH. This study aimed to verify the homoeopathic law of similars and to determine whether potencies diluted beyond Avogadro’s constant had physiological effects on cells; whether various potencies would cause different effects as proposed by the Arndt-Schultz law; whether succussed and unsuccussed homoeopathic potencies had different effects on the cells; and to establish whether a biotechnological method could be used to evaluate the above. Initial experiments involved isolation and culturing of the peripheral blood mononuclear cells (PBMCs) and the MT4 cell line. Cell titres were determined using the trypan blue dye exclusion assay. The solubilization method of As2O3 was optimized through various dissolution experiments, so as to attain a homogenous arsenical solution. The MTT assay was used to measure the percentage cytotoxicity and the half maximal inhibitory concentration (IC50) caused by the antagonist As2O3 on the PBMCs and the MT4 cell line. The two cell cultures were compared with regard to their susceptibility to As2O3 and their reliability of response. The homoeopathic potencies of Arsenicum album (6CH, 30CH and 200CH) were prepared by initially triturating the As2O3, and then either hand succussing 10 times (succussed) or allowing to diffuse for 30 s (unsuccussed) in sterile distilled water, with the final potencies made up in cell culture media, RPMI. The MTT assay was used to determine the percentage cell viability when the As2O3-antagonised cells were treated with the Arsenicum album potencies. All assays were performed in triplicate. v The As2O3 was found to fully dissolve when 396 mg of dry As2O3 was added to 100 mL of sterile distilled Milli-Q water, which was left to stand for 10 days at 80°C. The cytotoxicity results showed that the PBMCs were not as reliable as the MT4 cells, which showed significant susceptibility to the As2O3. The IC50 of As2O3 on 1 mL of MT4 cells was found to be 5 μM As2O3 (133 μL) for 48 h. The trypan blue dye exclusion assay demonstrated that the viable MT4 cells decreased in number after exposure to the As2O3, with an increase in number of the non-viable cells. Microscopically, the cells were fewer in number and displayed signs of possible blebbing and cell shrinkage, showing potential cell death due to apoptosis. The cell viability results showed that the Arsenicum album 6CH resulted in the lowest absorbance readings and the Arsenicum album 200CH gave the highest readings; this verified the therapeutic effects of homoeopathic remedies when given according to the law of similars; that potencies diluted beyond Avogadro’s constant had stimulating effects; and that the more dilute potencies stimulated recovery in the cells more than the lower potencies, verifying the Arndt-Schultz law. The treatments and the times of exposure were found to be statistically significant determinants of cell viability, whereas succussion did not cause any significant variation in the results. The study thereby provided evidence that a biotechnological method could be used to scientifically evaluate the physiological effects of homoeopathic potencies on human cells; that the homoeopathic potencies did have therapeutic effects; and that succussion was not required in the potentization method in order to produce a curative remedy.

<p>Arsenic (As) exposure via groundwater consumption is a global health problem affecting millions. Monitoring exposure is a key step in understanding and predicating future health outcomes. This thesis explores the relationships between arsenic concentrations in toenails and arsenic in water. Three case studies were investigated, with residents from: North Carolina, USA (n=103); the Rift Valley, Ethiopia (n=60); and the Mekong Delta, Vietnam (n=65). Arsenic concentrations above the WHO's recommended 10ppb limit were found in groundwater from the three research sites. </p><p>Arsenic in toenails was analyzed by inductively coupled plasma mass spectrometry (ICP-MS). </p><p>In the Rift Valley of Ethiopia, 53% of the tested drinking wells (n=34) had As above the WHO's limit. Arsenic concentrations in toenails (n=60) were significantly correlated to As concentrations in groundwater (r=0.72; p<0.001), reflecting the direct exposure of rural communities to As in well water, which is their principle water source. Male minors (<18 years old) were found to have greater nail-As concentrations compared with adults consuming equal amounts of As (p<0.05). Estimated As dose specifically from drinking water sources was also associated with nail concentrations (p<0.01). </p><p>In the Mekong Delta of Vietnam (Dong Thap Province), 36 out of the 68 tested wells had As content above the WHO's recommended limit of 10ppb, with levels as high as 981 ppb. Arsenic contents in nails collected from local residents (n=62) were significantly correlated to As in drinking water (r=0.49, p<0.001). Demographic and survey data show that the ratio of As in nail to As in water varies among residents that reflects differential As accumulation in the exposed population. The data show that water filtration and diet, particularly increased consumption of animal protein and dairy and reduced consumption of seafood, were associated with lower ratios of As in nail to As in water and thus could play important roles in mitigating As exposure.</p><p>Sixty-one wells were tested from Union County, North Carolina, with 15 out of 61 wells exceeded the WHO's 10 ppb limit. Arsenic values ranged from below the limit of detection (0.07) to 130ppb, with a mean of 11ppb (median=1.5ppb). Nails were collected from county residents (n=103) and were statistically correlated with As-water concentrations (r=0.48, p<0.001). </p><p>Integration of the data from the three cases studies across different populations and ethnicities show high correlation between As concentrations in groundwater and As in nails in all the three locations (r(Union County)= 0.48, p<0.001; r(Ethiopia)=0.72 p<0.001; r(Vietnam)=0.49, p<0.001). For As-nail to As-water pairs in which As in water was above 1ppb, these three locations are statistically indistinguishable from one another (r=0.62, p<0.001, n=176). These results support the hypothesis that nails can be used as a biomarker of exposure regardless of geographic or ethnic differences in populations considered. Nutrition (meat, seafood, and milk consumption) rather than gender, ethnicity, or dose is suggested to be the major confounding issue affecting the magnitude of As exposure in the human body.</p> / Dissertation

Dissertation (PhD)--Stellenbosch University, 2003. / ENGLISH ABSTRACT: The acidophilic, chemolithoautotrophic bacterium, Acidothiobaci/lus ferrooxidans is one of a consortium of bacteria involved in biornining, including the recovery of gold from arsenopyrite ores. The genes conferring arsenic resistance to At. ferrooxidans were cloned and sequenced and shown to be chromosomally located. Homologues to the arsB (membrane located arsenite efflux pump), arsC (arsenate reductase) and arsH (unknown function) genes from known arsenic resistance (ars) operons were identified. A fourth gene was found to have weak homology to the ArsR-family of regulators. The arsenic resistance genes of At. ferrooxidans are arranged in an unusual manner, with the arsRC and arsBH genes divergently transcribed. This divergent arrangement was found to be conserved in all four of the At. ferrooxidans strains we tested. All of the At. ferrooxidans ars genes were expressed in Escherichia coli and the arsB and arsC genes conferred arsenite (and antimonite) and arsenate resistance, respectively, to an E. coli ars mutant (AW311 0). Analysis of the putative amino acid sequences of these ars genes revealed that the ArsB from At. ferrooxidans is closely related to the ArsB proteins from other Gram-negative bacteria. However, the ArsC protein is more closely related to the ArsC proteins from Gram-positive bacteria. Furthermore, a functional thioredoxin (trxA) gene was required for ArsC-mediated arsenate resistance in E. coli. This suggests that reduction of arsenate by At. ferrooxidans has a similar reaction mechanism as that by Gram-positive ArsC proteins. While arsH was expressed in an E. coli-derived in vitro transcription-translation system, the presence of this gene was not required for, nor enhanced, arsenite or arsenate resistance in E. coli. We predict that the function provided by this gene is not required in E. coli. While the putative ArsR from At. ferrooxidans does contain a potential DNA-binding helix-turn-helix (HTH) domain, it does not contain the arsenite binding motif (ELCVCDL), required for response to the presence of inducer. Instead, the ArsR-like protein from At. ferrooxidans is related to a group of unstudied ArsR-like proteins that have been associated with other ars-like genes identified during genome sequencing projects. Using arsB-lacZ, arsC-lacZ, and arsR-lacZ fusions, it has been shown that this atypical ArsR protein from At. ferrooxidans did repress expression from the arsBH and arsRC promoters and that this repression was relieved by the presence of either arsenite or arsenate. Deletion of 19 amino acids from the C-terminus of the ArsR protein did not affect regulation, while deletion of a further 28 amino acids inactivated ArsR. Northern blot hybridization confirmed that expression of the arsRC and arsBH transcripts is increased in the presence of either arsenite or arsenate. This study is the first to show that the ars genes from the acidophilic biorning bacterium At. ferrooxidans are able to be studied in the neutrophilic bacterium, E. coli. We have also shown that the atypical ArsR found in this ars operon is able to regulate expression of these genes in response to arsenic, despite not containing the arsenite binding domain, suggesting that this protein senses arsenic by a different mechanism to that used by the ArsR family members already studied. / AFRIKAANSE OPSOMMING: Acidothiobacillus ferrooxidans, 'n asidofiliese, chemolitotrofiese bakterium, is een van 'n konsortium bakterieë betrokke by biologiese ontgunnig ("biomining") asook by die herwinning van goud uit arsenopiriet erts. Die gene wat aan At. ferrooxidans weerstandbiedendheid teen arseen verleen, is gekloneer. Die DNA-volgorde van hierdie gene is bepaal en daar is bewys dat die gene op die chromosoom geleë is. Homoloë van die arsB (membraan geleë pomp wat arseniet uitpomp), arsC (arsenaat reduktase) en die arsH (funksie onbekend) gene is in bekende arseenweerstanbiedheidsoperons (arsoperons) geïdentifiseer. Verder is daar 'n vierde geen geïdentifiseer wat lae homologie met die ArsR-familie van reguleerders toon. At. ferrooxidans se ars gene is op 'n ongewone manier gerangskik met twee van die gene, arsRC en arsBH wat lil teenoorgestelde rigtings getranskribeer word. Hierdie rangskikking van gene IS waargeneem in al vier die At. ferrooxidans rasse wat getoets is. Al die At. ferrooxidans ars gene is in Escherichia coli uitgedruk. Die arsB en arsC gene het aan 'n E. coli ars mutant (AW311 0) weerstandbiedendheid teen aseniet, antimoniet en arseen verleen. Analiese van die afgeleide aminosuurvolgorde van die ars proteïene het getoon dat die At. ferrooxidans ArsB naby verwant aan die ArsB-proteïene van ander Gram negatiewe bakterieë is. In teenstelling hiermee, is gevind dat die ArsC-proteïene nader verwant aan die ArsC-proteïene van Gram positiewe bakterieë is. Daar is ook gevind dat 'n funksionele tioredoksien (trxA) geen vir ArsC-bemiddelde arsenaat weerstandbiedendheid in E.coli benodig word. Dit dui daarop dat die meganisme van arsenaatreduksie deur At. ferrooxidans soortgelyk is aan die ArsC-proteïen-meganisme van Gram positiewe bakteriee. In vitro studies met behulp van 'n E. coli gebaseerde transkripsie-translasie sisteem het getoon dat arsH nie nodig is vir arsenaat of aseniet weerstanbiedendheid in sensitiewe E.coli rasse nie en ook nie help om weerstand in hierdie rasse te verhoog nie. Daarom kan daar aangeneem word dat die funskie van die arsH geen nie deur E. coli benodig word nie. Die vermeende ArsR van At. ferrooxidans bevat 'n potensiële DNA-binding heliks-draaiheliks motief, maar nie die arsiniet binding motief (ELCVCDL) wat nodig is vir reaksie in die teenwoordigheid van 'n induseerder nie. Die ArsA-proteïen van At. ferrooxidans is soortgelyk aan 'n groep ArsA-proteïene wat tydens genoom DNA- volgordebepalingsprojekte geïdentifiseer is. Hierdie groep gene is egter nog nie verder bestudeer nie. Deur gebruik te maak van 'n stel fusie gene, arsB-IacZ, arsC-IacZ en arsRlacZ kon daar bewys word dat die ongewone ArsH-proteïen van At. ferrooxidans uitdrukking van arsBH en arsRC onderdruk en dat die onderdrukking deur arseniet of arsenaat opgehef kan word. Delesie van die eerste 19 aminosure vanaf die C-terminus van die ArsA-proteïen het geen uitwerking op die regulering van die proteïen nie, maar delesie van 'n vedere 28 aminosure het ArsR geïnaktiveer. Verhoogde vlakke van transkripsie van arsRC en arsBH in die teenwoordigheid van arseniet en arsenaat is met behulp van Noordelike kladanalise bewys. Hierdie is die eerste studie waarin daar bewys word dat die ars gene van die asidofiliese bakterium Atferrooxidans in die neutrofiliese bacterium E. coli bestudeer kan word. Daar is ook bewys dat ten spyte daarvan dat die ArsR in die ars operon nie 'n arseniet bindingsdomein het nie, dit die uitdrukking van die gene in hierdie operon reguleer in reaksie op arseen. Dit dui dus daarop dat hierdie proteïen op arseen in die omgewing reageer met behulp van 'n meganisme wat verskil van die ArsR-proteïene wat tot dusver bestudeer is.

2 pp. / Arsenic is the twentieth most abundant element in the earth's crust and frequently occurs in rock formations of the Southwestern United States. Arsenic remains in the environment over long periods and when it occurs in high concentrations, it can be toxic to many life forms, but it also has been shown to be an essential nutrient for many animal species and may be to humans, too. This publication provides information about the impact arsenic in drinking water has over human and plant health and the ways to remove it.

3 pp. / 1. Drinking Water Wells; 2. Private Water Well Components; 3. Do Deeper Wells Mean Better Water; 4. Maintaining Your Private Well Water System; 5. Private Well Protection; 6. Well Water Testing and Understanding the Results; 7. Obtaining a Water Sample for Bacterial Analysis; 8. Microorganisms in Private Water Wells; 9. Lead in Private Water Wells; 10. Nitrate in Private Water Wells; 11.Arsenic in Private Water Wells; 12. Matching Drinking Water Quality Problems to Treatment Methods; 13. Commonly Available Home Water Treatment Systems; 14. Hard Water: To Soften or Not to Soften; 15. Shock Chlorination of Private Water Wells / This fact sheet is one in a series of fifteen for private water well owners. The one- to four-page fact sheets will be assembled into a two-pocket folder entitled Private Well Owners Guide. The titles will also be a part of the Changing Rural Landscapes project whose goal is to educate exurban, small acreage residents. The authors have made every effort to align the fact sheets with the proposed Arizona Cooperative Extension booklet An Arizona Well Owners Guide to Water Sources, Quality, Testing, Treatment, and Well Maintenance by Artiola and Uhlman. The private well owner project was funded by both the University of Arizonas Water Sustainability Program-Technology and Research Initiative Fund and the USDA-CSREES Region 9 Water Quality Program.

Chronic environmental exposure to inorganic arsenic is widely associated with human disease. Low human arsenic secondary methylation efficiency (SME), represented by high urinary monomethylarsonic acid (%uMMA) and low urinary dimethylarsinic acid to monomethylarsonic acid ratio (uDMA/uMMA), has been consistently associated with increased risk of arsenic-related diseases. Therefore the determination of factors modulating arsenic SME acquires particular importance. The aims of the present study are to identify novel factors of variability in arsenic secondary methylation, and to test for potential factors influencing arsenic SME for which there is equivocal literature support. A population of 808 subjects was recruited from northwest Mexico environmentally exposed to arsenic. The mean total urinary arsenic in the population was 171 μg/L. Great interindividual variability in %uMMA excretion was observed (0.85% - 40.5%). Three intronic polymorphisms in arsenic (3+ oxidation state) methyltransferase (AS3MT), the key gene in the metabolism of arsenic, were confirmed to be associated with increased arsenic SME in this study. Further analysis of this genomic region showed a large block of linkage disequilibrium (LD) comprising these three genetic variants and other 43 intronic polymorphisms within AS3MT and four additional genes. Genetic association analysis showed that all linked polymorphisms in this region except one were significantly associated with higher arsenic SME. The existence of this long region of LD associated with arsenic SME underscores the complexity of association studies involving any of these linked polymorphisms since there is no certainty of which polymorphism or gene is the causative of the association. In addition, a strong positive association between body mass index (BMI) and arsenic SME was observed in females but not in males. This association was replicated in two independently recruited populations of adult women. Moreover a unique finding of this study is the association between higher genetically estimated indigenous American (AME) ancestry and increased arsenic SME in this ancestrally admixed Mexican population. These results establish the importance of genetic and phenotypic factors in the efficiency of arsenic secondary methylation. Furthermore this study has identified several arsenic-associated risk factors that should be carefully considered in future studies seeking to better understand disease susceptibility in arsenic-exposed populations.

The immune system is a target of arsenic toxicity. Epidemiological data have shown that arsenic exposure is associated with characteristics of immunosuppression. Human B-lymphoblastoid cell lines (LCL) were used as an in vitro model of immune cell targeting by arsenic to investigate the mechanism of arsenic-induced cytotoxicity, which could provided insight into the mechanism underlying arsenic-induced immunotoxicity leading to the immunosuppression observed in humans. In LCL arsenite-induced cytotoxicity was not associated with apoptosis, but associated with hallmarks of autophagy, a cell stress-responsive process that facilitates the removal of cellular components through lysosome-mediated degradation. At environmentally relevant concentrations, arsenite-induced toxicity resulted in a decrease in cell proliferation that was correlated with hallmarks of autophagy including expansion of acidic vesicles, global induction of lysosomal gene expression, increased flux of the autophagosome marker LC3-II, and increased enzymatic activity of the lysosomal hydrolase cathepsin D. Investigation of the upstream cellular damage leading to the induction of autophagy revealed that arsenite induces proteotoxic damage leading to an accumulation of protein aggregates that may be targeted to the lysosome for degradation. In addition, global gene expression data showed an enrichment of ER stress responsive genes after arsenite exposure. Further evaluation of global gene expression data indicated that the global induction of lysosomal genes occurs before the activation of ER stress genes, suggesting that the induction of autophagy may occur before the generation of ER stress. To investigate the effect of arsenite-induced proteotoxicity and autophagy on normal immune function, the ability of LCL to process and present exogenous antigens onto MHC class II molecules was evaluated. Arsenite decreased antigen presentation of the exogenous antigen HSA. This decrease was associated with decreased lysosomal degradation of the model substrate DQ-Ova, suggesting that arsenite is disrupting lysosome-mediated degradation. In addition, arsenite exposure was associated with an increase in MHC class II protein aggregates, which could render them unavailable to bind peptide fragments. Through the identification that arsenite induces proteotoxicity and autophagy in LCL, it provides novel insight into the mechanisms of arsenic-induced immunotoxicity that could lead to a better understanding of the mechanisms underlying arsenic-induced immunosuppression observed in humans.

Background: Arsenic (As) is a naturally-occurring element with known toxicant effects. The primary exposure pathway is through ingestion, but the overall contribution of food versus water and the impact of specific dietary nutrients on urinary As excretion is not well understood. Methods: Secondary analyses of laboratory results from food, water and urine samples, questionnaire and anthropometric data, and dietary records were performed on four study populations: the National Health Exposure Assessment Survey (NHEXAS)-Arizona, Arizona Border Survey (ABS), the Arizona sub-group of the Binational Arsenic Exposure Survey (BAsES), and the 2003-2004 National Health and Nutrition Examination Survey (NHANES). Dietary As intake was measured in duplicate food samples and/or modeled from dietary records for each population using the U.S. Total Diet Study (TDS) arsenic residue database and a published market basket survey. Urinary total As, As⁵, As³, monomethylarsonic acid (MMA), and dimethylarsinic acid (DMA) were analyzed, and sum of species As was calculated as the sum of As⁵, As³, MMA and DMA. Regression analyses modeled the relation between urinary As biomarkers (total, sum of species, MMA:sum of species, and DMA:MMA) and dietary As, adjusted for drinking and cooking water As intake, current smoking, sex, age, ethnicity, body mass index, and nutrient intake. Results: Modeled dietary As based on TDS mean As residue data greatly underestimated exposure as compared with measured As in duplicate diet samples and estimates based on other residue data. Dietary As was a significant predictor of urinary total As in all four populations, of sum of species As in both BAsES and NHANES, and of %MMA and DMA:MMA in NHANES. Dietary protein intake was associated with decreased sum of species As in both BAsES and NHANES, but dietary folate was not. Conclusions: Dietary As contributes a markedly greater proportion of total ingested As and is a better predictor of urinary As than water As intake in the U.S. Among subjects who did not consume seafood, total As exposure from food and water exceeded the provisional tolerable daily intake of 2.1 µg/kg body weight/day in 3-15% of these study populations. Increased protein intake may mitigate the effects of As.